United States
Environmental Protection
Agency
Office of Radiation and Indoor Air
National Air and Radiation
Environmental Laboratory
540 South Morris Avenue
Montgomery, AL 36115-2601
EPA-402-R-05-002
August 2005
Radiological Survey at the
New London Harbor
Facilities
Internet Address (URL) • http://www.epa.gov
Recycled/Recyclable • Printed with Vegetable Oil Based Inks on 100% Postconsumer, Process Chlorine Free Recycled Paper
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Radiological Survey at the
NEW LONDON HARBOR FACILITIES
August 2005
U.S. Environmental Protection Agency
Office of Radiation and Indoor Air
National Air and Radiation Environmental Laboratory
540 South Morris Avenue
Montgomery, AL 36115-2601
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CONTENTS
EXECUTIVE SUMMARY v
ACKNOWLEDGMENTS vii
ILLUSTRATIONS ix
TABLES xi
ABBREVIATIONS xiii
1.0 INTRODUCTION 1
1.1 Site Description and History (Se91) 1
1.2 Survey History 2
1.3 Contaminants of Concern 3
1.4 Study Objectives 3
2.0 SAMPLING, MEASUREMENT AND ANALYSIS 5
2.1 Sampling and Measurement Strategy 5
2.1.1 Background Sampling Locations 5
2.1.2 New London Harbor Facilities (NLHF) Survey Site 6
2.1.3 Instrumentation 6
2.1.4 Table Notes 6
2.1.4.1 General 6
2.1.4.2 Sample Identification 6
2.2 Sample Collection and Analysis 7
2.2.1 Sample Collection 7
2.2.2 Sample Analysis 9
3.0 RESULTS AND DISCUSSION 31
3.1 Water Samples 31
3.1.1 Surface Water Samples 31
3.1.2 Drinking Water Samples 31
3.2 Sediment and Sediment Core Samples 32
3.2.1 Harbor and Shoreline Sediment Samples 32
3.2.2 Sediment Core Samples 33
3.3 Biota Samples 33
3.4 External Gamma Radiation Measurements 33
4.0 QUALITY ASSURANCE/QUALITY CONTROL (QA/QC) 39
4.1 The Quality Assurance Program 39
in
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4.2 Quality Control Samples 39
4.3 Performance Evaluation Programs 40
5.0 CONCLUSIONS 41
6.0 REFERENCES 43
APPENDIX 45
IV
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EXECUTIVE SUMMARY
This report presents results of a radiological survey conducted in September 1999 by the National
Air and Radiation Environmental Laboratory (NAREL) to assess levels of environmental
radioactivity in and around naval harbor facilities located on the Thames River near New
London, Connecticut. These facilities include the New London Submarine Base (NLSB) at
Groton, the Electric Boat Company (EB) at Groton, Sound Signature Facility and the State Pier.
These facilities will be referred to collectively in this report as the New London Harbor Facilities
(NLHF). The purpose of the survey was to assess whether the construction, maintenance,
overhaul, refueling or operation of nuclear-powered warships have created elevated levels of
radioactivity in the marine environment which could expose nearby populations or contaminate
the environment.
During this survey 265 samples were collected: 11 were from background locations and 19 near
the outfalls of the public water treatment plants. Samples included drinking water, harbor
surface water, sediment, sediment cores, and biota. All samples were analyzed for gross alpha
and beta activities and gamma emitting radionuclides. Water samples were also analyzed for
tritium. In addition to sample collection and analysis, radiation surveys were performed using
portable survey instruments to detect gamma radiation.
The measured cobalt-60 is consistent with and appears to be attributable to the cobalt-60
previously measured at the NLHF, corrected for radioactive decay. While the possibility of a
recent release being masked by the previously released cobalt-60 cannot be completely disproved
by the sample results, such a recent release would likely have little or no adverse impact on
human health or the environment. Iodine-131 was detected in 11 biota samples and a surface
water sample at a sewer outfall. The source of the 1-131 is most likely due to medical use.
Radioactivity levels detected in other samples were consistent with levels expected to exist due
to naturally occurring radioactivity or fallout from atmospheric nuclear testing and from the
Chernobyl reactor accident in 1986. Based on this radiological survey, practices regarding
nuclear-powered warship operations at NLHF have resulted hi no increases in radioactivity
causing significant population exposure or contamination of the environment.
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ACKNOWLEDGMENTS
Many staff participated in this study and helped prepare this report. The detailed planning,
support, and assistance of the Electric Boat Company and New London Submarine Base
personnel was much appreciated. The EPA survey team consisted of Sam Poppell, Ted Fowler,
Jim Moore, Ed Mantiply, and Bob Trefethen from NAREL and Jim Cherniack from EPA Region
1 in Boston, MA. Staff of the NAREL Monitoring and Analytical Services Branch prepared and
analyzed the samples collected during the survey. Chuck Petko edited the report. The NAREL
Information Technology staff provided invaluable support during preparation of this report.
Finally, thanks go to the EPA staff who served as technical peer reviewers of the manuscript.
DISCLAIMER
Mention of trade names or commercial products does not constitute endorsement or
recommendation for use.
VII
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ILLUSTRATIONS
Figure Page
1. Thames River Delta 10
2. New London Harbor 11
3. Electric Boat Company - South 12
4. Electric Boat Company - North 13
5. State Pier 14
6. Thames River - Waterford 15
7. New London Submarine Base - South 16
7a. New London Submarine Base - South - Insert 17
8. New London Submarine Base - North 18
9. Thames River - Montville 19
IX
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TABLES
Table Page
1. Sample and Measurement Locations ........................................ 20
2. External Gamma Radiation Measurements ................................... 35
A.I Gamma Spectrometry Results for Surface Water Samples ....................... 49
A.2 Tritium Results for Surface Water Samples .................................. 51
A.3 Gross Alpha and Gross Beta Activity Results for Surface Water Samples ........... 53
A.4 Gamma Spectrometry Results for Drinking Water Samples ...................... 55
A.5 Tritium Results for Drinking Water Samples ................................. 55
A.6 Gross Alpha and Gross Beta Activity Results for Drinking Water Samples ......... 56
A. 7 Gamma Spectrometry Results for Harbor and Shoreline Sediment Samples
Uranium and Actinium Decay Chains ....................................... 57
A.8 Gamma Spectrometry Results for Harbor and Shoreline Sediment Samples
Thorium Decay Chain and Other Gamma-Emitting Radionuclides ................ 67
A.9 Gross Alpha and Gross Beta Activity Results for Harbor and Shoreline Sediment
Samples [[[ 76
A. 1 0 Gamma Spectrometry Results for Sediment Core Samples Uranium and Actinium
Decay Chains [[[ 84
A. 1 1 Gamma Spectrometry Results for Sediment Core Samples Thorium Decay Chain
and Other Gamma Emitting Radionuclides ................................... 93
A. 12 Gross Alpha and Gross Beta Activity Results for Sediment Core Samples ......... 102
A. 1 3 Gamma Spectrometry Results for Biota Samples Uranium and Actinium Decay
Chains [[[ 110
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ABBREVIATIONS
cm Centimeter
EB Electric Boat Company
GPS Global Positioning System
IAG Inter-Agency Agreement
L Liter
m Meter
jj.R Microroentgen (10"6 roentgen of y-ray exposure)
jj,R/hr Microroentgen per hour
MDC Minimum Detectable Concentration
NAREL National Air and Radiation Environmental Laboratory
NAVSEA Naval Sea Systems Command
ND Not Detected
NLHF New London Harbor Facilities
NLSB New London Submarine Base
pCi Picocurie (10~12 curies of radioactivity)
pCi/g-dry Picocuries per gram-dry-weight
pCi/g-ash Picocuries per gram-ashed-weight
pCi/g-wet Picocuries per gram-wet-weight
pCi/L Picocuries per liter
PIC Pressurized lonization Chamber
POTW Public Owned Treatment Works
USEPA United States Environmental Protection Agency
xiii
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1.0 INTRODUCTION
The National Air and Radiation Environmental Laboratory (NAREL) of the U.S. Environmental
Protection Agency (EPA) in cooperation with the U.S. Naval Sea Systems Command (NAVSEA)
has previously surveyed facilities serving nuclear-powered warships. These surveys began in
1963 and have been conducted on the Atlantic and Pacific coasts, on the Gulf of Mexico within
the Continental United States, and at Pearl Harbor, Hawaii. In 1996, an interagency agreement
(LAG) was signed with NAVSEA for NAREL to perform radiological surveys over five years at
active facilities serving nuclear-powered warships. These surveys assess whether the
construction, maintenance, overhaul, refueling or operations of nuclear-powered warships have
created elevated levels of radioactivity that could expose nearby populations or contaminate the
environment.
The first six environmental surveys under the interagency agreement have been performed as
follows: Puget Sound Naval Shipyard (PSNS) at Bremerton, WA, and the Naval Submarine Base
(NSBB) near Bangor, WA, during 1996 (Fo98); San Diego Bay, CA, (Go99) and Portsmouth
Naval Shipyard at Kittery, ME, (SmOl) during 1997; at the Pearl Harbor Naval Complex
(PHNC), HI, during 1998 (PoOl); the Navy Nuclear Power Training Unit (NPTU), North
Charleston, SC, during 1999 (Fo03); and Kings Bay Submarine Base, GA, in 1999 (EPA04).
The seventh environmental survey under the IAG was performed September 13-24, 1999, at the
New London Harbor Facilities (NLHF), Groton, CT. A pre-survey trip was made July 19-21,
1999, to develop a sampling and survey work plan with the assistance of knowledgeable site
personnel and EPA radiation program representatives from EPA-NAREL and EPA Region 1.
Staff from NAVSEA, New London Submarine Base (NLSB) and Electric Boat Company (EB)
provided NAREL with information on past and present NLHF radiological operations and
procedures. All requested information was freely provided verbally and/or in writing. Based on
the information received and that derived from previous EPA studies, a work plan (EPA99) was
developed to describe the approach for assessing the radiological condition of the NLHF and
nearby aquatic environments.
1.1 Site Description and History (Se91)(Do99)
The Electric Boat Company, New London Submarine Base, State Pier and Sound Signature
Facility are located on the Thames River in New London County in Southeastern Connecticut.
The Thames River is a tidal estuary arising at the confluence of the Yantic and Shetucket Rivers,
approximately 24 km (15 miles) north of the Groton-New London Harbor area. The river varies
in width from 0.21 km (0.13 miles) to a maximum of 1.82 km (1.13 miles) where it empties into
Long Island Sound. The mean tidal range of the river at New London is 76 cm (2.5 feet).
The New London Submarine Base is located within the City of Groton and Town of Ledyard.
The base is situated on the east bank of the Thames River approximately six miles north of Long
Island Sound. The main base is bounded by Connecticut route 12 on the east, to the south by
Crystal Lake Road, and to the west by the Thames River. The northern border is a low ridge that
trends approximately east-southeast from the river to Baldwin Hill. The submarine base
encompasses 1,412 acres of land.
1
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Electric Boat Company is located within the confines of the City of Groton. EB is situated on the
east bank of the Thames River approximately three miles north of Long Island Sound. EB is
primarily engaged in the construction of nuclear submarines for the United States Navy.
State Pier is a facility in New London, just south of the Gold Star Bridge that spans the Thames
River. A submarine tender was stationed at this location from the early 1960's through the
1980's. Nuclear submarines tied up to the tender for short durations during these years. This
facility is no longer used by the Navy.
The Sound Signature Facility is located in New London and was formerly called the Naval
Underwater Warfare Center (NUWC). The piers at this facility were previously used to tie up
Trident submarines after delivery and for short durations. This facility is no longer used by the
Navy.
Groton, EB, and NLSB obtain their drinking water supply from a series of six surface water
reservoirs located northeast and east of the City of Groton (PNS97).
1.2 Survey History
The New London Harbor Facilities were previously surveyed by the Southeastern Radiological
Health Laboratory of the U.S. Public Health Service in 1966 (Ca66), and by EPA in 1972 (Wi73)
and 1989 (Se91). Detected Co-60 in harbor sediment during the 1966 survey (Ca66) ranged from
10-360 pCi/gm-dry at EB, with an average of 100 pCi/gm-dry; 6-49 pCi/gm-dry at the NLSB;
and 117-200 pCi/gm-dry at State Pier. Higher levels of Co-60 were detected alongside the
Graving Dock and the piers at EB and at piers 10, 12, 13 and 14 at NLSB. Detected Co-60 in
harbor sediment during the 1972 survey (Wi73) ranged from 0.2-26 pCi/gm-dry. Cobalt-60
concentrations in sediment samples collected during the 1972 survey from locations that
duplicated those of the 1966 survey had decreased by a factor of about 30. Average Co-60
concentrations detected in harbor sediment during the 1989 survey (Se91) ranged from 0.14
pCi/gm-dry at the NLSB to 0.26 pCi/gm-dry at State Pier. The highest Co-60 sediment
concentrations were 0.65 pCi/gm-dry at EB, 0.23 pCi/gm-dry at NLSB and 0.60 pCi/gm-dry at
State Pier. Sediment samples that duplicated samples obtained in 1972 contained 8-30 times less
Co-60 than the earlier samples.
Cobalt-60 concentrations in 1989 (Se91) core samples ranged from 0.05-0.19 pCi/gm-dry at EB
and 0.14-0.37 pCi/gm-dry at NLSB. Cobalt-60 concentrations in core samples from NLSB were
about twice those measured at EB (0.2 versus 0.1 pCi/gm-dry).
During the 1989 survey, small concentrations of Co-60, less than 0.1 pCi/gm-dry, were detected
in kelp, sea lettuce and starfish at EB and kelp, sea lettuce and sea cucumber from NLSB.
Cobalt-60 was not detected in any edible biota. Water samples contained no detectable levels of
radioactivity other than those occurring naturally. Measurements of external radiation exposure
along the two shorelines of the Thames River ranged from 3 u.R/hr to 12 fiR/hr. Measurements
taken on the NLSB in areas accessible to the public ranged from 6 u^R/hr to 19
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1.3 Contaminants of Concern
The results of previous harbor surveys indicate that cobalt-60 is the predominant radionuclide
one would find in environmental media if radioactivity is present as a result of naval nuclear
propulsion plant operations (Ca77, Ca87). Therefore, environmental sampling during this survey
emphasized detection of cobalt-60. Other radionuclides of concern in liquid effluents or
encountered during maintenance work would include tungsten-187, chromium-51, iron-59, iron-
55, nickel-63, niobium-95, zirconium-95, manganese-54 and cobalt-58 (ANS99). Water samples
were also analyzed for tritium since this radionuclide is known to be produced in the coolant of
light-water nuclear reactors.
1.4 Study Objectives
The objectives of the study were to determine if radioactive material related to U.S. Navy
nuclear-powered warship construction, operations, repair, and maintenance is present at
measurable levels in the harbor samples collected, to make comparisons of current study results
with past study results and, as deemed appropriate, to estimate potential doses to the public.
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2.0 SAMPLING, MEASUREMENT AND ANALYSIS
The following terms will be used in the discussion of the collection of samples and
measurements:
Survey Site: The geographical area in and around NLHF that was
studied.
Measurement Location: A location in or near the survey site where gamma radiation
levels were measured.
Sampling Location: A location within or near the study site from which samples
were collected.
Background Location: A selected sampling location where representative levels of
naturally occurring or existing radionuclides, not likely to
be related to NLHF, were measured.
2.1 Sampling and Measurement Strategy
This study was intended to determine the concentrations of cobalt-60 and other selected
radionuclides that could be present due to the operations performed at NLHF and other selected
radionuclides that may be present at or near the study site but originated from off-site locations.
The sampling locations selected were those where the Navy and Electric Boat Company
presently conduct environmental monitoring, locations where the USEPA-NAREL sampled in
1989, and locations selected by NAREL to more comprehensively characterize the study site.
Background sampling locations were selected to obtain baseline radionuclide levels that are
characteristic of the area. The data from the study site were compared directly to the background
concentrations when background data were available or to appropriate standards, such as those in
the national drinking water regulations (FROO).
Field duplicate samples were either co-located (adjacent) with the original samples or the original
samples were split. Biota, bottom sediment and water samples were typically composited at the
sampling location upon collection and then split into duplicate samples. However, duplicate
shoreline samples were collected as adjacent samples at the same sampling location.
2.1.1 Background Sampling Locations
Five locations were selected for background sampling. The background locations selected for
NLHF are on the Thames River north of the Submarine Base (see Table 1 and Figure 9). The
background locations were selected during the pre-survey visit (July 1999) and are located at a
distance far enough away from the survey site so that operations there would not have impacted
those locations. Therefore, representative levels of existing radionuclides in the samples as a
result of worldwide fallout and natural radioactivity can be measured. The data from the survey
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site were compared directly to the background concentrations when applicable.
2.1.2 New London Harbor Facilities (NLHF) Survey Site
The NLHF survey site is on the Thames River at the Electric Boat Company, the New London
Submarine Base and the surrounding environs including the State Pier and Sound Signature
Facility areas. Specific measurement and survey locations are listed in Table 1 and shown in
Figures 1 through 9. Note: Locations 1 and 101 are not shown on any of the figures. Sampling
locations presently used by the Navy, Electric Boat Company, and sampling locations added by
NAREL were used during this survey. A description of each sampling location and the type of
sample collected are presented in Table 1. A total of 265 samples were collected during this
survey. Of that total, 254 samples were collected within the area defined as the NLHF study site.
Eleven of the samples were collected from background locations and 19 samples were collected
near the outfalls of the public water treatment plants for the City of New London, City of Groton,
Town of Groton and Town of Montville. Repeated efforts to obtain sediment samples at
locations 3 (off Avery Point), 58 (33 yards south of end of "C" Dock), and 141 (halfway between
locations 8 and 9) were unsuccessful.
2.1.3 Instrumentation
At selected locations, primarily public access areas, radiation surveys were performed using
portable survey instruments to detect gamma radiation. Three types of gamma measuring
instruments were used: a Ludlum Model 19 Micro-R radiation survey instrument, a GENITRON
GM survey instrument and a Reuter-Stokes pressurized ionization chamber (PIC). Instrument
serial numbers and calibration dates are available on the field data sheets. External radiation
measurement locations are given in Table 2 and Figures 1-9.
2.1.4 Table Notes
2.1.4.1 General
Samples were taken as close to piers as situations permitted when a distance was not specified.
Sometimes barges, ships and other equipment prevented collecting a sample close to the pier,
therefore, an alternate location was selected. For each sample and measurement location, the
approximate geographical position (latitude and longitude) of the location was determined in the
field using commercially obtained global positioning system (GPS) receivers. These units had
typical accuracy ranging from 30 to 100 meters. These readings were supplemented by
measuring line-of-sight distances to nearby landmarks. The distances were measured using a
Bushnell YardagePro 400 laser range finder, which is accurate to within about two meters.
2.1.4.2 Sample Identification
Each sample collected or measurement taken during the survey was marked with a unique code
which denoted:
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• Location
• Matrix or Measurement type
Sample type detail (e.g. field duplicate, background, sewer outfall)
The sample identification (ID) code has the form NLHFxxx-yyyy-zz, where 'xxx' indicates the
sampling site ID number, 'yyyy' identifies the measurement type or matrix (and species for biota
samples), and 'zz' provides additional descriptive information such as 'DU' if the sample was a
duplicate or 'BG' if the sample was a background location. Not all samples required the use of
all characters. The following table explains the codes used for the different sample types.
Sample and Measurement Codes
Code Sample or Measurement Type
S
L
C
W
D
BB
Harbor Sediment
Shoreline Sediment
Sediment Core
Harbor Surface Water
Drinking Water
Barnacles
Code Sample or Measurement Type
BBK Brown Kelp
BM Mussel
BSF Starfish
BMG Marsh Grass
BSH Sea Hair
E External Exposure Rate
Coding for a typical sample might be as follows: an NLHF harbor-bottom sediment sample taken
at location 17 is coded 'NLHF017-S'. If the sample were a duplicate at NLHF location 36, it
would be 'NLHF036-S-DU'. A duplicate water sample taken at NLHF location 237 (a
background location) is labeled 'NLHF237-W-DU-BG'. A second water sample taken at the
depth of the sewer outfall has an additional identifier of "02" after the location number to
indicate that this is the second water sample collected at this location but at a different depth than
the first water sample, e.g. 'NLHF008-02-W. "Navy" location ID's have a three letter prefix
with the first two letters indicating the facility (EB for Electric Boat, SP for State Pier, NU for
Naval Undersea Warfare Center and SB for New London Submarine Base) and the third letter
indicating the sample type ("S" for sediment sample, "W" for water sample, "B" for biota
samples and "P" for perimeter thermoluminescent dosimeter [TLD] monitoring location).
2.2 Sample Collection and Analysis
2.2.1 Sample Collection
Shoreline (intertidal) sediment, harbor bottom sediment (grab and core), water (harbor surface,
sewage outfall, and drinking waters), and biota were collected. By previous agreement between
NAREL and the Navy, most samples were split for routine independent comparisons by the
Navy. The samples collected from NLHF are listed in Table 1. Approximately 5 percent of all
samples collected for each sample type were quality control duplicates. The locations where
duplicate samples were taken are noted in Table 1. All samples were analyzed for gross alpha
and beta activities and gamma emitting radionuclides. Water samples were analyzed for tritium.
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Surface Water. A total of 33 surface water samples were collected. This included two duplicate
samples, one of which was taken at a background location. Eight samples were taken near water
treatment facilities. A total of 31 sampling locations were used. Samples were collected by
lowering a Wildco horizontal water sampling bottle (alpha bottle) to a depth of one meter and
then closing the bottle by releasing a "messenger" that activated a tripping mechanism. (Note:
Four of the samples collected at the treatment facilities were collected at the depth of the outfall
pipe.) This process was repeated until 5 L of water were obtained. About 4 L of water were
poured into a plastic sample container and acidified to a pH of < 2 with nitric acid. The acidified
water sample was analyzed for gross alpha and beta activities and gamma emitting radionuclides.
One fourth liter of the water sample was poured into a glass container and, without being
acidified, was analyzed for tritium.
Drinking Water. Five drinking water samples were collected from 3 taps representing the water
supplies of Electric Boat Company, New London Submarine Base, and a background drinking
water sample collected at a motel in Mystic, CT. The 5 L drinking water samples were divided
into two sample containers and preserved and analyzed in the same manner as were the surface
water samples.
Harbor Bottom Sediment. During this study, there were 157 locations at which a total of 166
harbor sediment samples were obtained Of these 166 samples, 8 were duplicate samples, 4 were
collected at public water treatment outfalls, and 4 were at background locations including 1
background duplicate. Sediment sampling from boats was performed using a Peterson dredge to
sample approximately the top 10 cm of sediment. Each sample consisted of approximately 4
liters.
Shoreline Sediment. A total of 8 shoreline samples were collected, of which 1 was a background
sample and 1 was a duplicate sample. Samples were collected with a small trowel or scoop and
consisted of approximately 4 liters of surface soil collected from the intertidal shoreline near the
low tide line. Stones and organic debris were excluded as much as possible. Any remaining
debris was removed by sieving with a 16-mesh sieve during sample preparation at the laboratory.
Sediment Core. Thirty-one sediment core samples were taken at 29 sites. This included 2
duplicates, one of which was taken at a background location. Each core consisted of a 5 cm
diameter cylinder of sediment up to 51 cm in length. Sediment core samples were obtained to
evaluate the vertical distribution of radioactivity in harbor bottom sediment. Samples were
collected by divers who pushed plastic tubes into the sediment as far as possible and then capped
the ends. Excess water was decanted from the top of each core. The cores were frozen prior to
shipping and remained frozen during shipping. Before analysis, the frozen cores were cut into a
maximum of 5 segments per core with each segment having a minimum length of 5 cm.
Biota. Twenty two biota samples were collected at 17 different locations. These samples
consisted of 1 duplicate and 1 background sample and contained approximately 4 liters of one
8
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species of marine life. Samples were collected from as small a region as possible. Marsh grass
was collected on the shoreline by the EPA sampling team while mussels, sea hair, barnacles,
brown kelp, and starfish were collected by divers. Because of the interest in iodine-131, all biota
samples were counted wet by gamma spectroscopy within 7 days after collection.
2.2.2 Sample Analysis
Samples for each location were analyzed for gamma emitting radionuclides and for gross
alpha/beta activities. Of particular interest was cobalt-60 in the sediment samples and iodine-131
in the water and biota samples. All water samples were analyzed for tritium. Specific isotopic
analyses were performed on selected samples.
Gamma Spectrometry. This procedure allows for characterization of the gamma-emitting
radionuclides present in the sample without separating them from the sample matrix. The limit
of detectability of this method is a function of the sample size, counting geometry, detector
efficiency, background, counting time, gamma photon energy of the nuclide and branching ratio
(percent abundance). Liquid samples are acidified and soil or sediment samples are ground and
sieved to ensure the homogeneity of the samples. Biota samples are homogenized prior to
analysis to ensure uniformity of the sample.
Gross Alpha/Beta. This procedure, which provides a rapid screening measurement, was used
as a gross approximation of the alpha and beta activity present in the sample. Low energy and
volatile radionuclides such as tritium, carbon-14, and iodine will not be detected by this method.
In addition, polonium and cesium may be lost if the procedure requires flaming of the sample.
For water samples, a known amount of the sample is evaporated to a small volume then
transferred to a small container and further evaporated for measurement. For solid samples, a
known amount of the sample is placed on the planchet. Water is added and the sample is dried to
provide even distribution. The sample is weighed and counted on a gas proportional counter.
These analyses are not nuclide specific and are not as accurate as other types of analyses.
Tritium Analysis. Water samples are distilled and are incorporated into a counting mixture
consisting of a primary solvent, emulsifier, and fluors. The tritium is assayed in a liquid
scintillation spectrometer.
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Thames River
Q.
139
IJL I
•O- Sample Location * I
Fig. 1. Thames River Delta
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I Q Stmylf Lacatftm • \
Fig. 2. New London Harbor
11
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IJL I
%^p Smnplt Location • I
Fig. 3. Electric Boat - South
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u>
Fig. 4. Electric Boat - North
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Fig, 5. State Pier
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Fig. 6. Thames River - Waterford
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206
205
See Submarine Base
Insert on next page
169*
Thames Hive;
SanipJt Location • \
163 *
1 >ie\v London Submarine Base - South
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New London Submanne
Base - South Insert
Fig 7a New London Submarine Base-South Insert
17
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00
•22*
Thames River
•15*
I
Sample Location • I
Submarine
Bate
Fig. 8. New London Submarine Base - North
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Fig 9 Thames River-Montville
* " 19
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TABLE 1
Sample and Measurement Locations
Location ]
a
001
002
004
005
006
007
008
008-02
009
010
Oil
012
013
014
015
016
017
018
|
HH
D
EBP-9
EBP-5
EBP-2
EBS-57
EBS-47
Position b
E
o
N41.319410
N 4 1.3 1709"
N4 1.32033"
N 41. 32367°
N 4 1.32562°
N 4 1.32668°
N 41.33782°
N 41. 33782°
N 4 1.33857"
N 41.34144°
N 4 1.34660°
N 41. 34967"
N 41.35062°
N 41. 34784°
N 41.34318°
N 4 1.33948°
N 41.33913°
N 4 1.33848°
§
era
§'
0-
W 72.05605°
W 72.06644"
W 72.074 1 3°
W 72.07533°
W 72.07654
W 72.07227°
W 72.08257°
W 72.08257°
W 72.08561°
W 72.07898°
W 72.07887°
W 72.08042°
W 72.08236°
W 72.08489°
W 72.08372°
W 72.08085°
W 72.08147"
W 72.08140°
O
f
DU
CO
f
3
D.
Samples and
Measurements'
5? w o & E?
0. 0 CO ^ ^ q ^
1 § 1 g 1 1 1
§ S 8 1 3
E
E
E
E
E
E
S B W
W
S
E
E
E
E
E
E
E
S
S
Location11 Description
Jupiter Point Road, at the end of the road.
South Eastern Branch, University of Connecticut, Avery Point USGS Marker
Union Station Plant #2.
Tyler Place, Eastern Point Beach Parking Lot.
Shoreline off Shore Ave, 260 yards NE of house on Hobbs Island.
Shoreline off Shore Ave, 451 yards NE of house on Hobbs Island.
SE corner of Eastern Point Road and Plant Street (Avery disappeared for
Golf Course).
Sewer outfall Groton POTW.
Sewer outfall Groton POTW, sample taken at outfall level.
In the channel, south end of yard, next to Buoy G "7" - east side of buoy.
South Yard parking area - Lot "J" perimeter fence.
Adjacent to NE corner of Nuclear Engineering Bldg (Bldg #197) on
perimeter of fence.
Adjacent to Se corner of North Yard mock-up building (Bldg 16J) on
perimeter of fence.
On shore at far north end perimeter fence of EB.
On the water, 66 yards west of graving dock #3 at closest public access
joint.
On the water, 75 yards west of Graving Dock #1 at closest public access
joint.
On shore at far south end perimeter fence of EB.
105 yards SW of SW corner of South Yard perimeter fence, 152 yards east of
Buoy R/N"8."
141 yards east of Buoy R/N "8", 139 m SW of SW comer of South Yard
fence.
-------
TABLE 1 -Continued
ID
019
020
021
022
023
024
025
026
027
028
029
030
031
032
033
034
035
036
037
038
039
040
041
042
043
044
Navy
EBS-58
EBW-7
EBS-46
EBS-56
EBS-48
EBS-59
EBS-45
EBS-55
EBS-49
EBS-50
EBS-44
EBS-37
EBS-30
EBS-29
EBS-35
EBS-28
EBS-36
EBS-27
EBS-34
EBS-32
045 EBW-8
Latitude
N 41, 33825°
N 41. 33878°
N 41.33912°
N 41. 33959°
N 4 1.33949°
N 41. 33936°
N 41.34031°
N 41. 34073°
N 4 1.33980°
N 41. 33980"
N 4 1.34005°
N 4 1.34077°
N 41.34150°
N 41.34189°
N41.341710
N 4 1.341 77°
N 4 1.34 144°
N 4 1.34285"
N 41.34198°
N 4 1.34242°
N4 1.3428 1°
N41,34321°
N 41. 34330°
N 41 .34303
N 41. 34276°
N 4 1.34335°
N 41. 343 13°
Longitude
W 72.08221°
W 72.08264°
W 72.08250°
W 72.08123*
W 72.08245"
W 72.08300°
W 72.08234°
W 72,081 33°
W 72.08250°
W 72.08265°
W 72.08302°
W 72.08230°
W 72.08144°
W 72.08237°
W 72.08270°
W 72.083 12"
W 72.08324°
W 72.08334°
W 72.08271°
W 72.08277°
W 72.08250°
W 72.08266°
W 72.08308°
W 72.08334°
W 72.08354°
W 72.08448°
W 72.08479°
DU
DU
DU
BG
Samples & Measurements
»
W
>
s
s
s
s c
s
B
S C
S
s
s
s c
s
s c
S W
s
B
s
s c
s
B
S
s
s
W
Location Description
7 yards ESE of Buoy R/N "8", 219 yards WSW of SW corner of South
Yard fence.
8 yards northeast of Buoy R/N "8."
1 yards NE of Buoy R/N "8", 172 m west of SW corner of South Yard
fence.
47 yards west of Building 166, 182 mNE of Buoy R/N "8."
62 yards west of Building 61 , 95 m NE of Buoy R/N "8."
69 yards north of Buoy R/N "8."
.67 yards south of concrete dock, 95 yards west of gate in fence.
i 16 yards south of dolphin east of concrete dock, 23 yards offshore.
vtag Tower.
South side of Mag Range tower.
1 57 yards NNE of Buoy R/N "8", 21 8 yards west of EB.
1 S 1 yards SW of concrete dock, 246 yards NE of Buoy R/N "8. "
35 yards south of dock.
84 yards SW of SW comer of South Yard ways.
359 yards NNE of Buoy R/N "8", 231 yards south of middle wingwall.
370 yards NNE of Buoy R/N "8."
200 yards south of wingwall, 350 yards north of Buoy R/N "8."
151 yards west of South Yard ways, 122 yards south of south wingwall.
120 yards south of tight pole on west end of south wingwall.
40 yards west of SW corner of South Yard ways, 120 yards SE of light pole
on west end of south wingwall.
Due west of Building 132/256 off of South Yard ways.
40 yards south of south wingwall, 83 yards SE of light pole on west end of
south wingwall, west of Nuclear repair Facility.
Off southwest end of south wingwall.
1 20 yards south of light pole on west end of middle wingwatl.
87 yards SW of light pole on west end of middle wingwall.
109 yards west of light pole on west end of south wingwall.
142 yards west of light pole on west end of south wingwall.
-------
TABLE 1 -Continued
ID
046
047
048
049
050
051
052
053
054
055
056
057
059
060
061
062
063
064
065
066
067
068
069
070
071
Navy
EBS-33
EBS-22
EBW-6
EBS-23
EBS-25
EBS-31
EBS-21
EBS-20
EBW-5
EBS-I9
EBS-18
EBS-42
EBS-43
EBS-41
EBS-16
EBW-4
EBS-15
EBS-14
EBW-3
EBS-13
EBS-67
Latitude | Longitude
N 4 1.34368° W 72.08364"
N 41.34335° W 72.08316°
N 41.34362" W 72.08345°
N 4 1.343 1 5° W 72.08270°
N 4 1.34391° W 72.08264°
N 41. 34423° W 72.08 144"
N 41. 34441" W 72.08441°
N 41.34391° W 72.08375°
N 41.34444° W 72.08355°
N 41. 34505° W 72.08283°
N 4 1.34490° W 72.08260°
N 41.34547° W 72.08170*
N 41. 34525° W 72.08336°
N 41. 34487° W 72.08453°
N 4 1.34585° W 72.08229°
N 41. 34638° W 72.08204°
N 4 1.34665° W 72.08 188°
N 4 1.34634° W 72.08253°
N 4 1.34573° W 72.08280"
N 4 1.34624" W 72.08292°
N 4 1.34629" W 72.08304°
N 4 1.34654° W 72.08302°
N 41.34559° W 72.08355
N 41. 34585° W 72.08405°
N 41. 34627° W 72.08383°
DU
DU
DU
BG
Samples & Measurements
S
S C
S C W
W
S C
S C
S
S
S
W
S C
S
S
S
S
S C W
W
S C
S B
S C
W
S
S
S
S
Location Description
33 yards west of light pole on west end of south wingwall.
5 yards SW of west end of south wingwall.
Outfall of two graving docks, SW of middle wingwall.
35 yards south of south wingwall, 80 yards east of light pole on west end of
south wingwall.
10 yards south of south wingwall, 70 yards east of light pole on west end of
south wingwall.
20 yards south of south wingwall, 80 yards east of light pole on west end of
south wingwall.
83 yards WNW of light pole on west end of north wingwall, 220 yards SW
of "E" Dock.
15 yards north of north wingwall at west end of north wingwall.
20 yards north of north wingwall, 167 yards south of "E" Dock.
45 yards north of north wingwall, 135 yards NE of light pole on west end
of north wingwall.
265 yards SW of power plant stack, 105 yards south of "C" Dock.
67 yards south of Building #244 (Wet Dock Cafeteria), 230 yards SW of
power plant stack.
84 yards SSW end of "C" Dock.
120 yards SSW of end of "E" Dock.
50 yards SE end of "C" Dock, 120 yards south of "D" Dock.
20 yards east of "C" Dock, 80 yards south of "D" Dock.
Centered between "C" and "A" Docks, 35 yards south of "D" Dock.
5 yards east of "C" Dock, 80 yards south of "D" Dock.
17 yards off south end of "C" Dock.
Between "C" and "E" Docks, 27 yards south of "D" Dock.
Centered between "C" and "E" Docks, south of "D" Dock.
Between "C" and "E" Docks, south of "D" Dock.
SW of "E" Dock, south end.
45 yards west of "E" Dock, 1 60 yards south of south side of Land Level
Facility.
Midway on west end of "E" Dock, 45 yards out from the dock.
to
N)
-------
TABLE 1 -Continued
ID
Navy Latitude J Longitude
DU
BG
Samples & Measurements
Location Description
072
073
074
075
076
077
078
079
080
1081
082
083
084
OSS
086
087
088
089
090
091
092
093
094
095
096
EBS-66
EBW-9
EBS-68
EBS-60
EBS-61
EBS-62
EBS-65
N 41.34684° W 72.08373°
N 41.34718° W 72.08388°
N 41.34712° W 72.08325°
N 41.34706° W 72.08231°
N 41.34704° W 72.08136°
EBS-6
EBS-5
EBS-4
EBS-64
EBS-63
EBS-3
EBW-1
EBS-2
EBS-1
N 41.34716°
N 41.34727°
N 41.34826"
N 41.34893°
N 41.34944°
N 41.34925°
N 41.34808°
N 41.34826°
N 41.34890°
N 41.34913°
N 41.34993"
N 41.34994°
W 72.08421°
W 72.08464"
W 72.08431°
W 72.08388°
W 72.08495°
W 72.08357°
W 72.08257°
W 72.08206°
W 72.08183°
W 72.08226"
W 72.08276"
W 72.08289"
N 41.34973° W 72.08320°
N 41.34901°
N 41.34995°
N 41.34754°
N 41.34912°
N 41.34947'
N 41.34978°
N 41.3 5074°
W 72.08410°
W 72.08364°
W 72.085 57°
W 72.08520°
W 72.08413°
W 72.08449°
W 72.08304"
DU
DU
W
W
47 yards west of west end of "E" Dock, 46 yards south of south side of Land
Level Facility.
Centered between SW comer of Land Level Facility and west end of "D"
Dock.
10 yards north of "D" Dock at intersection of "E" Dock.
97 yards west of shore, centered between south side of Land Level Facility
and north side of D Dock.
5 yards west of shore, centered between south side of Land Level Facility
and north side of "D" Dock.
26 yards SW of SW corner of Land Level Facility.
20 yards west of Graving Dock "3" Discharge.
20 yards north of NW corner of Land Level Facility.
83 yards north of NW corner of Land Level Facility.
133 yards north of NW comer of Land Level Facility.
85 yards north of north side of Land Level Facility, 90 yards SW of dolphin
off Building 31.
North side of Land Level Facility, approximately 50 yards from shore.
20 yards north of north side of Land Level Facility, 20 yards west of
Submarine assembly/launching Building.
5 yards WSW of dolphin off "Seagull Point."
55 yards NW of dolphin off "Seagull Point", 30 yards offshore.
15 yards SW of dolphin off Building 212, 60 yards SE of "T Pier.
Inside the south side of "T" Pier, between two pilings.
25 yards west of dolphin ofTof Building 212?, 15 yards east of group of
dolphins.
170 yards north of NW corner of Land Level Facility.
Center of SW side of'T' Pier, 20 yards out from pier.
110 yards WSW of Co2j tank.
133 yards west of Co2 tank.
60 yards west of Co2j tank.
90 yards west of Co2jtank.
20 yards west of shore at north end of perimeter fence of EB.
-------
TABLE 1 -Continued
ID
097
098
099
100
101
102
103
104
104-02
105
106
107
108
109
no
111
112
113
114
115
116
117
118
119
120
121
Navy
SPS-1
SPS-40
SPS-38
SPS-6
SPS-9
SPS-25
SPS-13
Latitude [ Longitude
N 41. 34 113° W 72.08373°
N 41.35158° W 72.08673"
N41.3467T W72.08189"
N 4 1.392 10° W 72.09053°
N 41.37807" W 71. 95629"
N 4 1.35079" W 72.08284°
N 41.35221° W 72.08318°
N 4 1.35445° W 72.08479°
N 41.35445" W 72.08479°
N 41.35713° W 72.08485°
N 41.36175" W 72.08470°
N 41 .36328° W 72.08501°
N 41.36366° W 72.091 19°
N 41.36088° W 72.09087°
N 4 1.36270° W 72.08791°
N 4 1.36 176° W 72.089 1 3°
N 4 1.36053° W 72.08883°
N 41. 36065° W 72.09020°
N 4 1.35980° W 72. 09009°
N 41. 35976° W 72.08969°
N 4 1.3 5955° W 72.08861°
N 4 1.35962° W 72.09083°
N 4135922° W 72.09039°
N 41.35879° W 72.08950°
N 4 1.3 5947° W 72.08934°
N 41. 35770° W 72.08890°
DU
DU
DU
DU
BG
BG
Samples & Measurements
S W
s
D
D
D
E
E
S B W
W
E
E
E
E
E
S
S
S
s
S
s
s c
s c
s
s
s
s
Location Description
Center of private pier beyond north end of perimeter fence of EB.
Buoy G "13" - next to buoy on East side.
Drinking water from Wet Dock at EB,
Drinking water, Building 79, NLSB.
Drinking water, Residence Inn, 40 Whitehall Avenue, Mystic, CT.
Parking lot just ofFof Thames St, north of the northern most boundary of
EB.
Croaker memorial, just off of Thames Street.
Sewer outfall forGroton.
Sewer outfall for Groton, sampled at outfall level.
Point off of Thames Street and School Street.
Point off of Thames Street, between Broad Street and Bridge Street.
Off of Buell Street, underneath the 1-95 north bound bridge on the east shore
of the Thames.
Underneath the 1-95 north bound bridge on the west shore of the Thames.
Off of the 16s1 Street shoreline.
Midway of first span of Bascule Bridge and 50 feet south.
25 yards east of wooden pierhead and 125 yards south of Bascule Bridge.
8 yards north from first dolphin from shore.
Second set of bollards along quaywall from the north end of State Pier and 3
•ards east from shore,
Beside north side of forward mooring deck pilings.
leside north side of second mooring deck pilings.
Beside north side of last mooring deck pilings, approximately 83 yards from
lore.
ktween south side of forward (1st) mooring deck piling and north side of
tate Pier.
yards out from State Pier adjacent to B2 bollard, north side of pier.
0 yards from State Pier adjacent to B8 bollard.
0 yards south of middle set of mooring deck pilings.
North side of State Pier, 20 yards from end of the pier 2 yards out.
N)
-------
TABLE 1 -Continued
ID Navy Latitude
122
123
124
125
126
127
128
129
130
131
132
133
133-02
134
135
136
137
138
139
140
142
143
144
145
146
147
SPS-34
SPS-23
SPS-20
NUS-1
NUS-2/
NUW-1
NUS-3
NUS-4
N 4 1.35765°
N 4 1.35784°
N 4 1.35720°
N 4 1.35882°
N 41. 35352°
N 41.34559°
N 41. 34495°
N 41. 34494°
N 4 1.34479°
N 4 1.34477°
N 4 1.34439°
N 41.34156°
N 41. 34156°
Longitude DU BG
W 72.08899°
W 72.090 18°
W 72.09245°
W 72.09382°
W 72.09338°
W 72.09017°
W 72.09074°
W 72.08996°
W 72.08997°
W 72.09137°
W 72.09126°
W 72.08839°
W 72.08839°
N 41. 34266° W 72.09467°
N 41.33740° W 72.09979°
N 4 1.33268° W 72.09593°
N 41.32895° W 72.09146°
N 4 1.32347° W 72.08868°
N 41. 32165
0 W 72.085 11°
N 41.31748° W 72.09008°
N 4 1.31463° W 72.09332°
N 4 1.3 11 65° W 72.09451°
N 41. 30919° W 72.09653°
N 41. 38665° W 72.08660°
N 41. 38739° W 72.08778°
N 41. 39588° W 72.09258°
DU
Samples & Measurements Location Description
S C '
:
s
s
s
E
S
S W
s
s
s c
s
S B W
W
E
L E
E
L E
E
S
E
E
E
E
E
L E
E
Morth side of State Pier, Bumper 4 from head of pier, approximately 23
^ards from head of pier.
I yards out from bollard #4.
Midway between Long Dock and New London shore
Midway between Long Dock and New London shore and 1 5 yards south
from northern shore by fuel tank.
South Water St. between Pearl St. and Captain Walk/State St., 54 yards to
train station at pole 122/79.
1 00 yards north of shore power boom on Pier 7N adjacent to Buoy # 1 .
2 yards out from Pier 7N, adjacent to shore power bunker.
2 yards our from Pier 7N adjacent to camel.
10 yards out from Pier 7S adjacent to shore power.
2 yards out from Pier 7S, approximately 250 yards from shore.
2 yards out from Pier 4N adjacent to bollard.
Sewer outfall for City of New London.
Sewer outfall for City of New London, sampled at outfall level.
South end of East Street.
Greens Harbor beach.
Empty lot across the street from 313 Pequot Avenue.
Mitchell College beach.
Shoreline, Pequot Avenue at Chapel Street.
Mouth of Thames River, west side of river near Buoy G "5", 1 78 yards west
of buoy.
Across from 787 Pequot Avenue.
Shoreline, corner of Pequot Avenue and Lower Boulevard.
Across the street from 1011 Pequot Avenue.
Ocean Beach Park, next to 76 Mott Avenue gate to shoreline at corner of
Ocean Avenue and Mott Avenue.
Shoreline off of Military Highway, south of the USS Nautilus Museum.
Shoreline off of Military Highway, at the USS Nautilus Museum, south of
Submarine Base.
Shoreline at corner, 30 yards to Naval Sub Support Facility Hq,
approximately 1 1 yards to Building 91 at YRR-14.
-------
TABLE I-Continued
ID
148
149
150
151
152
153
154
155
156
157
158
159
160
161
162
363
164
165
166
167
168
169
170
171
172
173
174
Navy
SBW-7
SBW-1
SBS-1
SBS-2
SBS-40
SBS-36
Latitude | Longitude
N 41.39868° W 72.09321°
N 41 .40151* W 72.09343°
N 1.403 13" W 72.09344-
N 41.40454° W 72.09344°
N 4 1.40592" W 72.09340"
N 4] .40718" W 72.09336°
N 4 1.40686° W 72.091 97°
N 4 1.40361° W 72.09228°
N 41.40033° W 72.09241"
N 4 1.41049° W 72.09254"
N 41.39975" W 72.09522"
N 41 39433" W 72.09405°
N 41 .38750° W 72.08838°
N 41.38671° W 72.08786°
N 4 1.38709" W 72.08840"
N 41. 39008° W 72.08993"
N 4 1.39086° W 72.09058°
41.39133° W 72.09047°
41.39110° W 72.09079°
41.39067" W 72,09 123°
N41.390290 W 72.09212°
N 4 1.38748° W 72.092 14"
N 41. 39016° W 72.09657°
N 41.39241" W 72.09123°
N 41.39241" W 72. 09157°
N 41.39205° W 72.09224°
N 4 1.39 178" W 72.09223"
\75 \ SBS-35 | N 41.39254° W 72.09201"
DU
BG
Samples & Measurements
E
E
E
E
E
E
E
E
E
E
E
E
W
S
S
S
S
s c
s
s
W
s
S B
S
S
S
s
1 s
Location Description
Shoreline, lower base, near Building 478.
Shoreline, lower base, near Building 174.
Shoreline, lower base, near Building 175.
Shoreline, lower base, near Building 176.
Shoreline, lower base, near Building 387.
Shoreline, lower base, near Building 181,
Base Golf Course, neartfl Tee box.
Base Golf Course, at #3 Tee box next to hole #2 green.
Base Golf Course, behind hole #3 green.
Shoreline at far north perimeter fence of NLSB.
On water 5 7 yards west of Pier 3 1 at closest public access point.
On water 44 yards west of Pier 12 at closest public access point.
20 yards NW from the corner of Nautilus Pier.
7 yards off the southern tip of the Nautilus pier.
7 yards straight out from the midpoint of the Nautilus pier.
3 yards west of (f cleat from the north end of Pier 1 .
yards south of the center of Pier 2.
yards off north side of Pier 2, approximately 13 yards from shore.
yards north o f the center o f Pier 2 .
yards off of north side of Pier 2, west end of Pier.
1 yards straight oul - midway between Piers 2 and 4.
0 yards east of Buoy G "9. "
0 yards south of Mamacoke Hill between the pilings.
Midway between Piers 4 and 6, 33 yards from roadway (shore).
0 yards oul from the 3rf cleat on the south side of Pier 6 (Barge next to
ier).
7 yards out from west end of Pier 6.
Midway between Piers 4 and 6, 100 yards out,
yards out from the 3"1 cleat on the north side of Pier 6.
to
o\
-------
TABLE 1 -Continued
W
ID
176
177
178
179
180
181
1S2
183
184
185
186
187
188
189
190
191
192
193
194
195
196
197
198
199
200
201
202
203
Navy
SBS-3
SBS-34
SBS-41
SBS-25
SBS-6
SBS-8
SBW-2
SBS-7
SBS-4
SBS-10
SBS-9
SBS-13
SBW-3
SBS-15
SBS-14
SBS-12
SBS-18
SBS-30
Latitude | Longitude
N 41.39326° W 72.09212°
N 41.39381° W 72.09180°
N 41. 39348° W 72.09239°
N 41 .39292° W 72.09273"
N 4 1.39429° W 72.09250°
N 41 .391 10° W 72.09342°
N 41. 39407° W 72.09296°
N 4 1.39535° W 72.092X8°
N 41.39513° W 72.09325°
N 4! .39480° W 72.09325°
N 4 1.39410° W 72.09376*
N 41. 39275° W 72.09539°
N 41. 39315° W 72.09570°
N 41.39461" W 72.09395°
N 4 1.39509" W 72.09368°
N 4 1.39508° W 72,09376"
N 4 1.395 16° W 72.09343°
N 4 1.39581" W 72.09296°
N4 1.395 59° W72.09330"
N 41. 39570° W 72.09348°
N 41.39518° W 72.09384°
N 4 1.39547' W 72.09377°
N4 1.39607° W 72.09343°
N 4 1.3961 5° W 72.09346°
N 4 1 .39638° W 72.09323°
N 4 1.39645° W 72.09389°
N 4 1.39624" W 72.09432°
N41. 39695° W 72.09372°
DU
DU
BG
Samples & Measurements
S C
S
S
S
S C
S
S
S
S
W
S
S
S
S
S
W
S C
S C B
W
S
S
B
W
S
S
S C
S
W
Location Description
} yards out from midway of south side of Pier 8.
} yards out from the north side of Pier 8, approximately 7 yards from shore.
17 yards north of the midway point of Pier 8.
3 yards out from the north side of Pier 8, west end of pier.
I yard out from south side of Pier 10, 5 cleats out from shore.
Mid channel in line with the NLSB power plant northern most smoke stack
and chimney at Connecticut College.
3 yards out ftom the north side of Pier 10, midway of pier.
3 yards out from the south side of Pier 12, approximately 27 yards from
shore.
South side of Pier 12, 20 pilings from end of pier about 1 yard out.
South side of Pier 12, twelve pilings from end of pier, 26 yards straight out.
10 yards straight out from the midpoint between the ends Piers 1 0 and 12.
Mid-channel straight out from the midpoint between the ends of Piers 10 and
12..
Mid-channel straight out from the midpoint between the ends of Piers 12 and
13.
30 yards straight out from the north comer of Pier 12.
North side of Pier 12, 3'J cleat from the end of the pier and 10 yards out,
North side of Pier 12, 20 pilings from end of pier, 22 yards straight out,
3 yards off the north side of Pier 12, midpoint of pier.
Starboard side of Radeon barge, 2 yards forward of the RLW connection.
Mid-channel of Piers 12 and 13, 51 yards to Radeon Barge YRR-S4.
South side of Pier 13, 20 pilings from the end of the pier and 1 yard out.
Midway between Piers 12 and 13, in line with the ends of the two piers.
Between Piers 12 and 13.
North side of Pier 13, 10 yards out from 3rt bollard from the end of pier.
South side of Pier 13, 20 pilings from the end of the pier and 1 yard out.
Midway between Piers 12 and 13, in line with the ends of the two piers.
Midpoint between north Pier 13 and south Pier 15.
33 yards south of Pier 1 5, in line with the end of the pier.
South side of Pier 1 5, 24 yards from shore and 44 yards from pier.
-------
TABLE 1 -Continued
ID
204
205
206
207
208
209
210
211
212
213
214
215
216
217
218
219
220
221
222
223
224
Navy
SBS-21
SBS-20
SBS-43
SBS-42
SBS-46
SBS-44
SBS-45
SBS-48
SBS-23
Latitude | Longitude
N 41.39681° W 72.09406°
N 41. 39495° W 72.09874°
N 4 1.39750° W 72.09897°
N 4 1.39749° W 72.09428°
N 4 1.39822" W 72.09320°
N41.39837" W 72.09359°
N 4 1.39794° W 72.09483"
N 41. 40008" W 72.09331°
N 41.40001° W 72.09409°
N 41.40013° W 72.09421°
N 4 1.40020° W 72.09425°
N 41. 40085° W 72.09376°
N 41.40084° W 72.09416°
N 41. 39991° W 72.09537°
N 4 1,40 196° W 72.09348°
N 41.401 19° W 72.09430°
N 41.40157° W 72.09439°
N 41. 40283° W 72.09381°
N 41.40231° W 72,09427°
N 41.40076° W 72.09775°
N 4 1.403 19° W 72. 093 82°
1225 1 SBS-47 N 41. 40287° W 72.09484°
U26 \ \N 41.40624° W 72.09401°
I I \
DU
DU
DU
BG
Samples & Measurements
S
s c
S
s
s
s
s
s
s
S W
B
S
s
s
B
S
s
s c
s
s
s
s
s
Location Description
1 yard out from the south side of Pier 15, opposite the main shore power
connection.
80 yards out from the northern point of Mamacoke Hill, in line with buoy G
"11."
Straight out from the south end of the railroad bridge at Smith Cove, in line
with the end of the fueling pier on the west side of the river.
37 yards out from the north side of Pier 1 5, opposite the main shore power
connection - Dry dock in place.
5 yards out from Berth 19, opposite the fire alarm box.
Midway between Beth 16 and Pier 1 7, JO yards out from the quay wall.
Midway between Piers 1 5 and 1 7, straight out from the two red marks on
Pier 15.
1 3 yards straight out from the south side of Pier 3 1 , 20 yards from shore.
13 yards straight out from the shore power booms on the south side of Pier
31.
1 3 yards out from the shore power booms on the north side of Pier 3 1 .
Pier 31 norm, 42 yards from end of pier (Ft Marker).
13 yards out from south side of Pier 32, approximately 27 yards from shore.
13 yards straight out from the shore power boons on the south side of Pier
32,
Midway between Piers 3 1 and 32, in line with ends of the piers.
Between Piers 32 and 33, quay wall.
13 yards straight out from the shore power boons on the north side of Pier 32
Midpoint between north Pier 32 and south Pier 33.
13 yards straight out from the south side of Pier 33, approximately 17 yards
"rom shore.
1 3 yards straight out from the shore power booms on the south side of Pier
33.
7 yards from the south end of the fueling pier on the West side of the river.
13 yards straight out from the north side of Pier 33, approximately 20 yards
rom shore.
1 3 yards straight out from the shore power booms on the north side of Pier
33.
3 yards off the south side of Marina Pier, 3rd piling, approximately 20 yards
from shore.
K)
00
-------
TABLE 1 -Continued
ID Navy Latitude
to
VQ
227
228
229
230
31
32
33
34
235
236
236-02
237
238
239
240
241
242
243
244
245
246
247
248
249
SBS-24
SBW-6
N 4 1.40632°
N 4 1.40597"
N 4 1.40874°
N 4 1.40942°
N 41.41308°
N 41. 42575°
N 4 1.43060°
N 4 1.44085°
N 4 1,44462°
N 41 .43870"
N 4 1.43870°
N 41.43914°
N 41. 40390°
Longitude
W 72.09475°
W 72.09548°
W 72.09474°
W 72.09143°
W 72.08733°
W 72.09003°
W 72.09369°
W 72.09675°
W 72.08520°
W 72.09714°
W 72.097 14°
W 72.09567°
W 72.10599°
N 41.42699° W 72.10216°
N 4 1.42390° W 72.09874°
N 41. 40121° W 72.09929°
N 4 1.39708
° W 72. 10251°
N 4 1.38757° W 72.09804'
N 41. 39275
W 72. 10084°
N 4 1.39282° W 72.09747°
N 4 1.38060° W 72. 10090°
N 4 1.37857° W 72.09851°
N 4 1.37 128° W 72.09667°'
N 41. 36484° W 72.09500°
DU
DU
DU
DU
BG Samples & Measurements Location Description
BG
BG
BG
BG
S
W
s
E
E
E
E
B L E
S
S B W
W
S C W
E
E
E
L E
E
E
B L E
L E
E
E
E
E
7 yards straight out from the Marina Pier.
Midstream, straight out from the Marina Pier.
Between Buoy G "1" and Sub Base, approximately 300 yards north of the
Marina Pier.
North Gate of Submarine Base on Military Highway.
Shoreline Military Highway, between Long Cove Road and Mill Cove Road.
Cul de sac at south end of Bluff Road.
Shoreline, Shore Point off of Riverside Place and Hurlbutt Road (near Yale
Boathouse).
Uncasvilie, end of Cove Road.
Mid-channel west of Dow Chemical Co, 83 yards West of Marker 12.
Sewer outfall for Montville, shore next to railroad bridge.
Sewer outfall for Montville, shore next to railroad bridge, sampled at outfall
level.
50 yards out from railroad track, West side of River off of Breeze Point.
End of Powerhouse Road, comer of Powerhouse Road and Lanthrop Road.
Shoreline, unmarked road off of Lanthrop Road that leads down to Northeast
Utilities, near Bartlett Cove.
End of Bartlett Road, near Bartlett Point.
Scotch Cap Road, due west of Sub Base.
South of Smith Cove, end of Richards Grove Road, due west of Sub Base.
End of Benham Avenue near Mamacoke Cove.
Shoreline, west side of Mamacoke Hill.
Shoreline, east side of Mamacoke Hill, due west of Sub Base Pier 12.
End of Saltonstall Street.
Shoreline, end of Farnsworth Street.
US Coast Guard Academy, on the Eagle Road, near the pier.
Corner of Lewis Street and Eastern Avenue.
Navy symbols are explained on page 7.
Latitude and longitude are given in degrees and decimal degrees.
c Sample and measurement codes are explained on page 7.
Water samples were collected at a depth of 1 m unless otherwise specified.
-------
3.0 RESULTS AND DISCUSSION
The radioanalytical results for the NLHF samples collected during this survey are reported in the
Appendix. The tables were generated from Data Quality Packages (DQPs) produced from
radioanalytical results. The quality assurance/quality control (QA/QC) results for the laboratory
analyses and field sample QA/QC were presented in the DQPs for the sample analyses, and the
results were within acceptable limits as specified in the Quality Assurance Project Plan (EPA97)
for this survey. Some of the reported radionuclide activity results are negative. Negative results
occur when a previously determined background value is subtracted from a sample value that is
less than the background value. Negative values represent a portion of the statistical distribution
of negative and positive values around zero for samples containing very little or no detectable
radioactivity.
3.1 Water Samples
3.1.1 Surface Water Samples
The gamma analysis results for the 33 surface water samples are shown in Table A.L Only
naturally occurring radionuclides were detected in surface water samples collected from withm
the area defined as the NLHF. Iodine-131 atalevelof 6.1 ±3.5 pCi/L wasdete ctedatthe
discharge pipe location at the Montville Station Public Owned Treatment Works (POTW) ewer
outfall The most likely source of this 1-131 is from medical use in the load population with
resultant discharge of excreta into the sewage. Iodine-131 is used ,n clinical medicine for the
treatment of hyperthytoidism and thyroid cancer. Excreta from ^dividual* undergoing medical
diagnosis or therapy with radioactive material is exempt from the U.S. Nuclear Regulatory
Commission (NRC) regulations for the discharge of radioactive materials iinto municipal sewage
systems in accordance with the Code of Federal Regulations, Title 10, Part 20.2003(b).
Tritium analyses were performed on all 33 surface water ^^^^J1
A.2. Tritium concentrations in the surface water samples collected at NLHF were
those collected at the background location (NLHF237). All of these concentrations were below
the minimum detectable concentration (MDC) of about 140 pCi/L.
Results of the gross alpha and beta analyses of the 33 surface water samples are presented in
Table A 3 Using the K-40 gamma spectrometry data, the surface water background is not
represenfativeTf the sampling locations. Beta readings are consistent with expectations based on
the K-40 data.
3.1.2 Drinking Water Samples
The gamma analysis results for the five drinking water samples are shown in Table A.4. Only
naturally occurring radionuclides were detected in drinking water samples.
31
-------
Tritium analyses were performed on all five drinking water samples. Results are presented in
Table A. 5. Tritium concentrations in the drinking water samples collected at NLHF were similar
to those collected at the background location (NLHF 101). All of these concentrations were
below the minimum detectable concentration (MDC) of about 140 pCi/L.
Results of the gross alpha and beta analyses of the five drinking water samples are presented in
Table A.6. The drinking water samples had maximum gross alpha and beta concentrations,
respectively, of 0.50 ± 0.41 pCi/L and 2.4 ± 2.6 pCi/L. The National Drinking Water
Regulations (FROO) state that the maximum allowed gross alpha particle radioactivity in
community water systems is 15 pCi/L (including radium-226, but excluding radon and uranium).
Gross alpha concentrations in the NLHF drinking water samples were below the maximum
allowed gross alpha activity in drinking water for community water systems. Therefore, the
NLHF samples meet the drinking water regulation.
3.2 Sediment and Sediment Core Samples
3.2.1 Harbor and Shoreline Sediment Samples
The gamma analysis results for harbor and shoreline sediment samples are shown in Tables A.7
and A.8. All samples were counted on a germanium detector for 1000 minutes. Cobalt-60 was
detected in some sediment samples. The highest cobalt-60 concentrations were 1.820 pCi/g-dry
at EB, 0.074 pCi/g-dry at State Pier, and 0.062 pCi/g-dry at NLSB. The cobalt-60 MDCs for
sediment samples were in the range of 0.013 to 0.029 pCi/g-dry due to the detector used and the
sample size. The presence of cobalt-60 was expected based upon previous surveys conducted by
NAREL at this harbor.
To verify that the cobalt-60 measured in this survey is from previous operations and not newly
deposited cobalt-60, the Thames River and New London harbor were divided into eight sections
since cobalt-60 contamination varied widely in various sections of the river. For each of the
eight sections, a half-life for cobalt-60 was calculated using the average concentrations from the
results of the 1972,1989, and 1999 surveys. The half-lives of cobalt-60 in each section ranged
from 4.1 to 6.6 years. An uncertainty analysis of the half-lives for each section shows
satisfactory overlap with the expected cobalt-60 half-life of 5.27 years. Thus, it appears that the
cobalt-60 concentrations are lowering at the expected rate, suggesting that the cobalt-60 is
present from previous releases and that no new measurable releases of cobalt-60 have occurred.
Cobalt-56 was detected in one sediment sample. This was not expected. Upon further review of
the gamma radiation spectrum for this sample (NLHF048-S), there is some question concerning
whether cobalt-56 was actually present, or whether interference from naturally occurring Bi-21*
in the 1238 keV gamma peak caused the computer softwear algorithm to erroneously indicate the
presence of cobalt-56. Coupled with the fact that cobalt-56 is not a nuclide expected to be
detected from nuclear reactor operations (ANS99), the presence of cobalt-56 is concluded to be
unlikely m that sample. Further supporting this conclusion, cobalt-58 would have been expected
32
-------
to be detected before cobalt-56 (ANS99); however, no cobalt-58 was detected.
Results of the gross alpha and beta analyses of harbor and shoreline sediment samples are
presented in Table A.9. The maximum total gross alpha and beta concentrations, respectively,
were 19.9 ± 5.5 pCi/g-dry and 39.2 ± 5.0 pCi/g-dry in samples collected from NLHF; 12.1 ± 4.3
pCi/g-dry and 29.3 ± 4.3 pCi/g-dry in samples collected at the public water treatment outfall;
and 9.2 ± 4.0 pCi/g-dry and 24.3 ± 4.1 pCi/g-dry in samples from background locations.
Sediment samples from NLHF have gross alpha and beta concentrations similar to the
background and public water treatment outfall samples.
3.2.2 Sediment Core Samples
Gamma analysis results for the sediment core samples are shown in Tables A. 10 and A. 11. The
maximum cobalt-60 concentration measured in a core sediment sample was 0.534 pCi/g-dry.
The cobalt-60 MDCs were in the range of 0.025 to 0.106 pCi/g. The presence of Co-60 was
discussed above The samples contained naturally occurring radioactivity and radioactivity
consistent with levels expected from fallout due to atmospheric nuclear tests and the Chernobyl
reactor accident.
Results of the gross alpha and beta analyses of sediment core samples are shown in Table A. 12.
Gross alpha and beta concentrations in sediment core samples at NLHF are similar to
concentrations found in sediment core samples at the background location.
3.3 Biota Samples
Gamma analysis results for the 22 biota samples are shown in Tables A. 13 and A.M. Cobalt-60
readings were below the MDC. Iodine-131 was detected in 11 biota samples. The source of this
1-131 is most likely from medical use in the surrounding population. Other radionuchdes
detected in biota are naturally occurring or radioactivity consistent with levels expected from
fallout due to atmospheric nuclear tests and the Chernobyl reactor accident.
Results of the gross alpha and beta analyses of biota samples are presented in Table A. 15.
Samples collected from NLHF have concentrations similar to those found in the background
samples. The gross beta readings for brown kelp at the site locations ranged from 5.77 to 10.17
pCi/g-wet and the only sea hair sample registered 11.76 pCi/g-Wet. These compare with a
reading of 2.76 pCi/g-wet for a background marsh grass sample.
3.4 External Gamma Radiation Measurements
External gamma radiation measurements were made along the shoreline and on the water at
NLHF with emphasis on areas accessible to the public. M™—*™**™^™1?
minutes during the survey with a Genitron Instruments Gamma TRACER GM type survey
instrument Readings were downloaded at each external monitoring location. External exposure
33
-------
readings were also taken for 5 to 10 minutes at each location with a Reuter-Stokes pressurized
ion chamber (PIC). A Ludlum Model-19 was also used to measure variation in exposure rates
along the shoreline at each location. Results of the external gamma radiation measurements are
shown in Table 2. Radiation levels measured were similar to background.
34
-------
TABLE 2
External Gamma Radiation Measurements
Location ID
NLHF001-E
NLHF002-E
NLHF004-E
NLHF005-E
NLHF006-E
NLHF007-E
NLHF010-E
NLHF011-E
NLHF012-E
NLHF013-E
NLHF013-E-DU
NLHF014-E
NLHF015-E
NLHF016-E
NLHF102-E
NLHF103-E
NLHF105-E
NLHF106-E
NLHF107-E
NLHF108E
NLHF109-E
NLHFI26-E
NLHF134-E
NLHF135-E
NLHF136-E
NLHF137-E
PIC Exposure Rates
HR/hr
10.7
7.8
7.9
8
8.3
8.7
8.7
8.7
8.3
10.1
10.1
3.7
3.4
4.4
__ • — •
8.5
.^___— — — —
9.2
8.8
_^— ^— — -
8.9
9.3
— — —
9
_— — —
8.6
— • •
8.8
9.9
_ •
6.6
8.6
. .
5.9
_ . L
GENITRON Exposure
Rates
HR/hr
13
9
11
9
10
10
11
9
10
10
13
No Reading
No Reading
6
11
12
9
9
11
12
9
11
13
9
•
11
8
Ludlum ModeI-19
Exposure Rates
liR/hr
11
11
10
8
10
14
13
11
12
13
13
1-2
1-2
5
10
12-13
10
10
12
13
10
12
13
7-9
9
6
35
-------
TABLE 2 (Continued)
External Gamma Radiation Measurements
Location ID
NLHF138-E
NLHF140-E
NLHF142-E
NLHF143-E
NLHF144-E
NLHF145-E
NLHF145-E-DU
NLHF146-E
NLHF147-E
NLHF148-E
NLHF149-E
NLHF150-E
NLHF151-E
NLHF152-E
NLHF153-E
NLHF154-E
NLHF155-E
NLHF156-E
NLHF157-E
NLHF158-E
NLHF159-E
NLHF230-E
NLHF231-E
NLHF232-E
NLHF232-E-DU
NLHF233-E
PIC Exposure Rates
\iSJhr
8.2
11.2
8.1
9.3
6.4
10
8.7
7.6
13
7.2
8.5
8.4
7.1
6.6
7.3
8
8.7
8.9
5.5
3.5
4.7
9.5
8.5
9
9.3
8.8
GENITRON Exposure
Rates
uR/hr
10
14
10
13
10
10
11
10
13
9
11
10
9
9
10
No Reading
No Reading
No Reading
6
No Reading
No Reading
12
11
12
13
13
Ludlum Model-19
Exposure Rates
fjR/hr
10
15
7
12
7
11
12
8
18-20
8
8
7
7
7
8
13
13
12
3-4
1-2
2
13
10
12
12
8
36
-------
TABLE 2 (Continued)
External Gamma Radiation Measurements
Location ID
NLHF234-E-BG
NLHF238-E
NLHF239-E
NLHF240-E
NLHF241-E
NLHF241-E-DU
NLHF242-E
NLHF243-E
NLHF244-E
NLHF245-E
NLHF246-E
NLHF247-E
NLHF248-E
NLHF249-E
PIC Exposure Rates
jiR/hr
9.4
8.9
7.7
10.8
8.6
8.9
8.9
8.6
5
5.7
9.9
10
8.4
8.9
GENITRON Exposure
Rates
uR/hr
12
9
8
12
10
11
11
9
6
6
10
10
10
10
Ludlum Model-19
Exposure Rates
UR/hr
11
No Reading
10
16
11
11
12
11
11
1 6
15
13
10
11
37
-------
4.0 QUALITY ASSURANCE/QUALITY CONTROL (QA/QC)
4.1 The Quality Assurance Program
The NAREL Quality Assurance (QA) Plan applies to all work performed at NAREL. The
purpose of the quality assurance program is to ensure that all measurements performed at
NAREL are valid, scientifically defensible, and of known precision and accuracy. The NAREL
Quality Assurance Project Plan (QAPP) for the U.S. Navy Environmental Studies (EPA 97) was
prepared in accordance with the requirements described in "EPA Requirements for Quality
Assurance Project Plans for Environmental Data Operations" (EPA94).
Quality Assurance/Quality Control (QA/QC) for the laboratory analyses performed for this
survey is detailed in the QAPP (EPA97). Quality control (QC) samples are analyzed in
conjunction with routine samples to ensure the quality of the analytical results. Corrective
actions must be taken when it is shown by the results of QC samples that the radioanalytical
procedure is beyond predetermined control limits. Quality assurance is equally important in the
sample collection process. All documentation including chain-of-custody forms were properly
completed. Sampling equipment was in good working order and field measurement equipment
was calibrated and properly maintained.
4.2 Quality Control Samples
Field and laboratory quality control samples were included with site samples to help evaluate the
entire sampling and analysis process. Evaluation of QC samples allows assessment of the
accuracy and precision of the analytical procedures. The field duplicate results assess the
consistency of the sampling process and the representativeness of the samples collected.
In the laboratory samples were grouped in batches for quality control purposes, with a maximum
of 20 samples per matrix per analysis type. For each batch, the laboratory analyzed a reagent
blank, a matrix spike, a matrix spike duplicate, and a laboratory replicate sample. However, for
gamma spectrometry and gross alpha and beta analyses, only a recount (duplicate) or split was
performed for batch QC. Results of these QC samples were reviewed with sample results as part
of the data verification and review process. Specific criteria for acceptance were included m the
QAPP (EPA97) All blank results were maintained on control charts by analyst, matrix, and
analyte. Warning and rejection limits were used to assess acceptance of the blank results. No
substantial corrective actions were required during the processing and analysis of the samples for
this survey Radioanalytical sample results complied with the terms and conditions of the QAPP
as certified by the NAREL Quality Assurance Coordinator and the Chief, Monitoring and
Analytical Services Branch.
39
-------
4.3 Performance Evaluation Programs
It is NAREL policy to participate in many inter laboratory comparisons of radioactivity
measurements and cross-check programs. NAREL participates in intercomparison QA studies
with the National Institute of Standards and Technology (NIST) in Gaithersburg, MD; the World
Health Organization (WHO) in Le Vesinet, France; the International Atomic Energy Agency
(IAEA), Vienna, Austria; the U.S. Department of Energy (DOE) Radiological Environmental
Science Laboratory in Idaho Falls, ID; the DOE Environmental Measurements Laboratory (EML)
in New York, NY and Analytics, a commercial company in Atlanta, Georgia.
40
-------
5.0 CONCLUSIONS
The following conclusions apply to conditions as found during the radiological survey conducted
September 13-24, 1999, at the New London Harbor Facilities:
1. Trace quantities of cobalt-60 were found in the Sediment. When compared to previous survey
findings, cobalt-60 concentrations had decreased at an expected rate. It is possible that cobalt-
60 is present from previous operations and not newly deposited.
2. Cobalt-60 was not detected in biota or water samples.
3 Iodine-131 was detected in a water sample at the Montville Station POTW sewer outfall and in
eleven biotaTsamples. The source of this iodine is most likely due to excreta from individuals
in the general population undergoing medical diagnostic or therapeutic procedures.
4 Other radionuclides identified in the media collected in this survey are typically found in the
• VyUllCI IttLlIUlltlVIiM-WO j.v*w.ij.fc»*- £.__.. n+vvtsvcmltanf* 13LW»arW^T1C
j . *, »iur /wMim'np radioactivity or fallout from atmospheric weapons
pnT/irr\ritTif»nt nup tn natlirailV Olyt
-------
6.0 REFERENCES
ANS99 "Radioactive Source Term for Normal Operations of Light Water Reactors,"
American Nuclear Society, La Grange Park, IL, ANSI/ANS- 18.1-1 999.
Ca66 Cahill, D.F., Breakfield, W.D., and McCurry, D.C., Radiological Survey of Thames
River, Connecticut, and Environs, 1966 Department of Health, Education, and
Welfare, U.S. Public Health Service, Southeastern Radiological Health Laboratory
Technical Report, July-August 1966.
Ca77 Callis, R.S., Windham, S.T., and Phillips, C.R., 1977, Radiological Survey ofPuget
Sound Naval Shipyard, Bremerton, Washington and Environs, U.S. Environmental
Protection Agency Report, February 1977, EPA 520/5-77-001.
Ca87 Callis R S., 1 987, Radiological Survey of the Pearl Harbor Naval Shipyard and
Environs, Honolulu, Hawaii, USEPA Report, June 1987, EPA 520/5-87-010.
Do99 Douville, R.A., Electric Boat Corporation, Groton, CT., Personal communication,
July 1999.
EPA94 U S Environmental Protection Agency, Quality Assurance Management Staff (now
Quality Assurance Division), 1994, EPA Requirements for Quality Assurance Project
Plans for Environmental Data Operations, U.S. Environmental Protection Agency
Report, Draft Interim Final, August 1994, EPA QA/R-5.
EPA97 U S Environmental Protection Agency, 1 997, Work Plan for Environmental Surveys
at U.S Naval Stations-Quality Assurance Project Plan, U.S. Navy Environmental
Surveys, National Air and Radiation Environmental Laboratory, Draft, September 5,
1997, IAG/QAPP-1.
EPA99 U S Environmental Protection Agency, 1 999, Work Plan for Radiological Survey of
Naval Facilities in the New London Harbor and on the Thames River, Connecticut,
National Air and Radiation Environmental Laboratory, August 31,1 999.
EPA04 2004, Radiological Survey at the Kings Bay Naval Submarine
Environmental Protection Agency Report, October 2004, EPA-402-R-04-004.
Fo98 Fowler T W and Cox, C., 1998, Radiological Survey at the Puget Sound Naval
Shipyard and Naval Submarine Base - Bangor, U.S. Environmental Protection
Agency Report, July 1998, EPA-402-R-98-003.
43
-------
Fo03 Fowler,!.W., and Poppell, Jr., S.W., 2003, Radiological Survey at the Naval Nuclear
Power Training Unit, U.S. Environmental Protection Agency Report, August 2003,
EPA-402-R-03-002.
FROO Federal Register, Vol. 65. No. 236, National Primary Drinking Water Regulations;
Radionuclides; Final Rule, pp. 76708-76753, 65 FR 76708, December 7,2000.
Go99 Goodman, R. A., 1999, Radiological Survey of Naval Facilities on San Diego Bay,
U.S. Environmental Protection Agency Report, January 1999, EPA-402-R-98-011.
PoOl Pohl, K.R., 2001, Radiological Survey of the Pearl Harbor Naval Complex, U.S.
Environmental Protection Agency Report, November 2001, EPA-402-R-01-014.
PNS97 Radiological Controls Office, Portsmouth Naval Shipyard, Historical Radiological
Assessment Naval Submarine Base New London, Volume I, Naval Nuclear Propulsion
Program 1954-1993, November 1997.
Se91 Semler, M.O and Blanchard, R.L., Radiological Surveys of Naval Facilities in the
New London Harbor and on the Thames River, Connecticut, U.S. Environmental
Protection Agency Report, December 1991, EPA 520/5-91-004.
SmOl Smith, J.M. and Lloyd, V.D., 2001, Radiological Survey of Portsmouth Naval
Shipyard, U.S. Environmental Protection Agency Report, November 2001, EPA-402-
R-01-013.
Wi73 Windham, S.T. and Phillips, C.R., 1973, "Radiological Survey of New London
Harbor, Thames River, Conn., and Environs," U.S. Environmental Protection Agency,
Radiation Data and Reports, Vol. 14, No. 11, November 1973.
44
-------
APPENDIX
Radioanalytical Results for
September 1999
NLHF Samples
45
-------
General Information for NAREL Analytical Methods
as Reported in the NAREL Data Quality Packages
Gamma Spectrometry
Gamma analysis was done on all collected samples. The activity and 2-sigma uncertainty for
radionuclides measured by gamma spectroscopy are reported only if the nuclide is detected.
Nuclides that are not detected do not appear in the report, with the exception of barium-140,
cobalt-60, cesium-137, iodine-131, potassium-40, radium-226, and radium-228. If one of these
seven nuclides is undetected, NAREL reports it as "Not Detected" or "ND".
Due to potential spectral interferences and other possible problems associated with the
determination of the activity for certain radionuclides, the activities for thorium-234,
protactinium-234m, radium-226, and uranium-235 are subject to greater possible error than other
commonly reported radionuclides. Note that this potential error is not included in the 2-sigma
counting error reported with each activity. Although in this report we do provide the calculated
activities for these radionuclides, we recommend that the results be used only as a qualitative
means of indicating the presence of these radionuclides and not as a quantitative measure of their
concentration The results for these nuclides are not used in the evaluation of quality control
samples Furthermore, because of mutual interference between radium-226 and uranmm-235,
NAREL's gamma analysis software tends to overestimate the amounts of these nuclides
whenever both are present in a sample. Lower estimates for radium-226 activities can be
obtained from the reported activities of its decay products, lead-214 and bismuth-214, which
could be somewhat less than the radium-226 activity because of the potential escape of radon
gas.
NAREL's gamma spectroscopy software corrects activities and MDCs for decay between
collection and analysis, but only up to a limit often half-lives. So, if the decay time for a sample
is more than ten half-lives of a radionuclide, that nuclide will almost for certain be undetected,
and the reported MDC will be meaningless. This is usually a problem only for short-lived
radionuclides, such as iodine-131 and barium-140, when there is a long delay between collection
and analysis.
Gross Alpha and Beta Analysis
In comparison to the methods employed to determine radionuclide-specific activities, the method
employed by NAREL to determine gross alpha and beta activity has the potential for greater
analytical bias This is especially true for soils. Note that this potential analytical error is not
included in the 2-sigma counting error term. Therefore, gross alpha and beta results should be
used as gross approximations of the alpha and beta activity present.
47
-------
TABLE A.1
Gamma Spectrometry Results for Surface Water Samples
Sample ID
NARELID -
Activity (pCi/L ±
mRa
2"Pb
luBi
mPb
2o counting
21IBi
error)
JO.J,
'"Co
»,,
40K
STUDY SAMPLES
NLHF 008-02-W
NLHF 008-W
NLHF 020-W
NLHF 035-W
NLHF 045-W
NLHF 045-W-DU
NLHF 048-W
NLHF 049-W
NLHF 055-W
NLHF 062-W
NLHF 063-W
NLHF 067-W
NLHF 075-W
NLHF093-W
NLHF 097-W
NLHF 104-02-W
NLHF 104-W
99.05484
99.05492
99.05298
99.05296
99.05301
99.05302
99.05491
99.05300
99.05299
99.05170
99.05171
99.05172
99.05479
99.05294
99.05295
99.05493
99.05483
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
5.7 ±3.0
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
7.7 ±2.7
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
5.2 ±7.8
ND
ND
ND
ND
ND
ND
ND
ND 1.2 ±1.5
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.2 ± 4.0
1.3± 1.5
ND
ND
ND
ND
ND
ND
ND
ND
ND
<2.6
<8.5
<5.2
<8.0
<2.l
<2.7
<6.3
<2.6
<5.1
<8.0
<5.2
<4.1
<2.7
<6.4
<5.7
<5.4
<2.6
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
45 ±15
210 ±60
174 ± 40
162 ±59
155 ±19
152 ±19
310±50
185 ±20
197 ±43
273 ± 62
231 ±40
255 ± 33
230 ± 21
200 ±43
159 ±45
30 ±33
268 ± 22
-------
TABLE A.1 - Continued
Ul
o
Sample ID
NLHF 128-W
NLHF 133-W
NLHF 1 33-02- W
NLHF 160-W
NLHF 168-W
NLHF I85-W
NLHF 191-W
NLHF194-W
NLHF 198-W
NLHF 203-W
NLHF213-W
NLHF 228-W
NLHF 236-W
NLHF 236-02-W
NAREL ID
99.05297
99.05481
99.05482
99.05477
99.05480
99.05478
99.05476
99.05489
99.05488
99.05487
99.05173
99.05490
99.05275
99.05274
Activity (pCi/L ± 2o counting error)
22«Ra
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
50 ±90
ND
2Upb
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2HBi
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2l2Pb
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
4.7 ±7.4
ND
ND
ND
"2Bi
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
34 ±32
2MT1
ND
ND
ND
ND
ND
ND
ND
3.3 ±3.7
ND
ND
ND
ND
ND
2.7 ±4.1
MCo
<4.9
<10.0
<8.7
<2.8
<2.9
<2.9
<2.6
<5.9
<4.2
<8.5
<6.8
<5.8
<7.2
<6.0
Ul]
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
6.1 ±3.5
«K
123 ± 36
175 ±76
ND
246 ± 20
255 ± 22
235 ±21
227 ±21
166 ±48
227 ± 34
102 ±57
166 ±48
129 ±40
ND
48 ±42
(BACKGROUND SAMPLES
NLHF 237-W-BG
NLHF 237-W-DU-BG
99.05277
99.05276
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
<4.9
<5.3
ND
ND
ND
54 ±35
Note1. "ND" indicates the radionuclide was not detected by gamma spectrometry. "< X" indicates the radionuctide was not detected and X was the minimum
detectable concentration for the nuclide in this sample. No other gamma-emitting radionuclides were detected in these samples.
-------
TABLE A.2
Tritium Results for Surface Water Samples
Sample ID
NAREL ID
Tritium Activity
(pCi/L ± 2o counting error)
STUDY SAMPLES
NLHF 008-02-W
NLHF 008-W
NLHF 020-W
NLHF 035-W
NLHF 045-W
NLHF 045-W-DU
NLHF 048-W
NLHF 049-W
NLHF 055-W
NLHF 062-W
NLHF 063-W
NLHF 067-W
NLHF 075-W
NLHF 093-W
NLHF 097-W
NLHF 1 04-02- W
NLHF 104-W
NLHF 128-W
NLHF 133-W
NLHF 133-02-W
NLHF 160-W
^^_ — — —
99.05484
99.05492
99.05298
99.05296
99.05301
99.05302
99.05491
99.05300
99.05299
99.05170
99.05171
99.05172
99.05479
99.05294
99.05295
99.05493
99.05483
99.05297
99.05481
99.05482
99.05477
1
4 ±74
-11 ±73
-3 ±78
8 ±77
-2 ±77
-24 ± 75
-10 ±73
18 ±77
49 ±79
78 ±80
-13 ±76
42 ±79
3 ±73
13 ±78
-10 ±77
75 ±77
-55 ± 71
-42 ±75
-26 ±72
26 ±74
33 ±75
51
-------
TABLE A.2 - Continued
Sample ID
NLHF 168-W
NLHF 185-W
NLHF 191-W
NLHF 194-W
NLHF 198-W
NLHF 203-W
NLHF213-W
NLHF 228-W
NLHF 236-W
NLHF 236-02-W
NARELID
99.05480
99.05478
99.05476
99.05489
99.05488
99.05487
99.05173
99.05490
99.05275
99.05274
Tritium Activity
(pCi/L ± 2o counting error)
-16 ±73
0±73
-23 ± 72
-7 ±73
-52 ± 71
-39 ± 72
7 ±77
-31 ±72
10 ±77
92 ±80
BACKGROUND SAMPLES
NLHF 237-W-BG
NLHF 237-W-DU-BG
99.05277
99.05276
51 ±79
-5 ±77
52
-------
TABLE A3
Gross Alpha and Gross Beta Activity Results for Surface Water Samples
Sample ID
NARELID
Activity
(pCi/L ± 20 counting error)
Gross Alpha
Gross Beta
STUDY SAMPLES
NLHF 008-02- W
NLHF 008-W
NLHF 020-W
NLHF 035-W
NLHF 045-W
NLHF 045-W-DU
NLHF 048-W
NLHF 049-W
NLHF 055-W
NLHF 062-W
NLHF 063-W
NLHF 067-W
NLHF 075-W
NLHF 093-W
NLHF 097-W
NLHF 1 04-02- W
NLHF 104-W
NLHF 128-W
NLHF 133-W
NLHF 133-02-W
99.05484
99.05492
99.05298
99.05296
99.05301
99.05302
99.05491
99.05300
99.05299
99.05170
99.05171
99.05172
99.05479
99.05294
99.05295
99.05493
99.05483
99.05297
48 ±69
-60 ±180
-1±56
-20 ±52
-16±37
4±33
60 ±200
-7 ±37
-19 ±35
12 ±63
31 ±77
-33 ± 49
-3 ±54
34 ±61
23 ±52
0.4 ±6.0
-26 ±37
-1±38
99.05481 -35 ±61
99.05482
— "-
-1.0±2.7
0±140
280 ±170
240 ±130
150 ±120
50 ±110
150±110
250 ±160
350 ±140
240 ±130
320 ±140
270 ± 140
320 ±130
270 ±130
150 ±120
170 ±120
21.6±7.1
370 ± 160
90 ±110
200 ± 160
18.0 ±6.5
53
-------
Table A.3 - Continued
Sample ID
NLHF 160-W
NLHF 168-W
NLHF 185-W
NLHF 191-W
NLHF 194-W
NLHF 198-W
NLHF 203-W
NLHF 21 3- W
NLHF 228-W
NLHF 236-W
NLHF 236-02-W
NARELID
99.05477
99.05480
99.05478
99.05476
99.05489
99.05488
99.05487
99.05173
99.05490
99.05275
99.05274
Activity
(pCi/L ± 2o counting error)
Gross Alpha
-27 ±41
-44 ±32
-8 ±45
20 ±62
-20 ± 140
-60 ±160
33 ±66
-5 ±51
20 ±130
0.6 ±4.9
-0.8 ±8.3
Gross Beta
280 ± 130
340 ± 140
330 ±130
160 ±120
180±150
340 ± 170
160 ±140
250 ±130
90 ±150
8±11
52 ±25
BACKGROUND SAMPLES
NLHF237-W-BG
NLHF 237-W-DU-BG
99.05277
99.05276
4±12
4 ±14
35 ±25
47 ±25
54
-------
TABLE A.4
Gamma Spectrometry Results for Drinking Water Samples
Sample ID
NARELID
Activity
(pCi/L ± 2o counting
error)
2i4pb 2i4Bi «Co
STUDY SAMPLES
NLHF 099-D
NLHF 099-D-DU
NLHF 100-D
NLHF 100-D-DU
99.05272
99.05273
99.05486
99.05485
ND
ND
ND
ND
ND
ND
ND
ND
<9.4
<27.0
<2.3
<2.7
BACKGROUND SAMPLES
NLHF 101-D-BG
99.05303
68.8 ±6.8
72.8 ±7.1
<5.3
Note: "ND" indicates the radionuclide was not detected by gamma spectrometry. "< X" indicates
the radionucJide was not detected and X was the minimum detectable concentration for the nuclide
in this sample. No other gamma-emitting radionuclides were detected in these samples.
TABLE A.5
Tritium Results for Drinking Water Samples
Sample ID
NARELID
Tritium Activity
(pCi/L ± 2o counting error)
STUDY SAMPLES
NLHF 099-D
NLHF 099-D-DU
NLHF 100-D
NLHF 100-D-DU
BACKGROUND
NLHF 101-D-BG
99.05272
99.05273
99.05486
99.05485
18 ±78
10 ±77
23 ±74
-18 ±73
SAMPLES
99.05303
-12 ±73
55
-------
TABLE A.6
Gross Alpha and Gross Beta Activity Results for Drinking Water Samples
Sample ID
NARELID
Activity
(pCi/L ± 2o counting error)
Gross Alpha
Gross Beta
STUDY SAMPLES
NLHF 099-D
NLHF 099-D-DU
NLHF 100-D
NLHF 100-D-DU
99.05272
99.05273
99.05486
99.05485
0.10±0.19
0.6 ±1.0
-0.07 ± 0.37
0.50 ±0.41
0.97 ± 0.49
2.4 ± 2.6
1.5±1.1
1.2 ±1.2
BACKGROUND SAMPLES
NLHF 101-D-BG
99.05303
0.67 ±0.63
27.8 ± 2.2
56
-------
TABLE A.7
Gamma Spectrometry Results for Harbor and Shoreline Sediment Samples
Uranium and Actinium Decay Chains
Sample ID
HARBOR SEDIMENT -
NLHF 008-S
NLHF 009-S
NLHF 017-S
NLHF 018-S
NLHF019-S
NLHF 021-S
NLHF 022-S
NLHF 023-S
NLHF 024-S
NLHF 025-S
NLHF 026-S
NLHF028-S
NLHF 029-S
NLHF 030-S
NLHF031-S
NARELID -
Activity (pCi/g-dry± 2o counting error)
JMTh
STUDY SAMPLES
99.06439
99.06390
99.06422
99.06418
99.06415
99.06421
99.06419
99.06420
99.06430
99.06453
99.06416
99.06449
99.06392
99.06429
99.06428
ND
ND
0.70 ± 0.27
0.78 ± 0.29
ND
1.36 ±0.34
0.88 ±0.25
ND
0.88 ±0.31
ND
1.00 ±0.31
0.88 ±0.42
2.02 ±0.61
ND
1.05 ±0.25
"*-Pa
ND
ND
ND
1.5± 1.5
ND
1.5 ±1.5
1.6 ±1.3
ND
ND
ND
ND
ND
ND
ND
ND
n
-------
TABLE A.7 - Continued
Sample ID
NLHF 032-S
NLHF 033-S
NLHF 034-S
NLHF 035-S
NLHF 036-S
NLHF 036-S-DU
NLHF038-S
NLHF 039-S
NLHF 040-S
NLHF 042-S
NLHF 043-S
NLHF 044-S
NLHF 046-S
NLHF 047-S
NLHF 048-S
NLHF 050-S
NLHF 051-S
NLHF 052-S
•NLHF 053-S
NAREL ID
99.06452
99.06426
99.06451
99.06427
99.06423
99.06424
99.05312
99.06450
99.05310
99.05309
99.05311
99.05315
99.05314
99.06455
99.06465
99.06456
99.06459
99.05322
99.05317
Activity (pCi/g-dry ± 2o counting error)
»4Th
1.18±0.38
0.83 ± 0.27
0.67 ± 0.33
0.77 ± 0.26
ND
0.76 ± 0.28
0.98 ±0.31
0.68 ± 0.29
0.88 ± 0.34
ND
1.47 ±0.27
1.02 ±0.33
0.71 ±0.31
0.75 ±0.38
ND
0.63 ± 0.35
ND
0.78 ± 0.28
ND
'""Pa
ND
1.5 ±1.6
ND
2.1 ±1.7
1.7 ±1.6
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.0 ±1.7
ND
ND
ND
ND
"«Ra
2.07 ±0.41
1.85 ±0.33
2. 13 ±0.43
1.95 ±0.33
1.69 ±0.33
1.69 ±0.35
2.06 ± 0.45
2.00 ±0.42
1.90 ±0.38
2.03 ±0.33
1.47 ±0.41
2.03 ± 0.45
1.87 ±0.48
1.77 ±0.50
1.90 ±0.3 8
1.78 ±0.42
2.01 ±0.52
1.50 ±0.45
1.43 ±0.39
214Pb
0.833 ± 0.036
0.778 ± 0.034
0.905 ± 0.038
0.869 ±0.036
0.794 ± 0.037
0.764 ± 0.035
0.844 ±0.036
0.768 ± 0.034
0.710 ±0.037
0.74 1 ±0.03 6
0.837 ±0.033
0.812 ±0.036
0.824 ±0.038
0.817 ±0.039
0.851 ±0.038
0.779 ± 0.037
0.807 ± 0.042
0.773 ± 0.033
0.624 ±0.033
:uBi
0.780 ±0.035
0.747 ±0.034
0.831 ±0.036
0.779 ±0.036
0.707 ± 0.036
0.704 ± 0.035
0.777 ± 0.036
0.670 ± 0.032
0.672 ±0.03 8
0.669 ±0.036
0.748 ± 0.033
0.730 ±0.033
0.716 ±0.036
0.756 ± 0.037
0.765 ± 0.038
0.676 ± 0.034
0.7 17 ±0.038
0.708 ± 0.032
O.S6&± 0.032
"5U
ND
ND
ND
ND
ND
ND
ND
ND
0.1 18 ±0.023
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
J»Ra
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
TABLE A.7 - Continued
Sample ID
NLHF 054-S
1 NLHF 056-S
1 NLHF 057-S
1 NLHF 059-S
1 NLHF 060-S
I NLHF 061-S
JNLHF061-S-DU
1 NLHF 062-S
1 NLHF 064-S
1 NLHF 065-S
JNLHFQ66-S
1 NLHF 068-S
1 NLHF 069-S
1 NLHF 070-S
INLHFOTI-S
1NLHF071-S-DU
1 NLHF 072-S
NLHF 074-S
| NLHF 076-S
NAREL ID -
99.05316
99.06460
99.05185
99.05186
99.05323
99.05183
99.05182
99.05189
99.05191
99.05188
99.06461
99.05187
99.05184
99.06448
99.06446
99.06447
99.06445
99.06457
99.06444
Activity (pCi/g-dry ± 2o counting error)
wTh
0.82 ± 0.36
ND
ND
0.70 ± 0.23
0.74 ± 0.28
0.90 ±0.35
0.91 ±0.32
0.66 ± 0.33
ND
0.50 ±0.23
1.22 ±0.33
ND
0.96 ± 0.34
ND
ND
ND
ND
0.95 ±0.3 7
1.43 ±0.33
lMmpa
ND
2.2 ±1/7
ND
ND
1.8±1.4
ND
1.9 ±1.6
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
a6Ra
1.73 ±0.47
1.49 ±0.37
1.00 ±0.31
2.03 ± 0.54
1.70 ±0.32
2.18 ±0.38
1.85 ±0.37
1.73 ±0.43
2.06 ±0.54
1.35 ±0.37
1.87 ±0.40
1.74 ±0.46
1. 99 ±0.37
!. 73 ±0.49
1.72 ±0.42
1.78 ±0.44
1.73 ±0.44
2. 18 ±0.47
2.30 ± 0.41
ZHpb
0.779 ±0,040
0,723 ± 0.037
0,573 ±0.030
0.795 ± 0.038
0.752 ± 0.034
0.777 ± 0.041
0.720 ± 0.037
0.776 ±0.035
0,723 ± 0.044
0.453 ±0.031
0.755 ± 0.040
0.793 ± 0,044
0.826 ±0.040
0.815 ±0.040
0.756 ±0.038
0.797 ± 0.040
0.804 ±0.036
0.779 ±0.039
0.670 ±0.035
J14Bi
0.682 ±0.039
0.648 ± 0.037
0.526 ± 0.029
0.707 ±0.035
0.698 ± 0.033
0.690 ±0.041
0.648 ± 0.037
0.694 ± 0.035
0.643 ± 0.042
0.446 ± 0.030
0.665 ± 0.038
0.720 ± 0.040
0.778 ± 0.038
0.673 ± 0.037
0.704 ± O.Q36
0.665 ± 0.038
0.693 ± 0.034
0.727 ± 0.037
0.610 ±0,035
wsu
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
I13Ra
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
TABLE A.7 - Continued
Sample ID
INLHF077-S
NLHF 078-S
NLHF 078-S-DU
NLHF 079-S
NLHF 080-S
NLHF081-S
NLHF 082-S
NLHF 084-S
NLHF 085-S
NLHF086-S
NLHF086-S-DU
NLHF087-S
NLHF088-S
NLHF089-S
NLHF 090-S
NLHF 091-S
NLHF 092-S
1 NLHF 094-S
\NLHF095-S
NARELID
99.06454
99.06431
99.06432
99.06458
99.06393
99.06434
99.06408
99.06437
99.06438
99.06435
99.06436
99.06433
99.06425
99.05305
99.06441
99.05307
99.06443
99.05308
Activity (pCi/g-dry ± 2o counting error)
^Th """Pa «*Ra 2»Pb "
-------
TABLE A.7 - Continued
I Sample ID
| NLHF 096-S
| NLHF 097-S
| NLHF 098-S
| NLHF 104-S
|NLHFHO-S
INLHFHI-S
INLHFIH-S
| NLHF 1
| NLHF 1
13-S
14-S
INLHFIIS-S
JNLHF116-S
INLHFIH-S
INLHF
|NLHF
|NLHF
INLHF
|NLHF
|NLHF
INLHF
117-S-DU
118-S
119-S
120-S
121-S
122-S
123-S
1
NAREL ID 1 —
Activity (pCi/g-dry ± 20 counting error)
U4Th
99.06417 0.69 ±0.24
99.05306 1.18 ±0.31
99.06409 ND
99.06463 1 ND
99.06400 0.53 ±0.29
99.05319 ND
99.06403
99.05318 1
99.06379
99.06472
99.05214
99.06411
99.06412
99.05313
99.06398
99.06402
99.06401
99.06413
99.06470
ND
ND
ND
ND
0.82 ± 0.34
ND
1.04 ±0.26
ND
ND
ND
ND
0.55 ± 0.29
0.82 ± 0.29
**»Pa
1.2 ±1.4
ND
ND
1.6 ±1.6
ND
ND
ND
1.18 ±0.66
ND
1.9 ±2.0
ND
ND
ND
ND
1.2 ±1.4
ND
ND
ND
3.1 ±2.0
226Ra
1.82 ±0.30
2.16 ±0.37
1.71 ±0.48
1.89 ±0.35
1,43 ±0.46
1.37 ±0.32
1.76 ±0.50
0.86 ±0.15
1.74 ±0.49
1.76 ±0.43
1.65 ±0.47
1.49 ±0.31
1.62 ±0.33
1.90 ±0.46
1.92 ±0,39
1.64 ±0.50
1.59 ±0.49
1.66 ±0.33
2.04 ± 0.42
214Pb
0.795 ± 0.032
0.781 ± 0.037
0.724 ± 0.042
0.740 ± 0.034
0.642 ± 0.046
0.631 ±0.028
0.7 12 ±0.047
0.347 ±0.01 5
0.680 ± 0.048
0.758 ± 0.039
0.598 ±0.043
0.620 ± 0.030
0.610 ±0.033
0.716 ±0.037
0.699 ± 0.033
0.709 ± 0.048
0.614 ± 0.040
0.713 ±0.033
0.736 ± 0.042
2UBi
0.773 ± 0.033
0.691 ± 0.039
0.642 ± 0.034
0.721 ± 0.034
0.614 ±0.037
0.558 ± 0.028
0.608 ± 0.036
0.320 ±0.01 5
0.656 ± 0.040
0.702 ± 0.041
0.555 ± 0.043
0.578 ± 0.030
0.562 ± 0.033
0.671 ±0.035
0.653 ± 0.034
0.628 ± 0.037
0.550 ±0.035
0.675 ± 0.034
0.704 ±0.041
2MU
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.1 09 ±0.026
ND
ND
ND
ND
ND
ND
ND
ND
ND
2»Ra
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
TABLE A.7 - Continued
Sample ID
NLHF 124-S
NLHF 125-S
NLHF 127-S
NLHF 128-S
NLHF 129-S
NLHF 130-S
NLHF131-S
NLHF 132-S
NLHF 133-S
NLHF 139-S
NLHF 161-S
NLHF 162-S
NLHF 163-S
NLHF 164-S
NLHF 165-S
NLHF 166-S
NLHF 167-S
NLHF 169-S
NLHF 170-S
NAREL ID
99.06468
99.06467
99.06442
99.06473
99.06391
99.06469
99.06410
99.06471
99.06464
99.06407
99.06404
99.05320
99.05321
99.06396
99.05180
99.05196
99.05200
99.06399
99.06394
Activity (pCi/g-dry ± 20
Th
ND
1.50 ±0.33
ND
ND
ND
ND
ND
ND
ND
1.35 ±0.38
ND
ND
0.47 ± 0.26
ND
ND
ND
0.77 ±0.29
1.08 ±0.26
1.00 ±0.33
"""Pa
2.1 ±1.9
ND
ND
ND
ND
ND
ND
ND
1.7± 1.9
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.6 ±1.4
2MRa
1.82 ±0.41
2.01 ±0.42
1.78 ±0.43
1.41 ±0.40
1.24 ±0.56
1.67 ±0.46
1.55 ±0.47
0.31 ±0.21
1.72 ±0.37
2.06 ± 0.39
1.68 ±0.44
1.85 ±0.51
1.24 ±0.41
1.65 ±0.54
1.79 ±0.44
1.85 ±0.44
1.56 ±0.40
0.82 ±0.10
2.26 ± 0.34
214pb
0.739 ±0.042
0.765 ± 0.038
0.816 ±0.038
0.533 ± 0.039
0.508 ± 0.044
0.756 ± 0.043
0.701 ±0.042
0.1 92 ±0.023
0.777 ± 0.037
0.954 ± 0.037
0.603 ± 0.040
0.721 ±0.039
0.508 ± 0.033
0.663 ± 0.043
0.691 ±0.041
0.544 ±0.039
0.556 ± 0.033
0.763 ± 0.030
0.753 ± 0.034
counting error)
2I4Bi
0.680 ±0.041
0.699 ± 0.040
0.660 ±0.037
0.497 ± 0.038
0.484 ±0.041
0.696 ± 0.043
0.613 ±0.037
0.161 ±0.025
0.709 ± 0.039
0.863 ± 0.035
0.588 ± 0.034
0.650 ± 0.036
0.459 ±0.031
0.626 ± 0.040
0.606 ± 0.037
0.492 ± 0.039
0.474 ± 0.032
0.668 ±0.030
0.638 ±0.033
»su
ND
ND
ND
ND
ND
0.094 ± 0.026
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
*»Ra
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
TABLE A.7 - Continued
1
Sample ID
NLHF171-S
NLHF 172-S
NLHF 173-S
NLHF 174-S
NLHF 175-S
NLHF 176-S
NLHF 177-S
NLHF 178-S
NLHF 179-S
NLHF180-S
NLHF 181-S
NLHF 182-S
NLHF 183-S
NLHF 184-S
NLHF 1S4-S-DU
NLHF 186-S
NLHF 187-S
NLHF 188-S
NLHF189-S
i
NAREL ID -
99.06397
Activity (pCi/g-dry ± 2o
" |
-------
TABLE A.7 - Continued
Sample ID
NLHF 190-S
NLHF 192-S
NLHF 193-S
NLHF 195-S
NLHF 196-S
NLHF 199-S
NLHF 200-S
NLHF201-S
NLHF202-S
NLHF204-S
NLHF205-S
NLHF206-S
NLHF 207-S
NLHF 208-S
NLHF 209-S
NLHF210-S
NLHF210-S-DU
NLHF211-S
NLHF 212-S
NARELID
99.06386
99.05177
99.05179
99.06387
99.06378
99.06371
99.06382
99.06466
99.06385
99.06375
99.05213
99.06376
99.06374
99.06395
99.06381
99.06389
99.06388
99.05219
99.05220
Activity (pCi/g-dry ± 2o counting error)
M4Th
ND
ND
0.75 ± 0.28
1.65 ±0.40
ND
1.46 ±0.37
0.66 ± 0.28
ND
ND
ND
1.03 ±0.22
ND
ND
0.88 ±0.27
ND
ND
ND
ND
ND
«4.pa
ND
ND
ND
ND
ND
ND
1.2 ±1.5
ND
ND
ND
1.1 ±1.2
ND
ND
1.0 ±1.3
ND
ND
ND
ND
ND
«'Ra
]. 83 ±0.49
1.53 ±0.43
1.98 ±0.49
1.40 ±0.45
1.75 ±0.60
1.70 ±0.40
1.70 ±0.37
1.96 ±0.3 5
1.34 ±0.3 7
1.47 ±0.50
1.96 ±0.27
1.85 ±0.40
1.62 ±0.50
2.15 ±0.33
2.02 ± 0.30
1.77 ±0.36
1.47 ±0.48
0.84 ±0.38
1.98 ±0.51
»«pb
0.710 ±0.044
0.742 ± 0.044
0.721 ±0.047
0.671 ±0.036
0.619 ±0.048
0.650 ±0.039
0.782 ± 0.032
0.778 ±0.032
0.757 ±0,033
0.519 ±0.045
0.713 ±0.028
0.720 ±0.035
0.663 ± 0.048
0.71 3 ±0.029
0.793 ± 0.028
0.771 ±0.032
0.676 ±0.043
0.480 ±0.029
0.7 15 ±0.042
JHgj
0.611 ±0.035
0.680 ± 0.039
0.623 ± 0.041
0.576 ±0.031
0.683 ± 0.044
0.567 ±0.040
0.696 ± 0.033
0.701 ± 0.032
0.676 ± 0.027
0.527 ± 0.039
0.659 ± 0.028
0.644 ± 0.027
0.61 8 ±0.040
0.671 ±0.029
0.731 ±0.028
0.699 ± 0.027
0.606 ±0.034
0.422 ± 0.025
0.6 12 ±0.039
U5U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.120 ±0.017
ND
ND
0.131 ±0.020
ND
ND
ND
ND
ND
'"Ra
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.101 ±0.059
ND
ND
ND
ND
-------
TABLE A.7 - Continued
ON
Sample ID
NLHF 213-S
NLHF215-S
NLHF216-S
NLHF217-S
NLHF219-S
NLHF 220-S
NLHF221-S
NLHF 222-S
NLHF 223-S
NLHF 224-S
NLHF 225-S
NLHF226-S
NLHF 227-S
NLHF 236-S
HARBOR SEDIMENT
NLHF 229-S-BG
NLHF 235-S-BG
NLHF 237-S-BG
NLHF 237-S-DU-BG
MAD 17 1 ¥T\
INAKLLi ID
99.05216
99.05218
99.05215
99.05208
99.05205
99.05209
99.06414
99.05207
99.05204
99.05210
99.05202
99.05206
99.05203
99.05278
Activity (pCi/g-dry ± 2o
Z34Th
1.58 ±0.37
ND
1.23 ±0.40
0.88 ± 0.42
0.52 ± 0.26
ND
0.86 ± 0.35
1.52 ±0.47
1.17 ±0.24
1.12 ±0.31
ND
0.73 ± 0.32
0.71 ±0.23
1.71 ±0.31
- BACKGROUND SAMPLES
99.05211
99.06370
99.06406
99.06405
0.69 ± 0.25
ND
0.55 ± 0.22
ND
"'-Pa
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.4 ±1.4
1.1 ±1.4
ND
1.3±1.3
ND
IMRa
1.92 ±0.49
1.48 ±0.54
1.80 ±0.56
1.74 ±0.50
1.84 ±0.46
1.87 ±0.56
1.54 ±0.37
2.05 ± 0.57
1.48 ±0.35
1.78 ±0.43
1.66 ±0.52
1.98 ±0.49
1.69 ±0.40
2.59 ± 0.38
2.30 ±0.31
1.84 ±0.31
2.05 ± 0.30
2.03 ± 0.41
iupb
0.671 ±0.039
0.722 ± 0.043
0.747 ± 0.045
0.658 ±0.041
0.824 ± 0.036
0.781 ±0.044
0.712 ± 0.041
0.758 ± 0.047
0.590 ±0.026
0.814 ±0.035
0.684 ± 0.043
0.773 ± 0.042
0.788 ± 0.032
0.745 ± 0.036
0.783 ± 0.030
0.730 ± 0.035
0.793 ±0.031
0.7 14 ±0.040
counting error)
2UBj
0.640 ± 0.039
0.724 ± 0.040
0.664 ± 0.044
0.630 ±0.039
0.763 ± 0.033
0.683 ± 0.042
0.672 ± 0.038
0.752 ± 0.046
0.549 ± 0.025
0.703 ± 0.032
0.606 ± 0.039
0.656 ± 0.038
0.706 ±0.030
0.672 ± 0.035
0.719 ±0.031
0.672 ± 0.034
0.750 ±0.032
0.659 ± 0.032
MSU
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.1 58 ±0.023
0.142 ±0.019
ND
0.120±0.017
ND
223Ra
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
TABLE A.7 - Continued
Sample ID NAKtt. m
Activity (pCi/g-dry ± 2o counting error)
iS4Th
^»Pa
3*Ra
»
-------
TABLE A.8
Gamma Spectrometry Results for Harbor and Shoreline Sediment Samples
Thorium Decay Chain and Other Gamma-Emitting Radionuclides
Sample
ID
HARBOR
NLHF008-S
NLHF009-S
NLHF017-S
NLHF018-S
NLHF019-S
NIHF021-S
NLHF022-S
NLHF023-S
NLHF024-S
NLHF025-S
NLHF026-S
NLHF028-S
NLHF029-S
NLHF030-S
NLHF031-S
NLHF032-S
NLHF033-S
NLHF034-S
NLHF035-S
NIHF036-S
NAREL
ID
Activity (pCi/g-dry ± 2o counting error)
"'Ra
a
-------
TABLE A.8 - Continued
Sample ID
NLHF036-S-DU
NLHF038-S
NLHF039-S
NLHF040-S
NLHF042-S
NLHF043-S
NLHF044-S
NLHF046-S
NLHF047-S
NLHF048-S
NLHF 050-S
NLHF 051 -S
NLHF052-S
NLHP053-S
NLHF054-S
NLHF056-S
NLHF057-S
NLHF059-S
NLHF060-S
NLHF 061 -S
NLHF 061-S-DU
NLHF062-S
NAREL
ED
99.06424
99.05312
99.06450
99.05310
99.05309
99.05311
99.05315
99.05314
99,06455
99.06465
99.06456
99.06459
99.05322
99.05317
99.05316
99.06460
99.05185
99.05186
99.05323
99.05183
99.05182
99,05189
Activity (pCi/g-dry ±
M'Ra
0.961 ±0.051
1.050 ±0.049
1.010 ±0.046
0.888 ±0.052
0,945*0.051
0.993 * 0.047
1.010 ±0.049
1.120*0.052
1.140 ±0.060
1.080 ±0.055
0,918 ±0,050
0.966 ±0.055
1.000 ±0.045
0.843 ±0,045
0,978 ± 0.054
0.881 ± 0.052
0.825 ± 0.042
0,948 ± 0.049
0.982 ±0.046
0.928 1 0.060
0,967 i 0.053
1.120*0.052
K4Ra
0.89 ± 0.44
0.71 ±0.38
0.88 ± 0.44
0.78 ±0.48
0.90 ±0.43
0.91 ±0.35
1.20 ±0.39
1 .40 ± 0.41
0.82 ± 0.47
1.14 ±0.49
1.03 ±0.41
0.98 ±0.48
0.98 ±0.39
0.84 ±0.31
1.08 ±0.45
1.10 ±0.50
0.76 ± 0.40
0.57 ±0.41
0.77 ± 0.40
0.68*0.46
1 .21 ±0.46
0.95 ±0.41
mPb
1.110 ±0.040
1.130 ±0.041
1.060±0.041
1.120 ±0.040
1.1 50 ±0.040
1.100 ±0.038
1.180 ±0.039
1. 260 i 0.043
1.180 ±0.045
1.260 ±0.042
1.140 ±0.043
1.210 ±0.049
1.080*0.039
0,998 ±0.039
1.170 ±0.044
1.150 ±0.041
0.956 ±0.042
U 50 ±0.049
1 ,020 ± 0.035
1.160*0.047
1.160*0.041
1.170 ±0.042
II2Bi
0.95 ±0.21
1.07 ±0.20
0.98 ±0.17
1,05 ±0.22
1.16 ±0.21
1.12*0.18
1.04 ±0.19
1.20 ±0.19
1.06 ±0.22
1. 10 ±0.22
1.13±0.19
1.16 ±0.21
0.95*0.17
0.99 ±0.19
1.05 ±0.21
1.08 ±0.19
1.13 ±0.16
I.I4±O.I9
1.07 ±0.18
1.27 ±0.23
0.86 ±070
1.15 ±0.19
2MTI
0.401 ±0.023
0.376 ±0.021
0.381 ±0.021
0.380 ± 0.023
0.396 ±0.022
0.374 ± 0.019
0.364 * 0.021
0.437 ± 0.022
0.423 ± 0.025
0.463 ±0.025
0.393 ± 0.024
0.424 ±0.027
0.370 ±0.01 9
0.331 ±0.020
0.396*0.023
0.433 ± 0.024
0.303 ±0.0 17
0.371*0.021
0.362 ± 0.020
0.386 ±0.025
0.375 ±0.023
0.406*0.021
2a counting error)
7Be
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.52 ± 0.32
ND
0.97 ± 0.90
ND
ND
ND
ND
ND
ND
MCo
0.082 ±0.01 2
0.061 ±0.012
0.055 ±0.011
0.044 ±0.012
0.046 ±0.011
0.037 ± 0.010
0.025*0.010
0.016 ±0.011
1.820 ±0.029
0.062 ±0.012
0.041 ±0.011
0.1 64 ±0.01 5
0.018 ±0.010
0.046 ±0.010
0.043 ±0.011
0.051 ±0.012
0.0260 *
0.0081
0.04 18 ±
0.0098
0.0430 ±
0.0099
0.076*0.013
0.048*0.012
0.058 ± 0.011
"7Cs
0.090 ±0.01 5
0.097*0.015
0.073 ±0.014
0.092*0.015
0.102*0.016
0.068 ±0.014
0.050 ±0.01 6
0.065 ±0,015
0.132*0.021
0.092 ±0.01 5
0.100 ±0.015
0.1 10 ±0.018
0.045 ±0.0 14
0.082*0.014
0.100*0.017
0.095 ±0.0 15
0.055*0.013
0.088 ±0.0 15
0.08S± 0.014
0.08&* 0.018
0.115 ±0.015
0.086*0.016
4DK
19.60 ±0.45
19.80 ±0.40
20.50 ± 0.39
19.30 ±0.46
19.80 ±0.46
19.20 ±0.38
20.60 ±0.41
20.40 ± 0,42
20.40*0.41
19.00 ± 0.46
2 1.40 ±0.42
21. 50 ±0.46
19.60 ±0.39
17.70*0.38
22.20*0.45
1 9.60 ±0.47
19.10*0.38
21.10*0.43
18. 80 ±0.42
20.60 ±0.52
20.40 ±0.48
20.50 ± 0.42
"Co
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.08 1 ±0.063
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
TABLE A.8 - Continued
VO
Sample ID
1 NLHF064-S
1 NLHF065-S
1 NLHF066-S
1 NLHF068-S
1 NLHF069-S
1 NLHF 070-S
1 NLHF071-S
1 NLHF071-S-DU
I NLHF072-S
1 NLHF074-S
1 NLHF076-S
I NLHF077-S
1 NLHF 078-S
I NLHF078-S-DU
1 NLHF079-S
I NLHF080-S
1 NLHF081-S
1 NLHF082-S
NLHF084-S
NLHF085-S
NLHF086-S
| NLHF086-S-DU
NAREL
ID
99.05191
99.05188
99.06461
99.05187
99.05184
99.06448
99.06446
99.06447
99.06445
99.06457
99.06444
99.06454
99.06431
99.06432
99.06458
99.06393
99.06434
99.06408
99.06437
99.06438
99.06435
99.06436
Activity (pCi/g-dry ± 2o
**Ra
1.010 ±0.061
0.543 ±0.042
0.950 ±0,058
0.903 ±0.056
0.915 ±0.052
.050 ± 0.053
0.995 ± 0.052
1.020 ±0.054
0.974 ± 0.048
0.997 ±0.053
0.950 ±0.050
1.020 ±0.050
1.080 ±0.049
1.090 ±0.047
0.953 ±0.045
0.892 ±0.061
1.050 ±0.053
1,090 ±0.053
1.180 ±0.048
0.888 ± 0.034
1.060 ±0.050
1.040 ±0.053
IMRa
1.1 6 ±0.49
0.99 ±0.46
1.10*0.54
0.79 ± 0.52
0.88 ± 0.48
0.94 ±0.44
0.87 ±0.41
1.09 ±0.51
0.78 ±0.41
1.13 ±0.47
0,97 ± 0,41
1.20 ±0.43
1.09 ±0.46
1.04 ±0.38
0.91 ± 0.39
ND
1.03 ±0.47
1.04 ±0.45
1.20 ±0.45
0.72 ±0.32
1.31 ±0.51
1.18 ±0.47
mPb
1,190 ±0.048
0.734 ± 0.042
1.220 ±0.042
1.200 ±0.058
1.190 ±0.051
1.220 ±0.046
1.200 ±0.045
1.200 ±0.048
1.160 ±0.044
1.130 ±0.046
0.989 ±0.042
1.150 ±0.044
1,130 ±0.043
1.250 ±0.035
1.040 ±0.038
1.280 ±0.056
1.170 ±0.046
1.230 ±0.044
1.290 ±0.045
1.000 ±0.032
1.1 10 ±0.045
1.1 50 ±0.045
MBi
0.99 ±0.24
0.69 ± 0.17
1.07 ±0.21
1.02 ±0.21
1.19 ±0.20
0.91 ±0.21
1.09 ±0.19
1.21 ±0.21
1.01 ±0.18
1.03 ±0.21
0.95 ±0.1 8
1.12 ±0.19
0.97 ±0.19
].12±0.18
0.88 ±0.1 7
1.06 ±0.23
1.12±0.19
1.11 ±0.22
1.20 ±0.19
0.87 ±0.1 3
I.I7±O.I9
I.I8±O.I9
2C,T,
0.363 ±0.026
0.241 ±0.018
0.426 ±0.026
0.390 ± 0,024
0.199 ±0.022
0.396 ±0.025
0.432 ±0.024
0.438 ±0.026
0.381 ±0.023
0.408 ±0.024
0.334 ±0.022
0.389 ±0.023
0.403 ±0.023
0.436 ±0.020
0.365 ±0.019
0.396 ±0.026
0.418 ±0.024
0.460 ±0.024
0.440 ±0.023
0.357 ±0.015
0.403 ± 0.023
0,395 ±0.024
counting error)
7Be
ND
0.30 ±0.21
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
60Co
0,068 ±0.0 14
0.0301 ±
0.0087
0.048 ±0.01 2
0.036 ±0.01 3
0.033*0.011
0.034 ±0.012
0.038 ± 0.012
0.036 ±0.0 13
0.036 ±0.0 11
0.052 ±0.012
0.031 ±0.012
0.044 ±0.012
0.034 ±0.01 1
0.0254 ±
0.0099
0.031 8 ±
0.0088
0.036 ±0.0 12
0.053 ±0.012
< 0.028
0.024 ±0.0 11
0.0214 ±
0.0067
0.032 ± 0.01 1
0.046 ±0.01 2
117Cs
0,128 ±0.019
0.077 ±0.0 13
0.109 ±0.016
0.111 ±0.017
0.103 ±0.017
0.106 ±0.018
0.090 ±0.01 6
0.098 ± 0.017
0.088 ±0.015
0.1 12 ±0.017
0.195 ±0.0 17
0.099 ±0.016
0.071 ±0.015
0.066 ±0.01 4
O.OS8± 0.013
0.105 ±0.018
0.113 ±0.016
0.017 ±0.011
0.087 ±0.0 15
0.090 ±0.0 11
0 158 ±0017
0.142 ±0.017
<°K
2 1.50 ±0,50
12.80 ±0.35
20.30 ±0.49
2 1.20 ±0.50
21. 30 ±0.45
21. 60 ±0.44
2 1.20 ±0.42
2 1.80 ±0.45
20.70 ±0.41
21. 50 ±0.44
17. 30 ±0.39
20.90 ±0.42
21.00 ±0,40
20.80 ±0.37
19.40 ±0.36
21. 10 ±0.44
21.20 ±0.43
19.90 ±0.47
18.10 ±0.37
20.10 ±0.28
20.40 ±0.41
20,90 ±0,42
"Co
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
TABLE A.8 - Continued
Sample ID
NLHF087-S
NLHF088-S
NLHF089-S
NLHF090-S
NLHF091-S
NLHF092-S
NLHF094-S
MLHF095-S
NLHF096-S
NLHF097-S
NLHF098-S
NLHF J04-S
NLHF110-S
NLHF111-S
NLHF112-S
NLHF113-S
NIHF114-S
NLHF115-S
NLHF116-S
NLHF117-S
NUff 117-S-DU
NUHF U8-S
NAREL
ID
99.06433
99.06425
99.05305
99.06441
99.05307
99,06443
99.05308
99.05304
99.06417
99.05306
99.06409
99.06463
99.06400
99.05319
99.06403
99.05318
99.06379
99.06472
99.05214
99.06411
99.06412
99.05313
Activity (pCi/g-dry ±
IMRa
1.020*0.049
0.976*0.050
0.941*0.058
1.110*0.052
1.030*0.054
1.050*0.048
1.030*0.058
0.940*0.054
1.030*0.047
1.060*0.055
0.934 * 0.055
1.070*0.050
0.955 * 0.056
0.846 * 0.040
0.962*0.060
0.394*0.019
0.783*0.057
0.938*0.057
0.933 * 0.064
0.753*0.043
0.793*0.047
0.918 ± 0.050
M4Ra
1.16*0.46
0.89*0.44
1.00*0.52
0.92*0.43
0.82*0.43
0.96*0.40
1.01*0.51
1.01*0.45
0.86 * 0.40
0.77*0.47
ND
1.29*0.45
ND
0.74*0.33
ND
0.33*0.14
ND
1.18*0.56
1.23*0.56
0.76 * 0.38
1.08*0.43
1.14±0.45
21IPb
1.150*0.044
1.100*0.038
1.200*0.048
1.200*0.046
1.130*0.042
1230*0.043
1.200*0.046
1.230*0.042
1.090*0.037
1.280*0.044
1.290*0.051
1.110*0.038
1.260*0.056
0.979*0.033
1.250*0.054
0.432*0.015
1.290*0.055
1.190*0.045
1.300*0.052
0.907*0.034
1.010*0.037
1.080*0.043
2I2Bi
1.17*0.19
1.03*0.18
1.21*0.24
1.21*0.19
1.12*0.20
1.15*0.18
1.22*0.23
1.12*0.23
1.01*0.17
1.13*0.22
1.04*0.20
1.09*0.19
0.87*0.22
0.89*0.17
0.85*0.22
0.442*0.073
0.85*0.23
1.04*0.22
1.03*0.25
0.77*0.15
0.89*0.18
1.01 *0.19
20.T,
0.391*0.021
0.420 * 0.022
0.428 ± 0.027
0.419*0.024
0.396*0.022
0.397 * 0.021
0.413*0.025
0.397*0.023
0.386 * 0.020
0.417*0.023
0.390 * 0.025
0.404*0.023
0.361 * 0.025
0.335*0.018
0.352*0.024
0.1490*0.0083
0.346*0.025
0.430 * 0.028
0.419*0.029
0.311*0.019
0.375*0.021
0.396*0.022
2o counting
7Be
ND
ND
0.39 * 0.34
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.11*0.12
ND
ND
0.76 * 0.33
ND
ND
ND
error)
60Co
0.029*0.010
0.0096
0.045 ± 0.013
0.040*0.012
0.047*0.011
0.046*0.011
0.098*0.014
0.049*0,012
0.0355 *
0.0097
< 0.029
0.028*0.010
0.041*0.011
0.035*0.011
< 0.027
0.039*0.012
< 0.013
0.039*0.012
0.038*0.012
0.070*0.014
0.0087
0.048*0.010
0.041 ±0.011
u'Cs
0.122*0.015
0.139*0.016
0.102*0.018
0.107*0.018
0.092*0.015
0.081*0.016
0.111*0.018
0.114*0.017
0.080*0.014
0.034*0.013
0.100*0.016
0.120*0.017
0.098*0.018
0.043*0.011
0.105*0.018
0.0068
0.100*0.019
0.124*0.017
0.116*0.018
0.099*0.013
0.127*0.016
0.105*0.017
40R
19.20*0.38
17.90*0.42
20.50 * 0.53
21.10*0.42
19.70 * 0.46
20.10*0.39
20.10 ±0.50
19.80x0 AS
16.40*0.39
19.60*0.47
19.50*0.38
18.30*0.43
19.10*0.42
14.10*0.31
19.80*0.41
11.80*0.19
20.00*0.43
20.00*0.50
19.30*0.54
16.40*0.39
17.10*0.42
20.50*0.42
MCo
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
TABLE A.8 - Continued
1
Sample ID
NLHFM9-S
iNLHFVKW;
1 NLHF 121-S
1 NLHF 122-S
1 NLHF 123-S
| NLHF 124-S
1 NLHF 125-S
I NLHF 127-S
1 NLHF 128-S
1 NLHF 129-S
I NLHF 130-S
1 NLHFI31-S
1 NLHF 132-S
1 NLHFI33-S
1 NLHF 139-S
1 NLHF 161-S
1 NLHF 162-S
I NLHF I63-S
NLHF164-S
NLHF 165-S
NLHFI66-S
1 NLHF 167-S
NAREL
ID
99.06398
WflMK
99.06401
99.06413
99.06470
99.06468
99.06467
99.06442
99.06473
99,06391
99.06469
99.06410
99.06471
99.06464
99.06407
99.06404
99.05320
99,05321
99.06396
Activity (pCi/g-dry ± 2o counting error)
"*Ra
0.902 ± 0.048
1 UttfcftfiB
0.892 ±0.060
1 1 ,000 ± 0.049
1 0.935 ±0.061
1 1.030 ±0.059
1 1. HO ±0.058
1 1.030 ±0.052
1 0.762 ±0.056
QAJItOMO
I 0.9*0 ±0.061
1 0.971 ±0.060
I 0.241 ±0.033
0.999 ± 0.054
1 1.040 ±0.049
0.761 ± 0.051
I 0.965 ±0.053
I 0,740 ±0.046
I 0.841 ±0.061
99.05180 1 0,927 ±0.054
99.0J196 0,862 ±0.057
99.05100 0.7 86 ±0.048
E
0.097 ±0.015
0.131 ±0.020
0.128 ±0.01*
0.134 ±0.019
0.090 ±0.0 16
«K
18.70 ±0.44
20.10 ±0.42
19.80 ±0.42
18.30 ±0.42
20.80 ±0.53
20.10 ±0.51
19.30*0.48
21. 40 ±0.43
15. 50 ±0,46
18.60*0.46
20.30*0.53
2 1.40 ±0.38
4.71 ±0.30
20. 10 ±0.48
19.20 ±0.41
19.40 ±0.36
20.60*0.44
16.40 * 0.38
20.30*0.45
19.50*0.45
18.00*0.50
17.90*0,40
"Co
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
TABLE A.8 - Continued
Sample ID
NLHF169-S
NLHF 170-S
NLHF171-S
NLHF 172-S
NLHF 173-S
NLHF 174-S
NLHF 175-S
NLHF 176-S
NLHF 177-S
NLHF 178-S
NLHF 179-S
NLHF1SO-S
NLHF 181-S
NLHF 182-S
NLHF 183-S
NLHF 184-S
NLHF 184-S-DU
NLHF 186-S
NLHF 187-S
NLHF188-S
NLHF 189-S
NAREL
ID
99.06399
99.06394
99.06397
99,05221
99.05190
99.06372
99.05217
99.05212
99.05199
99.05197
99.05194
99.05178
99.06380
99,05193
99.05195
99.05192
99.05201
99.05198
99.06373
99.06383
99.06384
Activity (pCi/g-dry ± 2o
"»Ra
1.95 ±0.76
1.040 ±0.048
0.960 ± 0.047
0.934 ±0.065
0.884 ± 0,050
0.953 ± 0.046
0.890 ± 0.056
0.999 ± 0.056
0.796 ±0,036
0.893 ± 0.062
0.890 ± 0.061
0.880 ± 0.059
0.942 ± 0,039
0.859 ±0.049
0.917 ± 0,046
0.773 ± 0.050
0.882 ± 0.056
1.020 ±0.040
0.902 ±0.052
0.956 i 0.040
0.9&6± 0.053
»'Ra
1.07 ±0.37
0.75 ±0.41
130 ±0.40
1.17 i 0.55
1.05 ±0.40
ND
1.21 ±0.50
1.32 ±0.45
0.70 ±0.25
0.96 ±0.51
1.43 ±0.58
0,70 ±0.51
1.02 ±0,33
0.72 ±0,34
1.10 ±0.41
0,70 ± 0.3S
1.12*0.44
1.01 ±0.30
ND
US ±0.37
ND
I12Pb
1.250 ±0.034
1.080 ±0.039
1.200 ±0.038
1.1 90 ±0.048
1.030 ±0.039
1.250 ±0.042
1.120 ±0.045
1.160 ±0.046
0.963 ±0.029
1.160 ±0.051
1,250 ±0.053
1.240 ±0.064
1.100 ±0.030
1.040 ±0.04 2
1. 150 i 0.038
1. 010 ±0.041
1.040 ±0.045
1.090 ±0.032
1.360 ±0.047
1.1 40 ±0.032
1.280 ±0.044
21JBi
1,3±0,7
1.08*0.19
l.lbiO.18
1.02*0.27
1.15*0.18
0.81 ± 0.16
0.88 * 0.23
1.03 ±0.20
0.91*0.14
1.1240.26
1.0840.27
1.06 ±0.25
1.08 ±0.16
0.87*0.19
1.05 ±0.18
0.92 ±0,20
0.90 ±0.22
0.93*0.14
0.95*0.18
1.03iO,15
0,89 ± 0.17
M,T,
0.424 ±0.019
0.391 ±0.022
0.413 ±0.021
0.397 ± 0.028
0.346 ±0.020
0.348 ±0.018
0.385 ± 0.024
0.373 ±0.024
0316 ±0.0] 6
0.379 ±0.027
0.386 ±0.026
0.375 ±0.025
0,409 ±0.01 7
0,302 ±0,021
0.383 ±0.020
OJ3g± 0.021
0.348 ± 0.024
0.351 ±0.017
0482 ±0.022
0.395 ±0.0 17
0.336 ±0.020
counting
'Be
ND
ND
ND
ND
ND
ND
ND
ND
0.3 3 ±0.26
ND
1. 01 ±0.39
ND
ND
ND
ND
0,62 ±0,27
0.76 ± 0.35
ND
ND
ND
ND
error)
6QCo
0.0299 ±
0.0088
0.0137 ±
0.0083
0,0394 ±
0.0099
0.045 ±0.013
0.024 ±0.0 10
< 0.026
0.023 ± 0.012
O.OJ4± 0.011
0.0163 ±
0.0079
0.041 ±0.013
0.036*0,014
0.035*0.012
0.0222 ±
0.0074
0.033 ±0.01!
0.029 ±0.0 10
0.032 ±0.010
0.039 ± 0.012
< 0.02 8
< 0.029
0.0233 ±
0.0074
< 0.028
1J7Cs
0.162 ±0.014
0.080 ±0.0 13
0.166 ±0.015
0.167 ±0.021
0.1 13 ±0.016
0.080 ±0.01 3
0.121 ±0.018
0.143 ±0.019
0.068 ±0.01 2
0.130 ±0.020
0.131 ±0.021
0.149±0.019
0,139 ±0.013
0.123 ±0,017
0.159 ±0.016
0.139 ±0.018
0.125 ±0.019
0.097 ± 0.013
0.154 ±0.015
0.1 63 ±0.013
0.146 ±0,016
40R
19.20 ±0.35
17.00 ± 0.39
19.80 ±0.39
19.10 ±OJ4
18.30 ±0.40
17.60 ±0.30
19.80 ±0.46
20.80*0.46
I8.6D±OJI
19.50 ±0.55
20.40 ±0.52
2 1.30 ±0.50
18.50 ±0.33
I8.10±0.41
20.00 ± 0.38
16.30 ±0.41
17.50 ±0.45
18.60 ±0.32
19.40 ± 0.35
18.50 ±0.33
19. 40 ±0.3 5
"Co
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
TABLE A.8 - Continued
Ul
Sample ID
1 LHF 190-S
1 NLHF 192-S
I NLHF 193-S
1 NLHF 195-S
1 NLHF 196-S
1 NLHF 199-S
1 NLHF200-S
1 NLHF201-S
1 NLHF202-S
1 NLHF204-S
1 NLHF 205-S
1 NLHF206-S
1 NLHFW7-S
1 NLHF208-S
1 NLHF209-S
1 NLHF210-S
NLHF2IO-S-DU
NLHF2H-S
NLHF212-S
NLHF213-S
NAREL
ID
Activity (pCi/g-dry ± 2o
22'Ra
99.06386 1 0.861*0.053
99.05J77 1 1.050*0.059
99.05179 0.862*0.065
99.06387 1
99.06378 j
99.06371 1
99.06382 1
99.06466 1
99.06385 1
99.06375 1
99.05213 1
99.06376
99.06374 1
99.06395 1
99.06381
99.06389 !
99.06388
99.05219
99.05220
99.05216
0.896 * 0.047
0.834*0.069
0.886*0.055
0.922*0.044
1.010*0.048
0.908*0.042
0.704*0.056
0.967*0.039
0.799*0.041
0.81 5 ±0.059
0.914*0.042
0.984*0.038
0.882*0.040
0.928 * 0.056
0.782*0.039
0.991*0.058
1.010*0.055
224Ra
ND
1.16*0.59
0.97*0.62
ND
ND
0,73 * 0,49
1.04*0.40
0.98 * 0.41
ND
ND
1.07*0.35
ND
ND
0.88 ± 0.35
1.15*0.34
ND
ND
0.76*0.35
1.31*0.50
1.02*0.44
mpb
1.370*0.052
1.090*0.053
1.160*0.064
1.400*0.042
1.410*0.065
1.150*0.046
1.220*0.035
1.180*0.037
1.400*0.036
1.190*0.055
1.070*0.030
1.220*0.039
1.270*0.054
1.120*0.033
1.130*0.031
1.430*0.038
1.230*0.046
0.843 * 0.033
1.270*0.049
1.130*0.046
>"Bi
1.06*0.20
0.94 * 0.20
1.01*0.25
0.91*0.16
0.72*0.23
1.01*0.22
1.11*0.18
1.26*0.18
1.18*0.14
0.80*0.24
1.13*0.15
0.97*0.16
1.22*0.24
1.07*0.17
1.06*0.15
0.94*0.14
0.96*0.21
0.70*0.15
1.21*0.22
1.22*0.21
2MT1
0.397*0.024
0.327 * 0.023
0.364 * 0.025
0,378*0.020
0.328*0.028
0.367*0.025
0.436 * 0.020
0.477 * 0.023
0.413*0.018
0.331*0.025
0.370*0.017
0.348*0.017
0.380*0.026
0.392*0.019
0.397*0.017
0.382 ±0,017
0.370*0.022
0.281*0.017
0.419 ±0.026
0.374 * 0.024
counting error)
7Be
ND
ND
ND
0.75 * 0.37
ND
ND
0.42*0.32
ND
0.41*0.33
1.86*0.49
ND
ND
1.02*0.45
ND
ND
ND
ND
ND
ND
ND
"Co
0,045*0.011
0.059*0.012
0.039 ±0.013
0.0482 *
0.0082
0.032*0.012
0.039*0.012
0.0373 *
0.0086
0.0357 ±
0.0095
0.0324 *
0.0080
0.058*0.013
< 0.019
< 0.026
0.036*0.013
0.0262 ±
0,0082
0.0215*
0.0075
0.0322 *
0.0071
0.035 * 0.010
< 0.027
0.026*0.013
0.036*0.012
!37Cs
0.157*0.017
0.133*0.018
0.168*0.020
0.168*0.014
0.159*0.023
0.160*0.019
0.147*0.013
0.176*0.015
0.165*0.012
0.115*0.019
0.070*0.011
0.038*0.011
0.136 ±0.021
0.149*0.013
0.138*0.012
0.162*0.012
0.162*0.018
0.037*0.012
0.185*0.020
0.155*0.019
«K
20.10*0.37
20.20 * 0.47
20.80*0.51
19.80 ±0.30
20.40 ±0.49
18.70*0.50
18.90*0.37
20.30 * 0.38
20.90*0.27
18.20*0.44
15,70*0.31
16.00*0.28
19.90*0,45
18.60*0,35
18.30 ±0.32
20.60 ±0.27
19.90*0.37
25.30 ±0.38
20.30*0.47
21.40*0.47
"Co
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
TABLE A.8 - Continued
Sample ID
NLHF 215-S
NLHF216-S
NLHF217-S
NLHF2I9-S
NLHF220-S
NLHF221-S
NLHF222-S
NLHF223-S
NLHF224-S
NLHF225-S
NLHF226-S
NLHF227-S
NLHF236-S
NAREL
ID
99.05218
99.05215
99.0520S
99.05205
99.05209
99.06414
99.05207
99.05204
99.05210
99.05202
99.05206
99.05203
99.05278
Activity (pCi/g-dry ± 2o counting error)
2MRa
0.969 ± 0.057
0.924 ±0.062
1.030 ±0.058
0.962 ±0.048
0.932 ±0.059
0.961 ± 0.057
0.982 ± 0.064
0.750 ± 0.036
1.030 ±0.046
0.978 ± 0.057
0.994 ± 0.055
0.932 ± 0.043
1.040 ±0.051
HARBOR SEDIMENT - BACKGROUND
NLHF229-S-BG
NLHF23S-S-BG
NLHF237-S-BG
NLHF 237-S-DU-
8G
SHORELINE
NLHF 135-L
NLHF 137-L
99.05211
99.06370
99.06406
99.06405
1.180 ±0.047
0.878 ± 0.047
0.904 ± 0.043
0.835 ± 0.050
™Ra
1. 56 ±0.53
1.12 ±0.53
1.25 ±0.49
1. 10 ±0.37
0.93 ±0.49
0.86 ±0.50
1.00 ±0.52
0.6S±0.26
0.86 ±0.35
1.65 ±0.56
1.02 ±0.41
1.51 ±0.35
1.01 ±0.43
SAMPLES
1.21 ±0.38
0.9S±0.41
0.87 ±0.41
ND
IlIPb
1.240 ±0.048
1.260 ±0.053
1.120*0.047
1.240 ±0.040
1. 250 ±0.048
1.120 ±0.043
1.240 ±0.054
0.859 ± 0.029
1.240 ±0.039
1.220 ±0.048
1.130 ±0.045
1.190 ±0.034
1.160 ±0.038
1. 330 ±0.034
1.090 ±0.037
0.954 ±0.033
1.140 ±0.045
»>Bi
1.33 ±0.23
1.03 ± 0.26
0.98 ±0.22
1.23 ±0.17
1.19 ±0.23
1.03 ±0.23
1.54 ±0.25
0.84 ±0.13
1.16*018
1.2 3 ±0.23
0.94 ±0.21
1.12±0.15
t. 04 ±0.20
1.17 ±0.17
1.06 ±0.19
0.80 ±0.16
0.83 ±0.1 8
M.T,
0.41 S± 0.025
0.421 ±0.027
OJ66 ± 0.024
0.4 10 ±0.021
0.402 ±0.026
0.394 ±0.026
0.434 ±0.028
0.277 ±0.015
0.406 ±0.020
0.379*0.024
0.351 ±0.023
0.396 ±0.0] 9
0.374 ±0.021
0.444 ±0.01 9
0.389 ±0.022
0.361 ±0.019
0.301 ±0.020
7Be
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.61 ± 0.29
ND
ND
'"Co
0.039 ±0.012
0.045 ±0.014
0.029 ±0.012
0.037 ±0.010
0.062 ±0.013
0.036 ±0.011
0.041 ±0.014
< 0.026
0.025 ±0.010
0.033 ±0.012
0.029 ±0.011
0.01 92 ±
0.0085
< 0.029
< 0.023
< 0.029
< 0.024
< 0.027
'"Cs
0.19* ±0.021
0.197 ±0.022
0.1 78 ±0.020
0.193 ±0.016
0.1 66 ±0.020
0.1 84 ±0.01 9
0.166*0.023
0.0462 ±
0.0097
0.207 ±0.017
O.I 86 ±0.020
0.160 ±0.019
0.184 ±0.015
0.068 ±0.014
0.040 ±0.011
0.200 ±0.016
0.149 ±0.014
0.127 ±0.015
«K
20.50 ±0.47
21 .20 ±0.51
20.30 ±0.46
20.30 ±0.38
20.40 ±0.48
18.50 ±0.48
20.80 ±0.52
16.40 ±0.29
19.90 ±0.37
19.40 ±0.47
18.90 ±0.44
18.20 ±0.33
16, 70 ±0.42
18.80 ±0,35
14.90 ±0.40
13.90 ±0.35
14.50 ±0.32
"Co
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
SEDIMENT - STUDY SAMPLES
99.05223
99.05222
0.265 ±0.018
0.423 ±0.026
0.20 ±0.15
0.41 ±0.19
0.272 ±0.014
0.439*0.019
0.256 ±0.069
0.459 ±0.094
0.0911 ±0.0077
0.148 ±0.011
0.13±0.ll
ND
< 0.014
< 0.01 8
0.0093 ±
0.0058
ND
14.30 ± 0.22
12.80 ±0.25
ND
ND
-------
TABLE A.8 - Continued
Sample ID
NLHF 146-L
NLHF241-L
NLHF 241 -L-DU
NLHF244-L
NLHF 245-L
SHORELINE
NLHF234-L-BG
NAREL
ID
99,06440
99.05176
99.05175
99.06377
99.06462
Activity (pCi/g-dry ± 2o counting error)
B'Ra
0.419 ±0.028
0.278*0.026
0.291*0.027
0.929*0.043
0.636 ±0.041
U4Ra
OJ9±0.2S
ND
ND
ND
0.60 ±0.28
Mlpb 21JBj W»T, 7ge SOCo
0.476 ±0.020 0.54 =t 0.11 0.164 ±0.012 ND <0020
0.280 ±0.027 0.23 ±0.10 0.087 ±0.010 0.24 ±0.12 < 0.018
0.295 ±0.027 0.29 ±0.11 0.094 ±0.010 ND < 0.020
1.100 ±0.040 0,78 ±0.14 0,322 ±0.017 ND < 0.023
0.578 ±0.024 0.55 ±0.15 0.217 ±0.017 ND < 0.029
u1Cs 4DK
ND 19.60 ± 0.32
°S£i* "-30*0-29
"Sit* ™*™
0.095 ±0.013 12.60 ±0.26
0.016 ±0.0 11 17.70 ±0.44
"Co
ND
ND
ND
ND
ND
SEDIMENT - BACKGROUND SAMPLES
99.05174
0.721 ±0.036
0.58 ± 0.36
0.800±0.037 0.74±0.14 0.246±0.015 0.22±0.15 <0.023
ND 18.00 ±0.31
ND
Note: "ND" indicates the radionuclide was not detected by gamma spectrometry. "< X" indicates the radionuclide was not detected and X was
the minimum detectable concentration for the nuclide in this sample. No other gamma-emitting radionuclides were detected in these samples.
-------
TABLE A.9
Gross Alpha and Gross Beta Activity Results for
Harbor and Shoreline Sediment Samples
Sample ID
HARBOR SEDIMENT
NLHF 008-S
NLHF 009-S
NLHF 017-S
NLHF 018-S
NLHF 019-S
NLHF021-S
NLHF 022-S
NLHF 023-S
NLHF 024-S
NLHF 025-S
NLHF 026-S
NLHF 028-S
NLHF 029-S
NLHF 030-S
NLHF031-S
NLHF 032-S
NLHF 033-S
NLHF034-S
NLHF035-S
NARELID
(pCi/g-dry
Activity
± 2o counting error)
Gross Alpha Gross Beta
- STUDY SAMPLES
99.06439
99.06390
99.06422
99.06418
99.06415
99.06421
99.06419
99.06420
99.06430
99.06453
99.06416
99.06449
99.06392
99.06429
99.06428
99.06452
99.06426
99.06451
99.06427
5.8 ±3.2
9.4 ±3. 9
6.9 ±3.5
11.0±4.1
10.4 ±4.0
14.3 ±4.8
11.4 ±4.2
13.4 ±4.6
10.4 ±4.2
6.6 ±3.3
13.7 ±4.9
13.0 ±4.6
15.1 ±4.8
9.5 ± 4.2
12.2 ±4.5
12.8 ±4.4
10.4 ±4.2
9.1 ±3.9
8.8 ±3.8
29.3 ± 4.3
24.3 ± 4.2
29.2 ± 4.3
30.4 ± 4,4
27.0 ± 4.2
27.2 ± 4.3
26.3 ± 4.2
30.0 ± 4.4
27.9 ± 4.9
29.7 ± 4.3
25.9 ± 4.4
28.5 ± 4.3
25.6 ±4.1
25.4 ± 4.8
25.8 ± 4.8
29.7 ±4.3
24.4 ± 4.7
26.3 ± 4.2
30.4 ± 4.8
76
-------
TABLE A.9 - Continued
Sample ID
NLHF 036-S
NLHF 036-S-DU
NLHF 038-S
NLHF 039-S
NLHF 040-S
NLHF 042-S
NLHF 043-S
NLHF 044-S
NLHF 046-S
NLHF 047-S
NLHF 048-S
NLHF 050-S
NLHF051-S
NLHF 052-S
NLHF 053-S
NLHF 054-S
NLHF 056-S
NLHF 057-S
NLHF 059-S
NLHF 060-S
NLHF061-S
NLHF 061 -S-DU
NLHF 062-S
NLHF 064-S
NARELID
99.06423
99.06424
99.05312
99.06450
99.05310
99.05309
99.05311
99.05315
99.05314
99.06455
99.06465
99.06456
99.06459
99.05322
99.05317
99.05316
99.06460
99.05185
99.05186
99.05323
99.05183
99.05182
99.05189
99.05191
Activity
(pCi/g-dry ± 20 counting error)
Gross Alpha
11.1 ±4.2
9.4 ± 4.0
12.8 ±4.6
3.5 ±2.7
8.9 ± 4.0
12.2 ±5.1
10.0 ±4.2
8.9 ±3.7
8.1 ±3.8
11.2±4.1
11.1 ±4.0
8.0 ± 3.7
13.0 ±4.6
10.3 ±4.1
5.7 ±3.4
8.1 ±4.0
9.5 ± 3.9
11.8 ±4.5
9.3 ± 3.9
7.1 ±3.6
11.8 ±4.3
13.5 ±4.6
7.7 ±3.7
10.7 ±4.3
Gross Beta
35.1 ±4.6
28.6 ±4.3
29.6 ± 4.9
23.5 ±3.9
32.0 ±4.9
30.1 ±5.0
29.6 ± 4.8
30.6 ±4.4
26.7 ±4.3
28.9 ±4.3
25.3 ±4.1
24.1 ±4.1
31.5 ±4.5
25.5 ±4.2
25.2 ±4.1
32.5 ± 4.6
24.5 ±4.1
28.0 ±4.4
28.1 ±4.3
32.4 ± 4.6
31.1 ±4.4
31.1 ±4.5
26.8 ± 4.2
31.0 ±4.6
77
-------
TABLE A.9 - Continued
Sample ID
NLHF 065-S
NLHF 066-S
NLHF 068-S
NLHF 069-S
NLHF 070-S
NLHF 071 -S
NLHF 071 -S-DU
NLHF 072-S
NLHF 074-S
NLHF 076-S
NLHF 077-S
NLHF 078-S
NLHF 078-S-DU
NLHF 079-S
NLHF 080-S
NLHF081-S
NLHF 082-S
NLHF 084-S
NLHF 085-S
NLHF 086-S
NLHF 086-S-DU
NLHF 087-S
NLHF 088-S
NLHF 089-S
NAREL ID
99.05188
99.06461
99.05187
99.05184
99.06448
99.06446
99.06447
99.06445
99.06457
99.06444
99.06454
99.06431
99.06432
99.06458
99.06393
99.06434
99.06408
99.06437
99.06438
99.06435
99.06436
99.06433
99.06425
99.05305
Activity
(pCi/g-dry ± 20 counting error)
Gross Alpha
7.7 ±3.4
11.1 ±4.1
13.6 ±4.6
10.0 ±4.0
12.7 ±4.6
9.6 ±4.0
13.4 ±4.6
11.8 ±4.3
9.6 ± 4.0
10.9 ±4.0
9.0 ±3.7
14.5 ±4.8
12.5 ±4.5
6.4 ±3.3
11.8 ±4.2
8.8 ±3.7
4,8 ±3.5
7.6 ±3.6
10.3 ±4.2
10.7 ±4.2
9.0 ±4.0
10.2 ±4.2
11.4 ±4.2
11.7 ±4.6
Gross Beta
17.4 ±3.7
27.8 ±4.2
28.2 ± 4.2
32.7 ±4.5
26.9 ±4.3
25.2 ± 4.2
31.4 ±4.4
33. 7 ±4.6
28.5 ±4.3
24.9 ± 4.0
32.1 ±4.4
23.2 ± 4.6
23.5 ±4.7
23 .9 ±4.0
29.9 ±4.4
29.4 ±4.3
28.5 ± 4.4
25.7 ±4.1
26.7 ± 4.3
27.5 ± 4.3
29.0 ±4.4
18.0±3.7
24.1 ±4.0
30.1 ±4.5
78
-------
TABLE A.9 - Continued
Sample ID
NLHF 090-S
NLHF091-S
NLHF 092-S
NLHF094-S
NLHF 095-S
NLHF 096-S
NLHF 097-S
NLHF 098-S
NLHF 104-S
NLHF110-S
NLHF111-S
NLHF112-S
NLHF113-S
NLHF114-S
NLHF115-S
NLHF116-S
NLHF117-S
NLHF117-S-DU
NLHF118-S
NLHF119-S
NLHF 120-S
NLHF 121 -S
NLHF 122-S
NLHF 123-S
NARELID
99.06441
99.05307
99.06443
99.05308
99.05304
99.06417
99.05306
99.06409
99.06463
99.06400
99.05319
99.06403
99.05318
99.06379
99.06472
99.05214
99.06411
99.06412
99.05313
99.06398
99.06402
99.06401
99.06413
99.06470
Activity
(pCi/g-dry ± 2o counting error)
Gross Alpha
14.6 ±4.7
7.5 ± 3.7
11.3 ±4.2
8.4 ±4.2
6.6 ±3.7
11.6 ±4.2
9.1 ±4.0
15.1 ±4.9
9.5 ± 3.9
12.5 ±4.4
8.7 ±3. 9
11.5 ±4.3
2.4 ± 2.4
13.3 ±4.5
5.0 ±3.2
11.8 ±4.2
10.9 ±4.3
11.2 ±4.3
9.3 ± 4.2
14.9 ±4.9
11.5 ±4.4
9.8 ±3. 9
12.7 ±4.4
12.6 ±4.6
Gross Beta
28.1 ±4.4
22.3 ± 4.6
22.4 ±4.1
32.7 ±4.8
26.3 ± 4.3
21.5 ±4.0
28.8 ±4.3
28.2 ± 4.4
24.1 ±4.1
31.0±4.5
16.3 ±3.7
31.2±4.5
14.9 ±3.4
28.7 ±4.3
29.2 ± 4.3
28.3 ± 4.3
23.5 ±4.2
27.0 ±4.2
32.6 ±4.8
32.4 ±4.5
30.5 ± 4.6
26.1 ±4.2
24.8 ± 4.2
32.4 ± 4.5
79
-------
TABLE A.9 - Continued
Sample ID
NLHF 124-S
NLHF 125-S
NLHF 127-S
NLHF 128-S
NLHF 129-S
NLHF 130-S
NLHF 131-S
NLHF 132-S
NLHF 133-S
NLHF 139-S
NLHF 161-S
NLHF 162-S
NLHF 163-S
NLHF 164-S
NLHF 165-S
NLHF 166-S
NLHF 167-S
NLHF 169-S
NLHF 170-S
NLHF 171-S
NLHF 172-S
NLHF 173-S
NLHF 174-S
NLHF 175-S
NAREL ID
99,06468
99.06467
99.06442
99.06473
99.06391
99.06469
99.06410
99.06471
99.06464
99.06407
99.06404
99.05320
99.05321
99.06396
99.05180
99.05196
99.05200
99.06399
99.06394
99.06397
99.05221
99.05190
99.06372
99.05217
Activity
(pCi/g-dry ± 2o counting error)
Gross Alpha
8.5 ± 3.7
6.8 ±3.5
11.0 ±4.4
12.1 ±4.4
9.7 ±3.9
8.6 ±4.0
11.6±4.4
7.3 ±3. 7
12.1 ±4.3
9.2 ± 3.8
13.9 ± 4.6
12.2 ±4.4
7.5 ± 3.7
9.1 ±4.1
10.9 ±4.2
6.5 ± 3.4
8.4 ±3.8
19.9 ±5.5
7.4 ± 3.7
9.3 ±4.0
11.2 ±4.5
8.8 ±3.7
10.1 ±4.2
10.7 ±4.8
Gross Beta
25.5 ±4.1
22.1 ±4.0
28.9 ± 4.5
22.4 ± 3.9
23.6 ± 4.1
26.6 ± 4.2
29.8 ± 4.4
8.9 ±3.1
24.7 ± 4.0
25.1 ±4.1
3 1.6 ±4.4
29.1 ±4.3
20.0 ±3. 9
27.4 ± 4.3
28.8 ±4.3
27.9 ± 4.2
21.0 ±3.9
39.2 ± 5.0
24.3 ± 4.2
27.5 ± 4.3
24.1 ±4.2
24.5 ± 4.0
26.0 ± 4.3
32. 1 ±4.9
80
-------
TABLE A.9 - Continued
Sample ID
NLHF 176-S
NLHF 177-S
NLHF 178-S
NLHF 179-S
NLHF 180-S
NLHF 181-S
NLHF 182-S
NLHF 183-S
NLHF 184-S
NLHF 184-S-DU
NLHF 186-S
NLHF 187-S
NLHF 188-S
NLHF 189-S
NLHF 190-S
NLHF 192-S
NLHF 193-S
NLHF 195-S
NLHF 196-S
NLHF 199-S
NLHF 200-S
NLHF201-S
NLHF 202-S
NLHF 204-S
NARELID
99.05212
99.05199
99.05197
99.05194
99.05178
99.06380
99.05193
99.05195
99.05192
99.05201
99.05198
99.06373
99.06383
99.06384
99.06386
99.05177
99.05179
99.06387
99.06378
99.06371
99.06382
99.06466
99.06385
99.06375
Activity
(pCi/g-dry ± 2o counting error)
Gross Alpha
7.7 ±3.7
8.9 ±3.9
7.8 ± 3.9
11.9 ±4.4
13.4 ±4.7
12.2 ± 4.2
10.2 ±4.1
7.4 ±3. 6
11.1 ±4.4
6.5 ± 3.6
12.4 ±4.5
10.8 ±4.1
8.7 ±3.6
9.5 ± 3.8
7.9 ±4.3
9.8 ±4.1
10.2 ±4.1
14.7 ±4.7
16.0 ±4.9
9.7 ±4.0
5.7 ± 3.9
10.3 ±4.1
8.7 ±4.0
6.3 ±3.3
Gross Beta
26.6 ±4.2
23.9 ±4.0
29.1 ±4.4
21.3 ±3.9
28.5 ± 4.4
27.5 ± 4.7
23 .2 ±4.0
24.8 ±4.1
30.9 ± 4.5
22.7 ±4.1
23.0 ±4.0
27.5 ± 4.2
27.9 ±4.7
29.5 ± 4.6
28.9 ± 4.8
23.8 ±4.1
28.8 ± 4.4
30.4 ±4.5
22.9 ±4.1
27.5 ±4.3
29.2 ± 4.8
24.3 ±4.2
25.8 ± 4.5
21.9 ±3.9
81
-------
TABLE A.9 - Continued
Sample ID
NLHF 205-S
NLHF 206-S
NLHF 207-S
NLHF 208-S
NLHF 209-S
NLHF210-S
NLHF210-S-DU
NLHF211-S
NLHF212-S
NLHF213-S
NLHF215-S
NLHF216-S
NLHF217-S
NLHF219-S
NLHF 220-S
NLHF221-S
NLHF 222-S
NLHF 223-S
NLHF 224-S
NLHF 225-S
NLHF 226-S
NLHF 227-S
NLHF 236-S
NARELID
99.05213
99.06376
99.06374
99.06395
99.06381
99.06389
99.06388
99.05219
99.05220
99.05216
99.05218
99.05215
99.05208
99.05205
99.05209
99.06414
99.05207
99.05204
99.05210
99.05202
99.05206
99.05203
99.05278
Activity
(pCi/g-dry ± 2o counting error)
Gross Alpha
8.2 ±3.8
8.2 ±3.6
9.8 ± 4.0
7.5 ±3.5
8.3 ±3.9
14.2 ± 4.6
9.9 ±3.9
7.5 ± 3.7
12.9 ±4.9
4.6 ± 4.2
11.0±4.8
10.7 ±4.5
9.7 ±4.1
11.7 ±4.4
8.8 ±3.9
12.4 ± 4.4
11.7 ±4.2
6.9 ±3.5
7.9 ±3.8
8.5 ±3.8
12.3 ±4.6
5.4 ±3.4
12.0 ±4.6
Gross Beta
22.0 ±4.0
21.2 ±3.9
32.8 ±4.6
29.0 ±4.3
25.6 ±4.4
29.9 ± 4.4
24.5 ± 4.0
31.5 ±5.1
28.5 ±4.9
26.4 ±4.6
25.7 ±4.8
27.7 ± 4.8
21.6±4.0
27.0 ± 4.3
26.2 ±4.2
28.8 ±4.3
31.5 ±4.4
19.7 ±3.8
24.3 ± 4.2
22.6 ±4.0
26.5 ± 4.4
26.0 ±4.3
21.1 ±4.0
82
-------
TABLE A.9 - Continued
Sample ID
NARELID
Activity
(pCi/g-dry ± 20 counting error)
Gross Alpha
Gross Beta
HARBOR SEDIMENT - BACKGROUND SAMPLES
NLHF 229-S-BG
NLHF 235-S-BG
NLHF 237-S-BG
NLHF 237-S-DU-BG
SHORELINE SEDIMENT
NLHF 135-L
NLHF 137-L
NLHF 146-L
NLHF 241 -L
NLHF 241-L-DU
NLHF 244-L
NLHF 245-L
SHORELINE SEDIMENT
NLHF 234-L-BG
99.05211
99.06370
99.06406
99.06405
7.6 ±3.7
8.6 ±3.9
9.2 ±4.0
8.4 ±3.6
- STUDY SAMPLES
99.05223
99.05222
99.06440
99.05176
99.05175
99.06377
99.06462
-0.6 ±2.3
0.1 ±2.1
1.6 ±2.0
-0.4 ± 2.0
0.2 ±1.6
8.5 ±3.8
5.5 ±3.1
- BACKGROUND SAMPLES
99.05174
7.1 ±3.6
29.1 ±4.4
24.9 ±4.1
24.3 ±4.1
24.1 ±4.1
15.9 ±3.7
15.8 ±3.6
19.7 ±3.8
16.2 ±3.7
12.7 ±3.3
18.9 ±3.9
26.9 ±4.3
20.6 ± 3.9
83
-------
TABLE A.10
Gamma Spectrometry Results for Sediment Core Samples
Uranium and Actinium Decay Chains
Sample ID
Core Slice
(cm)
NAREL ID
Activity (pCi/g-dry ± 20 counting error)
*«Th """Pa »'Ra "«Pb 2MBi USU
STUDY SAMPLES
NLHF 025-C
NLHF 025-C
NLHF 025-C
NLHF 025-C
NLHF 025-C
NLHF 028-C
NLHF 028-C
NLHF 028-C
NLHF 028-C
NLHF 028-C
NLHF 032-C
NLHF 032-C
NLHF 032-C
NLHF 032-C
NLHF 032-C
00-05
05-10
10-15
15-34
34-53
00-05
05-10
10-15
15-31
31-48
00-05
05-10
10-15
15-34
34-53
99.07514
99.07515
99.07516
99.07517
99.07518
99.07479
99.07480
99.07481
99.07482
99.07483
99.07499
99.07500
99.07501
99.07502
99.07503
0.64 ± 0.46
ND
ND
1.13 ±0.29
ND
ND
ND
ND
0.93 ± 0.37
1.02 ±0.26
ND
ND
ND
1.79 ±0.34
0.40 ±0.22
ND
ND
ND
3.5 ±2.4
ND
ND
ND
ND
1.7 ±2.0
ND
4.4 ±4.9
ND
ND
ND
ND
1.97 ± 0.80
1.32 ±0.76
2.10 ±0.82
2.26 ± 0.38
2.33 ±0.76
1.6 ±1.0
1.35 ±0.69
2.41 ±0.70
1.69 ±0.40
2.13 ±0.38
1.40 ±0.74
2.08 ± 0.69
1. 52 ±0.77
2.32 ±0.42
1.82 ±0.28
0.826 ± 0.075
0.768 ± 0.083
0.672 ± 0.080
0.916 ±0.039
0.898 ± 0.069
0.624 ± 0.090
0,634 ± 0.063
0.757 ± 0.074
0.763 ± 0.040
0.878 ± 0.037
0.743 ± 0.074
0.740 ± 0.064
0.747 ± 0.085
0.991 ±0.045
0.788 ± 0.028
0.719 ±0.088
0.687 ± 0.092
0.664 ± 0.087
0.904 ± 0.044
0.767 ± 0.092
0.55 ±0.10
0.560 ± 0.072
0.702 ±0.081
0.716 ±0.043
0.824 ± 0.042
0.656 ±0.081
0.721 ±0.076
0.669 ± 0.095
0.939 ± 0.050
0.703 ±0.031
ND
ND
0.134 ±0.050
0.1 37 ±0.023
ND
0.108 ±0.059
ND
ND
ND
ND
ND
0.1 30 ±0.040
ND
ND
0.112± 0.017
-------
TABLE A.10 - Continued
oo
Sample ID
NLHF 034-C
NLHF 034-C
NLHF 034-C
NLHF 034-C
NLHF 034-C
NLHF 039-C
1 NLHF 039-C
NLHF 039-C
NLHF 039-C
NLHF 039-C
1 NLHF 047-C
NLHF 047-C
NLHF 047-C
NLHF 047-C
NLHF 047-C
NLHF 048-C
NLHF 048-C
NLHF 048-C
Core Slice
(cm)
00-05
05-10
10-15
15-33
33-52
00-05
05-10
10-15
15-28
28-42
00-05
05-10
10-15
15-24
24-33
00-05
05-10
10-15
NAREL ID •
99.07509
99.07510
99.07511
99.07512
99.07513
99.07524
99.07525
99.07526
99.07527
99.07528
99.07494
99.07495
99.07496
99.07497
99.07498
99.07489
99.07490
99.07491
Activity (pCi/g-dry ± 2o counting
^Th
1.19 ±0.56
0.80 ±0.43
ND
0.66 ± 0.24
1.04 ±0.19
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
«4-pa
ND
ND
ND
ND
ND
ND
ND
ND
1.7 ±1.4
ND
ND
ND
ND
ND
ND
ND
ND
ND
2MRa
2.11 ±0.79
1.94 ±0.66
1.43 ±0.60
1.73 ±0.33
1.64 ±0.28
0.89 ± 0.73
1.78 ±0.53
1.63 ±0,71
1.16±0.3i
1.67 ±0.33
ND
1.7 ±1.0
1.53 ±0.82
1.38 ±0.59
1.59 ±0.51
1.66 ±0.84
1.40 ±0.85
1.45 ±0.57
»4Pb
0.724 ± 0.079
0.825 ± 0.064
0.758 ± 0.069
0.770 ± 0.035
0.757 ± 0.027
0.550 ± 0.074
0.658 ± 0.049
0.547 ± 0.065
0.471 ± 0.030
0.799 ±0.031
0.640 ± 0.085
0.631 ±0.090
0.542 ± 0.075
0.690 ± 0.064
0.712 ±0.055
0.714 ± 0.072
0.621 ±0.073
0.784 ± 0.052
error)
JUBi
0.621 ± 0.089
0.726 ± 0.076
0.695 ± 0.074
0.706 ± 0.037
0.704 ± 0.030
0.568 ± 0.077
0.593 ± 0.048
0.500 ± 0.067
0.396 ±0.030
0.71 8 ±0.03 5
0.583 ± 0.092
0.5 12 ±0.090
0.509 ±0.091
0.641 ± 0.089
0.621 ± 0.058
0.689 ±0,076
0.570 ± 0.072
0.687 ± 0.062
1KV
ND
ND
ND
ND
0.100 ±0.017
ND
ND
ND
ND
ND
0.089 ± 0.056
0.1 17 ±0.058
ND
0.089 ± 0.035
ND
0.101 ±0.050
ND
0.090 ± 0.034
-------
TABLE A.10 - Continued
Sample ID
NLHF 048-C
NLHF 048-C
NLHF 050-C
NLHF 050-C
NLHF 050-C
NLHF 050-C
NLHF 050-C
NLHF051-C
NLHF051-C
NLHF051-C
NLHF051-C
NLHF051-C
NLHF 056-C
NLHF 056-C
NLHF 056-C
NLHF 056-C
NLHF 056-C
NLHF 062-C
Core Slice
(cm)
15-34
34-53
00-05
05-10
10-15
15-33
33-52
00-05
05-10
10-15
15-33
33-52
00-05
05-10
10-15
15-31
31-48
00-05
NAREL ID
99.07492
99.07493
99.07469
99.07470
99.07471
99.07472
99.07473
99.07504
99.07505
99.07506
99.07507
99.07508
99.07519
99.07520
99-07521
99.07522
99.07523
99.05262
Activity (pCi/g-dry ± 2o counting
error)
«4Th IM-p,, Z«Ra 2Up|) ,MBi »SU
ND
1.03 ±0.25
ND
ND
ND
0.95 ± 0.26
0.61 ±0.22
ND
ND
ND
ND
ND
ND
ND
ND
1.67 ±0.44
ND
ND
1.6 ±1.9
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
3.9 ±4.4
ND
ND
ND
1.8 ±2.3
2.34 ± 0.44
2. 10 ±0.37
1.2 ±1.1
1.29 ±0.83
1.29 ±0.78
1.93*0.35
1,87 ±0.29
1.1 ±1.1
J. 86 ±0.94
1.48 ±0.83
1.36 ±0.38
1.67 ±0.35
1.17±0.97
J. 26 ±0.89
2. 19 ±0.78
1. 78 ±0.49
1.31 ±0.78
1.97 ±0.43
0.834 ±0.042
0.875 ±0.03 7
0.61 ±0.10
0.660 ± 0.079
0.633 ± 0.073
0.763 ± 0.035
0.741 ± 0.028
0.635 ± 0.093
0.609 ±0.084
0.665 ± 0.084
0.701 ± 0.038
0.671 ± 0.033
0.523 ± 0.084
0.637 ± 0.085
0.634 ± 0.063
0.666 ± 0.049
0.687 ± 0.065
0.819 ±0.048
0.732 ± 0.047
0.772 ±0.039
0.60 ±0.11
0.551 ±0.090
0.647 ± 0.084
0.664 ± 0.038
0.689 ±0.033
0.607 ± 0.094
0.530 ±0.086
0.649 ± 0.090
0.624 ±0.041
0.583 ± 0.036
0.485 ± 0.094
0.576 ± 0.095
0.581 ± 0.083
0.626 ±0.061
0.652 ± 0.086
0.744 ± 0.052
ND
0.1 27 ±0.022
ND
ND
ND
ND
0.115±0.018
0.075 ± 0.065
ND
ND
0.086 ± 0.023
ND
0.082 ±0.058
ND
ND
ND
ND
ND
oo
-------
TABLE A.10 - Continued
00
Sample ID
NLHF 062-C
NLHF062-C
NLHF 062-C
NLHF 062-C
NLHF 064-C
NLHF 064-C
NLHF 064-C
NLHF 064-C
NLHF 064-C
NLHF 066-C
NLHF 066-C
NLHF 066-C
NLHF 066-C
NLHF 066-C
NLHF 074-C
NLHF074-C
NLHF 074-C
NLHF 074-C
Core Slice
(cm)
05-10
10-15
15-30
30-50
00-05
05-10
10-15
15-25
25-35
00-05
05-10
10-15
15-27
27-39
00-05
05-10
10-15
15-34
NARELID
99.05263
99.05264
99.05265
99,05266
99.05267
99.05268
99.05269
99.05270
99.05271
99.07484
99.07485
99.07486
99.07487
99.07488
99.07529
99.07530
99.07531
99.07532
Activity (pCi/g-dry ± 2o counting
23*rh
L53 ± 0.30
ND
1.35 ±0.36
0.55 ± 0.23
1.07 ±0.73
ND
ND
ND
ND
ND
ND
ND
0.53 ± 0.32
ND
ND
ND
ND
ND
*"-Pa
ND
ND
3.6 ±1.9
ND
ND
ND
ND
ND
4.6 ±5.0
ND
ND
ND
ND
ND
ND
ND
ND
ND
"6Ra
2. 14 ±0.42
1.53 ±0.76
2.31 ±0.40
1.67 ±0.31
2.4 ±1.0
1.58 ±0.74
ND
2. 12 ±0.65
1.51 ±0.92
1.7±1.1
2.02 ± 0.95
1.74 ±0.81
1.58 ±0.47
2.93 ± 0.89
1.1 ±1.2
1.35 ±0.99
1.36 ±0.96
1.67 ±0.52
JI4Pb
0.721 ±0.042
0.673 ± 0.072
0.950 ± 0.044
0.602 ±0.031
0.542 ± 0.097
0.661 ±0.084
0.794 ± 0.054
0.767 ± 0.065
0.670 ± 0.092
0.582 ±0.091
0.584 ± 0.076
0.61 3 ±0.069
0.695 ± 0.044
0.7 10 ±0.076
0.63 ±0.10
0.674 ± 0.092
0.593 ± 0.088
0.689 ±0.051
error)
"4Bi
0.663 ± 0.050
0.5 75 ±0.081
0.829 ± 0.047
0.579 ± 0.033
0.510 ±0.099
0.543 ±0.091
0.662 ± 0.063
0.623 ± 0.074
0.613 ± 0.093
0.538 ± 0.097
0.598 ±0.080
0.56! ±0.072
0.596 ± 0.049
0.731 ±0.078
0.58 ±0.11
0.647 ± 0.095
0.582 ±0.091
0.642 ± 0.059
"SU
0.129 ±0.025
ND
ND
ND
ND
ND
0.125 ±0.035
ND
ND
0.1 04 ±0.065
0.131 ±0.054
0.1 12 ±0.048
ND
ND
ND
ND
ND
0.104 ±0.031
-------
TABLE A.10 - Continued
Sample ID
NLHF 074-C
NLHF 079-C
NLHF 079-C
NLHF 079-C
NLHF 079-C
NLHF 079-C
NLHF 082-C
NLHF 082-C
NLHF 082-C
NLHF 082-C
NLHF 082-C
NLHF 1 16-C
NLHF 1 16-C
NLHF 1 16-C
NLHF 1 16-C
NLHF 1 16-C
NLHF117-C
NLHF 1 17-C
Core Slice
(cm)
34-53
00-05
05-10
10-15
15-33
33-51
00-05
05-10
10-15
15-33
33-51
00-05
05-10
10-15
15-30
30-53
00-05
05-10
NAREL ID
99.07533
99.07474
99.07475
99.07476
99.07477
99.07478
99.05350
99.05351
99.05352
99.05353
99.05354
99.05242
99.05243
99.05244
99.05245
99.05246
99.05341
99.05342
Activity (pCi/g-dry ± 2a counting
error)
» |
-------
TABLE A.10 - Continued
oo
Cnnvnl^ IT\
sample 1U
NLHF117-C
NLHF117-C
NLHF117-C
NLHF 1 17-C-DU
NLHF 1 17-C-DU
NLHF 1 17-C-DU
NLHF 1 17-C-DU
NLHF 1 17-C-DU
NLHF 122-C
NLHF 122-C
NLHF 122-C
NLHF 122-C
NLHF 131-C
NLHF 131-C
NLHF 131-C
NLHF 131-C
NLHF 131-C
NLHF 165-C
Core Slice
(cm)
10-15
15-24
24-34
00-05
05-10
10-15
15-30
30-45
00-05
05-10
10-15
15-25
00-05
05-10
10-15
15-28
28-42
00-05
NAREL ID
99.05343
99.05344
99.05345
99.05331
99.05332
99.05333
99.05334
99.05335
99.05346
99.05347
99.05348
99.05349
99.05326
99.05327
99.05328
99.05329
99.05330
99.05229
Activity (pCi/g-dry ± 2o counting
2MTh
0.69 ± 0.29
0.55 ± 0.30
0.95 ±0.55
ND
ND
ND
ND
ND
ND
ND
1.02 ±0.47
1.19 ±0.25
ND
1.68 ±0.90
ND
ND
ND
1.32 ±0.81
»4mpa
2.4 ± 2.2
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2"Ra
1.70 ±0.47
1.55 ±0.42
0.88 ± 0.86
2.34 ± 0.98
0.99 ± 0.98
1.49 ±0.84
1.03 ±0.59
1.73 ±0.81
1.75 ±0.89
1.23 ±0.73
1.16 ±0.62
1.46 ±0.43
1.3 ±1.3
1.4 ±1.2
1.8 ±1.2
1.68 ±0.85
1.67 ±0.84
1.8±1.1
214Pb
0.649 ± 0.048
0.601 ± 0.047
0.560 ± 0.078
0.647 ± 0.075
0.621 ±0.079
0.617 ±0.071
0.642 ± 0.053
0.639 ± 0.066
0.748 ± 0.075
0.545 ± 0.075
0.667 ± 0.057
0.618 ±0.045
0.50 ±0.12
0.54 ±0.11
0.50 ±0.10
0.562 ± 0.079
0.597 ± 0.084
0.37 ±0.10
error)
IUBi
0.604 ± 0.057
0.527 ± 0.047
0.5 19 ±0.087
0.5 18 ±0.075
0.576 ± 0.083
0.481 ±0.078
0.553 ±0.057
0.506 ± 0.070
0.687 ± 0.076
0.530 ±0.077
0.528 ±0.063
0.533 ± 0.052
0.42 ±0.1 3
0.46 ±0.11
0.54 ±0.10
0.556 ± 0.082
0.533 ± 0.082
0.37 ±0.10
»su
0.106 ±0.028
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.090 ± 0.026
ND
ND
ND
ND
ND
ND
-------
TABLE A.10 - Continued
1
Sample ID
NLHF 165-C
NLHF 165-C
NLHF 165-C
NLHF 176-C
NLHF 176-C
NLHF 176-C
NLHF 176-C
NLHF 176-C
NLHF 180-C
NLHF 180-C
NLHF 180-C
NLHF 180-C
NLHF 180-C
NLHF 192-C
NLHF 192-C
NLHF 192-C
NLHF 192-C
NLHF 192-C
Core Slice
(cm)
05-10
10-15
15-35
00-05
05-10
10-15
15-30
30-53
00-05
05-10
10-15
15-30
30-46
00-05
05-10
10-15
15-27
27-39
NAREL ID
99.05230
99.05231
99.05232
99.05257
99.05258
99.05259
99.05260
99.05261
99.05233
99.05234
99.05235
99.05236
99.05237
99.05252
99.05253
99.05254
99.05255
99.05256
Activity (pCi/g-dry ± 2o counting
«4Th
ND
ND
ND
ND
1.46 ±0.83
1.46 ±0.83
ND
0.91 ±0.44
1.4±1.0
1.74 ±0.93
ND
ND
ND
ND
1.30 ±0.48
ND
ND
ND
^-Pa
ND
ND
2.4 ± 2.3
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
3.2 ± 2.6
ND
M6Ra
2.0± I.I
i.41±0.97
1.44 ±0.53
2.2 ±1.2
2.3 ±1.2
ND
1.62 ±0.54
1.33 ±0,59
1.5 ±1.5
2.2 ±1.3
1.66 ±0.85
2.14 ±0.67
1.44 ±0.79
2.4 ±1.3
2.4 ±1.3
1.7 ±1.1
1.56 ±0.54
1,78 ±0.91
114Pb
0.50 ±0.10
0.540 ± 0.097
0.626 ± 0.055
0.51 ±0.12
0.48 ±0.12
0.49 ±0.10
0.588 ± 0.059
0.563 ± 0.054
0.40 ±0.14
0.44 ±0.12
0.598 ±0.076
0,6 16 ±0.063
0.561 ±0.067
0.583 ± 0.092
0.478 ± 0.099
0.607 ±0.084
0.6 12 ±0.057
0.580 ± 0.086
error)
1MB,
0.55 ±0.11
0.444 ± 0.092
0.51 7 ±0.056
0.56 ±0.12
0.44 ±0.12
0.39 ±0.10
0.529 ±0.060
0.5 13 ±0.060
0.40 ±0.1 3
0.51 ±0.12
0.558 ±0.091
0.462 ± 0.070
0.475 ± 0,066
0.38 ±0.11
0.424 ± 0.096
0.408 ± 0,085
0.549 ±0.068
0.541 ± 0.090
»SU
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-------
TABLE A. 10 - Continued
;
ample ID
NLHF 193-C
NLHF 193-C
NLHF 193-C
NLHF 193-C
NLHF 193-C
NLHF 201-C
NLHF 201-C
NLHF 201-C
NLHF 201-C
NLHF 201-C
NLHF 205-C
NLHF 205-C
NLHF 205-C
NLHF 205-C
NLHF221-C
NLHF221-C
NLHF221-C
NLHF221-C
Core Slice
(cm)
00-05
05-10
10-15
15-30
30-52
00-05
05-10
10-15
15-25
25-36
00-05
05-10
10-15
15-36
00-05
05-10
10-15
15-33
NAREL ID
99.05247
99.05248
99.05249
99.05250
99.05251
99.05360
99.05361
99.05362
99.05363
99.05364
99.05238
99.05239
99.05240
99.05241
99.05365
99.05366
99.05367
99.05368
Activity (pCi/g-dry ± 2o counting error)
H4Th
ND
ND
ND
ND
ND
ND
1.19 ±0.91
ND
ND
0.73 ±0.3 8
2.14 ±0.84
1.69 ±0.49
ND
3.39 ±0.71
ND
ND
ND
ND
2MraPa
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
7.8 ±4.4
4.5 ±2.9
ND
ND
ND
ND
ND
"&Ra
1.2±1.4
2.0 ±1.3
2.2 ±1.4
1.67 ±0.87
1.72 ±0.90
1.3 ±1.4
ND
1.6±1.2
1.83 ±0.70
1.55 ±0.73
2.3 ±1.3
1.62 ±0.77
1.79 ±0.80
ND
1.5 ±1.3
1.3 ±1.3
2.0± l.l
1.76 ±0.43
2Upb
0.62 ±0.10
0.55±0.10
0.57 ±0.11
0.647 ± 0.075
0.679 ± 0.085
0.54 ±0.13
0.54 ±0.12
0.66 ±0.11
0.648 ±0.080
0.632 ±0.069
0.47 ±0.11
0.654 ± 0.078
0.674 ±0.081
0.546 ± 0.069
0.48 ±0,11
0.52 ±0.12
0.617 ±0.086
0.5 15 ±0.041
114Bi
0.55 ±0.12
0.42 ±0.10
0.44 ±0.10
0.581 ±0.074
0.693 ± 0.084
0.38 ±0.13
0.48 ±0.13
0.55 ±0.11
0.54 ±0.10
0.566 ± 0.078
0.40 ±0.11
0.61 6 ±0.096
0.546 ± 0.083
0.466 ± 0.067
0.45 ±0.11
0.44 ±0.12
0.579 ±0.088
0.471 ±0.046
13SU
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.098 ±0.043
ND
ND
0.1 12 ±0.048
ND
ND
0.091 ±0.077
0.126 ±0.064
ND
-------
TABLE A.10 - Continued
Sample ID
NLHF221-C
Core Slice
(cm)
33-52
NAREL ID
99.05369
Activity (pCfg-dry ± la counting
error)
2*Th «4.pa «Ra »,pb 2,43; «Su
0.40 ±0.20
ND
1.27 ±0.25
0.470 ± 0.023
0.413 ±0.024
ND
BACKGROUND SAMPLES
NLHF 237-C-BG
NLHF 237-C-BG
NLHF 237-C-BG
NLHF 237-C-BG
NLHF 237-C-BG
NLHF 237-C-DU-BG
NLHF 237-C-DU-BG
NLHF 237-C-DU-BG
NLHF 237-C-DU-BG
NLHF 237-C-DU-BG
00-05
05-10
10-15
15-28
28-41
00-05
05-10
10-15
15-25
25-36
99.05336
99.05337
99.05338
99.05339
99.05340
99.05355
99.05356
99.05357
99.05358
99.05359
ND
ND
0.89 ±0.40
ND
ND
ND
ND
ND
ND
1.18 ±0.35
ND
ND
3.8 ±3.1
2.8 ±2.5
ND
ND
ND
ND
ND
ND
2.6 ±1.1
2.29 ± 0.87
2.19 ±0.68
2.47 ± 0.58
1.71 ±0.78
2.4 ± 1.1
1.96 ±0.59
2.07 ± OJ6
2.05 ±0.56
2.00 ± 0.59
0.839 ±0.082
0.768 ±0.071
0.742 ± 0.070
0.772 ± 0.063
0.628 ± 0.072
0.763 ± 0.090
0.703 ± 0.050
0.760 ± 0.049
0.701 ± 0.053
0.774 ± 0.056
0.605 ± 0.091
0.682 ±0.081
0.672 ± 0.080
0.719 ±0.066
0.580 ±0.082
0.726 ±0.093
0.669 ± 0.059
0.672 ±0.058
0.668 ± 0.060
0.685 ± 0.065
ND
ND
ND
ND
ND
ND
ND
0.128 ±0.034
0.128 ±0.034
0.1 20 ±0.035
Note: "ND" indicates the radionuclide was not detected by gamma spectrometry. No other gamma-emitting radionuclides were detected
in these samples.
-------
TABLE A.11
Gamma Spectrometry Results for Sediment Core Samples
Thorium Decay Chain and Other Gamma Emitting Radionuclides
Sample ID
Core
Slice
(cm)
NAREL
ID
Activity (pCi/g-dry ±
2MRa
M4Ra
21IPb
I12Bi
1
2a counting error)
"•n
*°Co
U7Cs
«,K
STUDY SAMPLES
NLHF 025-C
NLHF 025-C
NLHF 025-C
NLHF 025-C
NLHF 025-C
NLHF 028-C
NLHF028-C
NLHF 028-C
NLHF 028-C
NLHF 028-C
NLHF 032-C
NLHF032-C
NLHF 032-C
NLHF 032-C
NLHF 032-C
00-05
05-10
10-15
15-34
34-53
00-05
05-10
10-15
15-31
31-48
00-05
05-10
10-15
15-34
34-53
99.07514
99.07515
99.07516
99.07517
99.07518
99.07479
99.07480
99.07481
99.07482
99.07483
99.07499
99.07500
99.07501
99.07502
99.07503
1.07 ±0.12
1.04 ±0.11
1.19±0.13
1.250 ±0.066
1.30±0.11
0.90 ±0.1 5
0.80 ±0.10
1.16±0.10
1.1 70 ±0.064
1.190 ±0.059
0.94 ±0.12
1.00 ±0.11
1.28 ±0.12
1.330 ±0.072
1.1 70 ±0.045
0.75 ± 0.85
ND
0.7±1.1
1.25 ±0.50
ND
1.2 ±1.1
0.85 ± 0.74
0.74 ± 0.96
1.39 ±0.48
1.05 ±0.47
0.65 ± 0.98
1.35 ±0.80
1.0±1.1
1.10±0.55
0.80 ±0.34
1.060 ±0.074
0.994 ± 0.080
1.1 20 ±0.080
1.280 ±0.042
1.34±0.13
0.876 ±0.094
0.755 ± 0.061
1.100 ±0.073
1.210 ±0.043
1.220 ±0.039
0.943 ± 0.070
1.070 ±0.064
1.1 60 ±0.085
1.350 ±0.046
1. 210 ±0.032
1.21 ±0.40
1.17±0.41
0.71 ±0.57
1.29 ±0.23
0.93 ± 0.43
0.79 ± 0.73
0.76±0.32
1.12 ±0.38
1.06 ±0.30
1.28 ±0.22
0.85 ± 0.52
1.16 ±0.40
1.05 ±0.42
1.10 ±0.25
1.13±0.17
0.381 ±0.053
0.343 ± 0.050
0.381 ±0.058
0.466 ± 0.027
0.363 ± 0.072
0.337 ± 0.063
0.295 ± 0.046
0.411 ±0.046
0.433 ±0.027
0.486 ±0.027
0.336 ±0.052
0.406 ±0.046
0.418 ± 0.054
0.490 ±0.031
0.448 ±0.021
< 0.091
< 0.099
< 0.079
0.206 ±0.0 17
< 0.085
0.138 ±0.030
< 0.062
0.068 ±0.022
< 0.041
0.147 ±0.015
< 0.076
0.058 ± 0.024
0.071 ± 0.028
0.534 ±0.023
< 0.028
0.085 ± 0.033
0.129 ±0.033
0.1 96 ±0.041
0.188 ±0.019
0.064 ± 0.036
0.1 29 ±0.040
0.1 03 ±0.028
0.1 57 ±0.030
ND
0.1 10 ±0.016
0.070 ± 0.027
0.073 ± 0.029
0.145 ± 0.036
0.1 83 ±0.022
0.032 ±0.011
18.00 ±0.88
18.40 ±0.84
18.70 ±0.87
19.40 ±0.50
21.80 ±0.85
15.00 ±0.91
13.90 ±0.74
17.50 ±0.76
17.30 ±0.46
18.50 ±0.47
16.10 ±0.79
17.10 ±0.78
17.40 ±0.86
19.10 ±0.53
18.80 ±0.39
-------
TABLE A.11 - Continued
Sample ID
NLHF034-C
NLHF034-C
NLHF034-C
NLHF 034-C
NLHF 034-C
NLHF 039-C
NLHF 039-C
NLHF 039-C
NLHF 039-C
NLHF 039-C
NLHF 047-C
NLHF 047-C
NLHF 047-C
NLHF 047-C
NLHF 047-C
NLHF 048-C
NLHF048-C
NLHF 048-C
NLHF 048-C
Core
Slice
(cm)
00-05
05-10
10-15
15-33
33-52
00-05
05-10
10-15
15-28
28-42
00-05
05-10
10-15
15-24
24-33
00-05
05-10
10-15
15-34
NAREL
ID
99.07509
99.07510
99.07511
99.07512
99,07513
99.07524
99.07525
99.07526
99.07527
99.07528
99.07494
99.07495
99.07496
99.07497
99.07498
99.07489
99.07490
99.07491
99.07492
Activity (pCi/g-dry
2MRa
0.88 ±0.12
1.08 ±0.11
1.010 ±0.094
1.1 80 ±0.056
1.1 80 ±0.044
0.89 ±0.11
0.984 ±0.071
0.91 ±0.10
0.722 ± 0.045
1.1 90 ±0.050
1.01 ±0.13
0.92 ±0.1 3
0.73 ±0.1 3
0.92 ±0.11
0.990 ±0.081
1.00 ±0.11
1.01 ±0.11
0.968 ± 0.081
1.110 ±0.067
^Ra
ND
0.95 ± 0.75
0.97 ±0.95
1.32 ±0.46
1.00 ±0.34
1,5 ±1.0
1.05 ±0.67
0.82 ± 0.90
0,72 ± 0.43
1.31 ±0.41
0.8 ±1.3
0.9 ±1.3
ND
0.86 ±0.74
0.82 ±0.74
1.92 ±0.97
1.46 ±0.96
0.88 ±0.72
1.18 ±0.48
J12Pb
0.980 ±0.077
1.060 ±0.064
0.932 ±0.065
1.1 60 ±0.036
1.220 ±0.032
0.855 ±0.078
1.020 ± 0.054
0.822 ± 0.066
0.753 ±0.034
1.240 ±0.035
0.873 ±0,079
0.944 ±0.089
0.806 ±0.075
1.020 ±0.066
0.957 ±0.057
1.010 ±0.072
1.000 ±0.075
0.985 ±0.056
1.1 00 ±0.045
1UBI
0.90 ±0.59
1.04 ±0.43
1.08 ±0.33
1.11±0.19
1.23 ±0.15
0.67 ±0.45
0.64 ± 0.28
0.89 ±0.42
0.70 ±0.1 8
1.16±0.17
0.43 ± 0.52
0.97 ±0.56
0.89 ±0.42
0.81 ±0.46
0.76 ±0.32
1.16 ±0.45
1.26 ±0.46
1.06±0.31
0.99 ±0.30
± 20 counting error)
2MTJ
0.385 ± 0.057
0.383 ± 0.046
0,358 ± 0.044
0.439 ± 0.024
0.438 ±0.021
0.3 14 ±0.048
0.378 ±0.033
0.330 ±0.043
0.265 ± 0.020
0.457 ±0.023
0.287 ± 0.056
0.396 ±0.057
0.306 ±0.056
0.367 ± 0.050
0.364 ± 0.035
0.355 ±0.051
0.380 ±0.052
0.383 ± 0.041
0.407 ±0.027
"Co
< 0.071
< 0.074
0.055 ±0.021
0.037 ±0.011
< 0.025
0.046 ± 0.022
0.051 ±0.0 16
0.1 23 ±0.024
< 0.027
< 0.031
0.060 ± 0.026
0.043 ± 0.024
< 0.083
0.062 ±0.029
0.072 ±0.0 18
0.050 ±0.022
0.075 ±0.022
0.044 ±0.01 8
0.046 ±0.0 14
137Cs
0.059 ±0.029
0.095 ± 0.026
0.076 ±0.025
0.076 ±0.01 7
ND
0.04 1 ±0,026
0.045 ±0.019
0.024 ±0.025
ND
ND
0.084 ±0.027
0.100 ±0.029
0.070 ±0.031
0.08 1 ±0.036
0.087 ±0.021
0.088 ±0.023
0.107 ±0.023
0.078 ± 0.024
0.093 ±0.0 17
40R
15.80 ±0.83
18.00 ±0.80
16. 60 ±0.73
18.10±0.44
18.40 ±0.37
19.30 ±0.86
17.90 ±0.59
19.90 ±0.80
16.40 ±0.41
19.60 ±0.42
17.90 ±0.84
17.20 ±0.86
14.00 ±0.85
17.5 ±1.0
17.80 ±0.62
18.30 ±0.68
19.00 ±0.68
17.70 ±0.66
17.80 ±0.49
-------
TABLE A.11 - Continued
1 Sample ID
1 NLHF 048-C
1 NLHF 050-C
1 NLHF 050-C
1 NLHF 050-C
I NLHF 050-C
1 NLHF 050-C
1 NLHF 051-C
1 NLHF 051-C
1 NLHF 051-C
I NLHF 051-C
1 NLHF 051-C
1 NLHF 056-C
1 NLHF 056-C
1 NLHF 056-C
1 NLHF 056-C
1 NLHF 056-C
1 NLHF 062-C
1 NLHF 062-C
1 NLHF 062-C
Core
Slice
(cm)
34-53
00-05
05-10
10-15
15-33
33-52
00-05
05-10
10-15
15-33
33-52
00-05
05-10
10-15
15-31
31-48
00-05
05-10
10-15
NAREL
ID
99.07493
99.07469
99.07470
99.07471
99.07472
99.07473
99.07504
99.07505
99,07506
99.07507
99.07508
99.07519
99.07520
99.07521
99.07522
99.07523
99.05262
99.05263
99,05264
Activity (pCi/g-dry ± 2o counting error)
2MRa
1.290 ±0.059
0.97 ±0.16
0.85 ±0.13
0.87 ±0.12
0.984 ±0.055
1.070 ±0.047
0.94 ±0.13
0.83 ±0.12
0.88 ±0.1 3
0.958 ±0.062
0.970 ±0.054
0.81 ±0.13
0.86 ±0.14
0.793 ±0.09 1
0.805 ± 0.070
0.951 ±0.097
1.390 ±0.081
1.1 00 ±0.063
1.07±0.11
2MRa
1. 48 ±0.49
1,3 ±1.7
1.41 ±0.94
0.77 ±0.91
1,00 ±0.43
1.10±0.37
ND
1.0 ±1.3
1.1 ±1.2
0.84 ±0.44
0.96 ±0.42
0.9 ±1.3
1.2±1.1
1.05 ±0.89
0.68 ± 0.58
ND
1.62 ±0.56
1.07 ±0.43
0.82 ± 0.92
2"Pb
1.270 ±0.039
1.03 ±0.11
0.868 ± 0.077
0.917 ±0.075
1.010 ±0.035
1.060 ±0.032
0.993 ± 0.092
1.0 10 ±0,086
1.020 ±0.081
0.978 ±0.041
0.982 ±0.037
0.996 ± 0.083
0.859 ±0.084
0.80 ±0.12
0.835 ± 0.086
0.98 ±0.12
1. 430 ±0.051
1.170 ±0.046
1.010 ±0,073
M1Bi
1.30±0.19
1.13 ±0.64
0.58 ± 0.45
1.15 ±0.59
1.11 ±0,19
0.97 ±0.16
1.06 ±0.58
1.02 ±0.51
0.76 ± 0.62
1.02 ±0.29
1.00 ±0.24
0.84 ± 0.54
ND
0.52 ±0.39
0.67 ±0.31
1.05 ± 0.39
1.32 ±0.26
1.05 ±0,23
1. 26 ±0.40
IHn
0.488 ±0.026
0.387 ±0.066
0.3 14 ±0.056
0.299 ±0.054
0.371 ±0.024
0.373 ±0.021
0.362 ± 0.057
0.3 80 ±0.057
0.353 ± 0.058
0.332 ± 0.026
0.368 ± 0.022
0.360 ± 0.054
0.321 ±0.059
0.250 ±0.067
0.290 ± 0.045
0.340 ± 0.066
0.538 ± 0.032
0.41 9 ±0.030
0,379 ±0,047
60Co
0.038 ±0.012
0.039 ±0.033
< 0.089
0.060 ± 0.025
0,089 ±0.01 3
0.179± 0.012
0.084 ± 0.029
0.062 ± 0.027
< 0.080
0.067 ±0.0 14
0.095 ±0.012
0.046 ± 0.027
0.056 ± 0.025
0.036 ±0.021
< 0.058
0.051 ±0.024
< 0.057
< 0.047
< 0.069
"TCs
0.078 ±0.01 7
0.083 ± 0.042
0.047 ± 0.029
0.060 ± 0.027
0.067 ±0.016
0.082 ±0.0 13
0.087 ± 0.030
0.084 ± 0.032
0.078 ±0.035
0.080 ±0.0 18
0.085 ±0.0 15
0.076 ±0.031
0.090 ± 0.033
0.05 8 ±0.028
0.068 ± 0.023
0.091 ±0.036
ND
0.022 ±0.0 18
0.074 ± 0.029
"K
16.90 ± 0.44
18.8±1.2
17. 10 ±0.94
18.00 ±0.82
18.30 ±0.45
18.80 ±0.39
19.60 ± 0.89
19. 10 ±0.86
17. 10 ±0,86
17.90 ±0.46
16.30 ±0.40
18.00 ±0.84
18.00 ±0.89
22.20 ± 0.83
23. 10 ±0.65
22.40 ± 0.83
17.80 ±0.56
18.50 ±0.54
17.50 ±0.77
-------
TABLE A. 11 - Continued
Sample ID
NLHF 062-C
NLHF 062-C
NLHF064-C
NLHF 064-C
NLHF 064-C
NLHF 064-C
NLHF 064-C
NLHF 066-C
NLHF 066-C
NLHF 066-C
NLHF 066-C
NLHF 066-C
NLHF074-C
NLHF074-C
NLHF 074-C
NLHF 074-C
NLHF 074-C
NLHF 079-C
NLHF 079-C
Core
Slice
(cm)
15-30
30-50
00-05
05-10
10-15
15-25
25-35
00-05
05-10
10-15
15-27
27-39
00-05
05-10
10-15
15-34
34-53
00-05
05-10
NAREL
ID
99.05265
99.05266
99.05267
99.05268
99.05269
99.05270
99.05271
99.07484
99.07485
99.07486
99.07487
99.07488
99.07529
99.07530
99.07531
99.07532
99.07533
99.07474
99.07475
Activity (pCi/g-dry ± 20 counting
2MRa
1.450 ±0.067
0.953 ± 0.052
0.8 J± 0.14
0.76 ±0.1 3
1.1 20 ±0.078
1.21 ±0.11
1.17±0.14
0.86 ±0.14
0.94 ±0.1 2
0.84 ±0.11
0.920 ± 0.065
0.91 ±0.11
0.99 ±0.15
0.97 ±0.13
0.90 ±0.t3
0.91 7 ±0.083
1.020 ±0.076
1.20±0.15
0.928 ± 0.097
IMRa
1.08 ±0.53
0,75 ±0.38
].l±1.4
0.8 ±1.0
1.17 ±0.59
0.96 ±0.88
ND
1.5 ±1.2
1.3 ±1.0
1.17±0.87
0.59 ±0.56
1.4±1.1
I.l± 1.6
1.5 ± 1.4
0.9 ±1.3
0.85 ± 0.70
0.89 ±0.56
1.2±1,7
0.94 ± 0.86
21Jpb
1.480 ±0.047
0.996 ±0.033
0.939 ±0.088
0.875 ± 0.078
1.090 ±0.058
1. 190 ±0.070
1.080 ±0.090
1.050 ±0.099
0.959 ±0.077
0.953 ± 0.068
0.979 ±0.049
1.140 ±0.094
0.99 ±0.10
1.040 ±0.091
0.998 ±0.082
0.955 ±0.053
0.981 ±0.047
1,08±0.10
0.942 ± 0.066
il2Bi
1.45 ±0.25
1.02 ±0.17
1.26 ±0.65
1.15±0.39
1.28 ±0.32
1.17±0.37
0.82 ± 0.60
0.96 ±0.67
0.81 ±0.55
1.25 ±0.44
0.88 ±0.25
1.00 ±0.44
0.87 ±0.67
1.12 ±0.59
0.95 ±0.57
1.09 ±0.35
0.71 ±0.25
0.79 ±0.71
1.10±0.34
M«T1
0.541 ±0.031
0.376 ±0.022
0.370 ±0.063
0.342 ±0.055
0.3 82 ±0.038
0.443 ± 0.045
0.430 ±0.067
0.375 ± 0.068
0.341 ±0.055
0,352 ±0.050
0.347 ± 0.034
0.390 ±0.048
0.344 ± 0.064
0.373 ± 0.058
0.351 ±0.059
0.369 ±0.038
0.381 ±0.032
0,395 ±0.067
0.369 ±0.041
error)
MCo
< 0.043
< 0.033
0.074 ± 0.030
0.072 ± 0.025
0.054 ±0.01 8
0.099 ±0,023
0.077 ±0.029
0.064 ± 0.026
0.048 ±0.021
0.056 ±0.021
0.062 ±0.01 5
0.065 ± 0.026
0.096 ± 0.026
0.086 ±0.027
< 0.072
0.048 ±0.019
0.069 ±0.0 17
< 0.070
< 0.083
"7Cs
0.019 ±0.016
ND
0.088 ±0.031
0.1 24 ±0.031
0.061 ±0.024
0.099 ±0.026
0,161 ±0.040
0.1 15 ±0.027
0.090 ± 0.023
0.095 ± 0.023
0.100 ±0.020
0.081 ±0.033
0.079 ± 0.028
0.095 ± 0.032
0.094 ± 0.030
0.097 ± 0.020
0.081 ±0.021
0.102 ±0,028
0.062 ± 0.025
40K
17.70 ±0.50
17.30 ±0.42
18.00 ±0.94
17.40 ±0.84
18.10 ±0.65
17.80 ±0.71
18.30 ±0.98
19.40 ± 0,84
19.40 ±0.72
19.00 ±0.66
20.00 ± 0.59
2 1.70 ±0.82
19. 70 ±0.87
19.80 ±0.89
19. 10 ±0.87
18.30 ±0.64
17.50 ±0.60
18.60 ±0.89
17.60±0.73
-------
TABLE A.11 - Continued
1 Sample ID
1 NLHF 079-C
1 NLHF 079-C
I NLHF 079-C
1 NLHF 082-C
I NLHF 082-C
I NLHF 082-C
1 NLHF 082-C
1 NLHF 082-C
JNLHF116-C
INLHF116-C
INLHF116-C
INLHF116-C
NLHF 1 16-C
NLHF117-C
NLHF117-C
NLHF117-C
NLHF117-C
NLHF117-C
NLHF117-C-
DU
Core
Slice
(cm)
10-15
15-33
33-51
00-05
05-10
10-15
15-33
33-51
00-05
05-10
10-15
15-30
30-53
00-05
05-10
10-15
15-24
24-34
00-05
NAREL
ID |
99.07476 1
99.07477 1
99.07478 1
99.05350 1
99.05351 1
99.05352
99.05353
99.05354 j
99.05242 1
99.05243 1
99.05244
99.05245
99.05246
99.05341
99.05342
99.05343
99.05344
99.05345
99.05331
Activity (pCi/g-dry ± 2o counting error)
M'Ra
1.14±0.12
180 ±0.058
.350 ± 0.048
1.08 ±0.10
1.05 ±0.13
1.07 ±0.12
1.120 ±0.041
1.140 ±0.061
0.86 ±0.13
0.81 ±0.13
1.030 ±0.085
1.1 40 ±0.078
1.240 ±0.060
0.836 ±0.094
0.72 ±0.11
0.908 ±0.075
0.743 ±0.061
0.86 ±0.12
0.789 ±0.092
M4Ra
0.89 ±0.95
1.02 ±0.45
1.34 ±0.39
1.06 ±0.88
1.4±1.1
1.14 ±0.89
1,32 ±0,30
1.43 ±0.46
ND
0.96 ± 0.96
1.18 ±0.64
1.17±0.59
1.38 ±0.42
1.30 ±0.97
ND
1.12 ±0.56
0.80 ±0.56
0.8 ±1.0
0.93 ±0.71
mPb
1.120 ±0.073
1.200 ±0.039
1.290 ±0.034
1.1 50 ±0.073
1.140 ±0.080
1.1 50 ±0.067
1.160 ±0.031
1.250 ±0.039
0.857 ±0.079
0.940 ± 0.073
1.030 ±0.061
1.1 70 ±0.048
1.260 ±0.045
0.778 ±0.071
0.686 ±0.070
1.040 ±0.048
0.819 ±0.044
0.802 ±0.080
0.892 ±0.070
»2Bi
1.08 ±0.50
1.02 ±0.20
1.35 ±0.17
1.05 ±0.36
1.31 ±0.57
1.20 ±0.37
1.15±0.15
1.08 ±0.20
0.56 ±0.59
1.35 ±0.45
1.57 ±0.35
1.26 ±0.25
1.21 ± 0.24
0.59 ± 0.30
1.02 ±0.39
0.89 ±0.29
1.11 ±0.25
0.76 ±0.54
0.60 ±0.35
WT,
0.355 ± 0.050
0.434 ± 0.026
0.477 ± 0.022
0.404 ±0.047
0.415 ±0.055
0.431 ±0.047
0.429 ±0.019
0.458 ± 0.026
0.311 ±0.057
0.323 ± 0.052
0.324 ±0.042
0.424 ±0.032
0.433 ±0.030
0.260 ± 0.049
0.279 ±0.047
0.379 ±0.033
0.298 ±0.028
0.304 ±0.056
0.323 ±0.047
"Co
< 0.070
0.030 ±0.012
< 0.031
< 0.084
< 0.078
< 0.083
< 0.028
< 0.040
0.050 ± 0.026
0.065 ± 0.025
0.074 ± 0.023
< 0.051
< 0.041
0.035 ± 0.025
< 0.078
< 0.051
< 0.046
< 0.076
0.055 ± 0.023
»7Cs
0.1 00 ±0.029
0.084 ±0.016
ND
ND
ND
ND
ND
ND
0.101 ±0.030
0.084 ± 0.035
0.1 10 ±0.024
0.073 ±0.021
ND
0.096 ± 0.028
0.078 ± 0.029
0.031 ±0.0 18
0.070 ±0.0 18
0.1 02 ±0.036
0.081 ±0.029
40K
16.40 ±0.77
18.90 ±0.47
21.30 ±0.41
19.30 ±0.81
18.00 ±0.85
18.00 ±0.78
18.20 ±0.37
18.90 ±0.47
15.50 ±0.86
16.90 ±0.84
18.00 ±0.70
18.20 ±0.58
20.40 ± 0.53
17.00 ±0.60
14.70 ± 0.75
16.30 ±0.61
15.60 ±0.53
15.10 ±0.83
18.80 ±0.62
-------
TABLE A.11 - Continued
Sample ID
NLHF117-C-
DU
NLHF117-C-
DU
NLHF117-C-
DU
NLHF117-C-
DU
NLHF 122-C
NLHF 122-C
NLHF 122-C
NLHF 122-C
NLHF 13 1 -C
NLHF131-C
NLHF131-C
NLHF 131-C
NLHF 131-C
NLHF 165-C
NLHF 165-C
NLHF 165-C
NLHF 165-C
Core
Slice
(cm)
05-10
10-15
15-30
30-45
00-05
05-10
10-15
15-25
00-05
05-10
10-15
15-28
28-42
00-05
05-10
10-15
15-35
NAREL
ID
99.05332
99.05333
99.05334
99.05335
99.05346
99.05347
99.05348
99.05349
99,05326
99.05327
99.05328
99.05329
99.05330
99.05229
99.05230
99.05231
99.05232
Activity (pCi/g-dry
mRa
0.81 ±0.11
0.755 ±0.098
0.817 ±0.084
1.020 ±0.094
0.965 ± 0.095
0.78 ±0.1 2
0,905 ± 0.079
0.940 ± 0.075
0.92 ±0.1 9
0.81 ±0.17
1.00 ±0.16
0.96 ±0.1 2
1.00 ±0.12
0.81 ±0.15
0.82 ±0.1 6
0.88 ±0.14
0.923 ± 0.078
J24Ra
1.10±0.84
1.23 ±0.95
ND
0.58 ±0.62
1.10 ±0.72
1.45 ±0.92
0.93 ± 0.56
0,75 ± 0.52
ND
ND
1.3 ±1.5
1.2±1.1
2.0 ±1.3
1.4 ±1.6
ND
ND
0.62 ±0.64
I12Pb
1.070 ±0.091
0.967 ± 0.080
0.892 ±0.064
1,030 ±0.078
0.958 ±0.080
0.856 ±0.065
0.939 ±0.057
0.941 ±0.045
0.87 ±0.12
1.04±0.!1
1.12±O.IO
1.060 ±0.085
1.1 00 ±0.087
0.866 ±0.093
0.955 ±0.096
0.971 ±0.095
0.940 ±0.052
2UBi
1.24 ±0.43
0.80 ± 0.39
0.94 ± 0.32
0.64 ±0.35
0.85 ± 0.36
0.70 ±0.40
1.11 ±0.32
1.15 ±0.26
1.33 ±0.81
0.86 ±0.77
1.24 ±0.67
0.97 ± 0.54
1.02 ±0.53
ND
1.37 ±0.64
1.22 ±0.60
0.69 ±0.28
± 2o counting
1MTI
0.362 ± 0.055
0.301 ±0.049
0.275 ± 0.036
0.316 ±0.046
0.328 ± 0.047
0.292 ± 0.045
0.322 ±0.040
0.304 ±0.029
0.296 ± 0.080
0.386 ± 0.073
0.392 ± 0.067
0.361 ± 0.050
0.355 ± 0.052
0.311 ±0.065
0.306 ±0.068
0.328 ±0.061
0.325 ± 0.033
error)
60Co
< 0.089
< 0.079
< 0.065
0.042 ±0.025
0.051 ±0.021
0.058 ±0.024
0,034 ±0.019
0.051 ±0.016
0,058 ±0.035
< 0.097
< 0.089
0.049 ± 0.026
0.049 ± 0.028
0.039 ±0.026
0.070 ±0.029
0.055 ±0.029
0.034 ±0.017
IJ7Cs
0.091 ±0.032
0.098 ± 0.030
0.054 ± 0.025
0.1 06 ±0.028
0.1 27 ±0.031
0.080 ± 0.027
0.089 ± 0.025
0.071 ±0.021
0.1 34 ±0.045
0.1 28 ±0.040
0.1 27 ±0.03 5
0.108 ±0.033
0.099 ± 0.033
0.082 ±0.043
0.128 ±0.038
0.1 05 ±0.035
0.101 ±0.023
40R
20.80 ±0.79
18.00 ±0.71
18.20 ±0.62
19.80 ±0.70
18.90 ±0.64
16. 10 ±0.79
18.60 ±0.68
16.10 ±0.58
18.3 ±1.2
19.4±1.1
18.90 ±0.97
18.10±0.87
18.50 ±0.88
16. 10 ±0.92
18.40 ±0.96
17. 10 ±0.89
17.00 ±0.61
-------
TABLE A.11 - Continued
SO
Sample ID
NLHF 176-C
NLHF 176-C
NLHF 176-C
NLHF 176-C
NLHF 176-C
NLHF 180-C
NLHF 180-C
NLHF 180-C
NLHF 180-C
NLHF 180-C
NLHF
NLHF
NLHF
NLHF
NLHF
NLHF
NLHF
NLHF
NLHF
192-C
192-C
192-C
192-C
192-C
193-C
193-C
193-C
193-C
Core
Slice
(cm)
4AREL
ID r
Activity (pCi/g-dry ± 2o counting error)
M'Ra
00-05 99.05257 1.08 ±0.17
05-10 99.05258 0.82 ±0.16
10-15 99.05259 1 0.94 ±0.16
15-30 99.05260 1 0.884 ±0.075
30-53 99.05261 | 0.963 ± 0.084
00-05
05-10
10-15
15-30
30-46
00-05
05-10
10-15
15-27
27-39
00-05
05-10
10-15
15-30
99.05233 1
99.05234 1
99.05235
99.05236 1
99.05237 j
99.05252
99.05253 1
99.05254
99.05255
99.05256
99.05247
99.05248
99.05249
99.05250
0.88 ± 0.20
0.81 ±0.18
0.89 ±0.11
0.89 ±0.10
1.1 50 ±0.094
0.92 ±0.1 5
0.81 ±0.11
0.99 ±0.10
0.995 ±0.091
0.96 ±0.14
1.03 ±0.15
0.88 ±0.12
0.84 ±0.1 2
0.93 ±0.10
M4Ra
1.2±1.7
1.1 ±1.6
1.4 ±1.5
0.65 ± 0.70
0.81 ±0.62
ND
ND
1.27 ±0.82
1.00 ±0.84
0.81 ±0.71
ND
0.89 ±0.82
0.81 ±0.80
1.27 ±0.69
ND
ND
1.14 ±0.90
ND
1.17 ±0.89
inPb
1.01 ±0.11
1.09 ±0.11
1.06 ±0.10
0.940 ±0.056
0.958 ± 0.054
0.99 ±0.1 3
1.03 ±0.11
1.010 ±0.078
0.978 ±0.066
1.020 ±0.073
1.00 ±0.11
0.992 ±0.094
1.020 ±0.084
0.983 ±0.056
1.050 ±0.087
1.04±0.13
0.964 ±0.098
1.04 ±0.10
1.020 ±0.076
"2Bi
1.22 ±0.70
1.28 ±0.65
1.06 ±0.65
0.89 ±0.34
1.03 ±0.35
1.38 ±0.83
1.52 ±0.72
1.11 ±0.44
0.86 ±0.33
0.76 ± 0.40
0.84 ± 0.46
0.60 ±0.44
0.81 ±0.38
1.41 ±0.37
0.64 ± 0.58
1.06 ±0.48
1.26 ±0.46
0.74 ± 0.44
0.87 ± 0.40
:OST,
<0Co
0.384 ± 0.073 < 0.092
0.396 ±0.073 0.049 ±0.031
0.353 ± 0.067 < 0.089
0.361 ±0.036 < 0.064
0.383 ± 0.037 < 0.044
0.3 52 ±0.090
0.296 ±0.077
0.322 ±0.055
0.342 ±0.042
0.336 ±0.042
0.321 ±0.074
0.3 59 ±0.059
0.334 ± 0.052
0.355 ± 0.040
0.345 ± 0.059
0.280 ±0.080
0.343 ± 0.060
0.386 ±0.061
0.342 ± 0.046
< 0.105
< 0.090
< 0.075
< 0.071
< 0.080
0.071 ±0.039
< 0.087
0.046 ± 0.024
< 0.058
< 0.081
< 0.104
< 0.093
< 0.098
< 0.088
»7Cs
0.158 ±0.039
0.105 ±0.037
0.122 ±0.041
0.117 ±0.022
0.1 03 ±0.021
0.126 ±0.053
0.1 15 ±0.040
0.127 ±0.034
0.141 ±0.029
0.1 39 ±0.031
0.130 ±0.042
0.1 39 ±0.043
0.1 00 ±0.032
0.1 13 ±0.027
0.1 83 ±0.044
0.125 ±0.045
0.136 ±0.038
0.1 65 ±0.042
0.140 ±0.033
<»K
19.1 ±1.1
18.2 ±1.0
18.30 ±0.98
17.30 ±0.65
17.00 ±0.64
18.0 ±1.2
17.5 ±1.1
18.20 ±0.86
17.50 ±0.71
20.00 ±0.71
18.20 ±0.85
18.90 ±0.76
19.20 ±0.68
18.20 ±0.73
18. 10 ±0.99
19.50 ±0.89
18.60 ±0.76
18.70 ±0.80
20.80 ± 0.77
-------
TABLE A.11 - Continued
Sample ID
NLHF 193-C
NLHF201-C
NLHF201-C
NLHF 201 -C
NLHF 201 -C
NLHF201-C
NLHF 205-C
NLHF 205-C
NLHF 205-C
NLHF 205-C
NLHF221-C
NLHF221-C
NLHF 221-C
NLHF 221-C
NLHF 221-C
Core
Slice
(cm)
30-52
00-05
05-10
10-15
15-25
25-36
00-05
05-10
10-15
15-36
00-05
05-10
10-15
15-33
33-52
NAREL
ID
99.05251
99.05360
99.05361
99.05362
99.05363
99.05364
99.05238
99.05239
99.05240
99.05241
99.05365
99.05366
99.05367
99.05368
99.05369
Activity (pCi/g-dry ± 2o counting
JMRa
1.06 ±0,11
1.07 ±0.18
0.91 ±0.18
0.90 ±0.1 5
0.88±O.J3
0.91 ±0.12
1.04 ±0.17
0.99 ±0.12
0.89 ±0.10
1.030 ±0.093
0.85 ±0.16
0.88 ±0.17
0.98 ±0.1 3
0.849 ± 0.069
0.672 ±0.037
II4Ra
1.47 ±0.93
1.2 ±2.0
ND
1.4 ±1.5
0.99 ±0.93
0.73 ± 0.75
ND
1.16 ±0.93
1.2±t.O
0.74 ±0.93
0.8 ±1.5
ND
1.5±1.2
0.64 ± 0.56
0.76 ±0.32
211pb
1.040 ±0.085
0.91 ±0.12
0.94 ±0.1 2
0.99 ±0.10
0.962 ± 0.080
0.953 ± 0.070
0.96 ±0.11
1.010 ±0.077
0.91 5 ±0.073
1.1 20 ±0.065
0.92 ±0.10
0.92 ±0.1 2
1.000 ±0.090
0.8 12 ±0.044
0.695 ±0.024
2UBi
0.81 ±0.47
0.59 ±0.80
0.91 ±0.82
0.91 ±0.65
0.82 ±0.49
1.10 ±0.38
1.16 ±0.63
1.1 8 ±0.38
1.01 ±0.45
0.99 ± 0.40
0.93 ± 0.68
ND
1.24 ±0.55
0.93 ± 0.23
0.78 ±0.13
2MT1
0.378 ±0.048
0.340 ±0.080
0.356 ± 0.080
0.399 ± 0.067
0.324 ± 0.057
0.345 ± 0.050
0.351 ±0.072
0.351 ±0.052
0.338 ±0.047
0.366 ±0.042
0.375 ± 0.070
0.418 ±0.075
0.372 ± 0.063
0.306 ±0.029
0.264 ±0.016
error)
wCo
0.051 ± 0.026
0.055 ± 0.030
0.044 ±0.030
< 0.078
< 0.106
< 0.075
< 0.091
< 0.083
< 0.074
< 0.041
< 0.084
< 0.097
< 0.065
< 0.044
< 0.026
l37Cs
0.146 ±0.038
0.126 ±0.039
0.1 16 ±0.048
0.113 ±0.039
0.158 ±0.040
0.133 ±0.032
ND
0.050 ±0.030
0.059 ±0.029
ND
O.I 43 ±0.040
0.1 62 ±0.041
O.I 76 ±0.033
0.049 ±0.0 1 8
ND
40K
20.70 ±0.82
17.6 ±1.0
19.5±1.1
18.70 ±0.99
[6.9± 1.2
16.20 ±0.83
15.30 ±0.98
14.20 ±0.85
14.20 ±0.78
15.50 ±0.61
15.70 ±0.96
16.3 ±1.1
18.30 ±0.78
17.60 ±0.52
17.20 ±0.33
BACKGROUND SAMPLES
NLHF237-C-
BG
NLHF 237-C-
BG
00-05
05-10
99.05336
99.05337
1.04 ±0.12
1.09 ±0.11
ND
1. 23 ±0,93
1.130 ±0.094
1. 020 ±0.084
0.81 ± 0.39
0.88 ± 0.40
0.352 ±0.061
0.334 ±0.051
< 0.091
< 0.087
0.1 24 ±0.034
0.1 13 ±0.035
15.80 ±0.67
15.30 ±0.68
-------
TABLE A.11 - Continued
Sample ID
NLHF 237-C-
BG
NLHF 237-C-
BG
NLHF 237-C-
BG
NLHF 237-C-
DU-BG
NLHF 237-C-
DU-BG
NLHF 237-C-
DU-BG
NLHF 237-C-
DU-BG
NLHF 237-C-
DU-BG
Core
Slice
(cm)
10-15
15-28
28-41
00-05
05-10
10-15
15-25
25-36
NAREL
ID
99.05338
99.05339
99.05340
99.05355
99.05356
99.05357
99.05358
99.05359
Activity (pCi/g-dry ±
mRa
0.88 ±0.11
1. 080 ±0.084
1.12±0.12
1.02±0.13
0.797 ± 0.075
0.941 ±0.078
1.020 ±0.085
1.250 ±0.095
»»Pb
0.85 ±0.78 0.988 ±0.067
1.29 ±0.78 1.100 ±0.061
1.24 ±0.83 l.]60±0.071
1.6±1.1 0.908±0.092
0.50 ±0.66 0.770 ±0.050
0.87 ± 0,65 0.866 ± 0.053
1.00 ±0.61 1.030 ±0.057
0.88 ±0.66 1.260 ±0.058
JUBi
0.99 ±0.36
1.28 ±0.32
1.07 ±0.51
0.66 ±0.44
0.80 ± 0.29
1.08 ±0.28
0.79 ± 0.42
1.16 ±0.33
2o counting error)
1WTt
0,347 ± 0.045
0.41 7 ±0.039
0.405 ± 0.050
0.311 ±0.056
0.292 ± 0.037
0.286 ±0.036
0.383 ±0.037
0.454 ± 0.040
s»Co
< 0.068
< 0.065
< 0.062
< 0.090
< 0.059
< 0.056
< 0.056
< 0.062
l"Cs
0.1 14 ±0.030
0.077 ±0.024
ND
0.148 ±0.039
0.114 ±0.023
0.134 ±0.025
0.030 ±0.023
ND
"K
13. 10 ±0.73
15.90 ±0.65
1 5.40 ±0.76
15.00 ±0.77
12.00 ±0.54
14.00 ±0.59
14.40 ± 0,59
17.00 ±0.72
Note: "ND" indicates the radionuclide was not detected by gamma spectrometry. "< X" indicates the radionuclide was not detected and X
was the minimum detectable concentration for the nuclide in this sample. No other gamma-emitting radionuclides were detected in these
samples.
-------
TABLE A.12
Gross Alpha and Gross Beta Activity Results for
Sediment Core Samples
Sample ID
Core Slice
(cm)
NARELID
Activity
(pCi/g-dry ± 2o counting error)
Gross Alpha
Gross Beta
STUDY SAMPLES
NLHF 025-C
NLHF 025-C
NLHF 025-C
NLHF 025-C
NLHF 025-C
NLHF 028-C
NLHF 028-C
NLHF 028-C
NLHF 028-C
NLHF 028-C
NLHF 032-C
NLHF 032-C
NLHF 032-C
NLHF 032-C
NLHF 032-C
NLHF 034-C
NLHF 034-C
NLHF 034-C
NLHF 034-C
00-05
05-10
10-15
15-34
34-53
00-05
05-10
10-15
15-31
31-48
00-05
05-10
10-15
15-34
34-53
00-05
05-10
10-15
15-33
99.07514
99.07515
99.07516
99.07517
99.07518
99.07479
99.07480
99.07481
99.07482
99.07483
99.07499
99.07500
99.07501
99.07502
99.07503
99.07509
99.07510
99.07511
99.07512
13.0 ±7.2
3.3 ±6.6
9.7 ± 6.3
12.2 ±7.4
11.2 ±6.9
8.9 ±6.5
10.6 ± 7.5
8.3 ± 7.0
10.1 ±6.8
10.4 ±6.8
10.0 ±6.5
6.2 ±6.1
10.6 ±6.8
8.9 ± 7.0
5.6 ±6.1
6.5 ±5.8
10.3 ±7.2
12.5 ±7.9
13.5 ±6.8
28.1 ±5.4
29.9 ± 5.6
28.8 ±5.3
29.7 ± 5.4
30.5 ±5.1
26.2 ±5.1
28.3 ± 5.4
31.6±5.7
25.4 ±4.8
27.4 ±5.0
29.1 ±4.9
31.1 ±5.0
30.6 ±5.1
32.0 ±5.6
33 .4 ±5.6
26.3 ± 5.2
33.7 ±5.7
27.6 ±5.6
31.1±5.5
102
-------
TABLE A.12 - Continued
Sample ID
NLHF 034-C
NLHF 039-C
NLHF 039-C
NLHF 039-C
NLHF 039-C
NLHF 039-C
NLHF 047-C
NLHF 047-C
NLHF 047-C
NLHF 047-C
NLHF 047-C
NLHF 048-C
NLHF 048-C
NLHF 048-C
NLHF 048-C
NLHF 048-C
NLHF 050-C
NLHF 050-C
I NLHF 050-C
1
NLHF 050-C
NLHF 050-C
.
NLHF051-C
Core Slice
(cm)
33-52
00-05
05-10
10-15
15-28
28-42
00-05
05-10
10-15
15-24
24-33
00-05
05-10
10-15
15-34
34-53
00-05
05-10
10-15
15-33
33-52
00-05
NARELID
99.07513
99.07524
99.07525
99.07526
99.07527
99.07528
99.07494
99.07495
99.07496
99.07497
99.07498
99.07489
99.07490
99.07491
99.07492
99.07493
99.07469
99.07470
99.07471
99.07472
99.07473
99.07504
Activity
(pCi/g-dry ± 2o counting error)
Gross Alpha
4.4 ± 6.3
11.5 ±6.8
15.5 ±7.5
10.5 ±6.6
9.8 ± 6.7
14.5 ± 7.4
10.7 ±6.9
8.1 ±6.3
16.8 ±7.6
8.3 ± 6.4
11.2 ±6.9
13.3 ±7.0
9.5 ± 6.7
11.0 ±6.7
20.6 ±8.0
10.6 ±6.6
12.4 ±6.9
6.9 ±6.1
15.8 ±7.7
12.4 ±6.8
9.2 ± 6.4
7.7 ±7.3
Gross Beta
30.1 ±5.4
26.5 ± 4.8
26.9 ±4.9
28.9 ±4.9
19.6 ±5.1
31.6±5.5
27.2 ±4.9
30.0 ±4.9
27.5 ±4.9
26.5 ± 4.8
28.2 ± 5.0
30.2 ±4.9
26.1 ±4.8
27.0 ±4.8
24.2 ± 4.8
29.3 ± 4.9
31.6±5.0
29.8 ±4.9
27.9 ±5.0
32.5 ±5.1
30.6 ±4.9
25.9 ±5.5
103
-------
TABLE A.12 - Continued
Sample ID
NLHF 051-C
NLHF051-C
NLHF 051-C
NLHF 051-C
NLHF 056-C
NLHF 056-C
NLHF 056-C
NLHF 056-C
NLHF 056-C
NLHF 062-C
NLHF 062-C
NLHF 062-C
NLHF 062-C
NLHF 062-C
NLHF 064-C
NLHF064-C
NLHF 064-C
NLHF 064-C
NLHF 064-C
NLHF 066-C
NLHF 066-C
NLHF 066-C
Core Slice
(cm)
05-10
10-15
15-33
33-52
00-05
05-10
10-15
15-31
31-48
00-05
05-10
10-15
15-30
30-50
00-05
05-10
10-15
15-25
25-35
00-05
05-10
10-15
NARELID
99.07505
99.07506
99.07507
99.07508
99.07519
99.07520
99.07521
99.07522
99.07523
99.05262
99.05263
99.05264
99.05265
99.05266
99.05267
99.05268
99.05269
99.05270
99.05271
99.07484
99.07485
99.07486
Activity
(pCi/g-dry ± 20 counting error)
Gross Alpha
9.3 ± 6.2
7.8 ±6.8
8.9 ±6.6
7.2 ± 7.2
6.7 ±6.1
14.9 ± 7.4
12.6 ±7.1
10.0 ±6.5
4.8 ±5.9
16.1 ±7.5
15.5 ±7.3
10.2 ±6.8
9.0 ± 6.4
13.7 ±7.2
13.1 ±7.0
11.2 ±7.0
9.1 ±6.7
16.4 ±7,6
7.3 ± 6.4
14.0 ±7.2
10.6 ± 6.6
14.0 ± 7.3
Gross Beta
27.2 ± 5.3
34.3 ± 5.6
27.5 ± 5.3
22.9 ±5.3
27.2 ±4.8
30.4 ±5.1
21. 9 ±4.6
28.2 ±4.8
29.4 ± 4.9
29.4 ± 5.0
28.1 ±4.9
28.8 ±5.0
24.1 ±4.7
24.1 ±4.7
29.1 ±4.9
29.2 ± 5.0
30.1 ±5.1
33.7 ±5.2
31.9±5.1
29.8 ± 5.0
31.4 ±5.0
28.2 ± 5.0
104
-------
TABLE A.12 - Continued
Sample ID
NLHF 066-C
NLHF 066-C
NLHF074-C
NLHF 074-C
NLHF 074-C
NLHF 074-C
NLHF 074-C
NLHF 079-C
NLHF 079-C
NLHF 079-C
NLHF 079-C
NLHF 079-C
NLHF 082-C
NLHF 082-C
NLHF 082-C
NLHF 082-C
NLHF 082-C
_
NLHF 1 16-C
NLHF116-C
NLHF 1 16-C
NLHF 1 16-C
NLHF 1 16-C
— —
Core Slice
(cm)
15-27
27-39
00-05
05-10
10-15
15-34
34-53
00-05
05-10
10-15
15-33
33-51
00-05
05-10
10-15
15-33
33-51
.
00-05
05-10
10-15
15-30
30-53
. —
NARELID
99.07487
99.07488
99.07529
99.07530
99.07531
99.07532
99.07533
99.07474
99.07475
99.07476
99.07477
99.07478
99.05350
Activity
(pCi/g-dry ± 2o
Gross Alpha
12.9 ±7.0
13.9 ±7.2
11.1±7.1
7.9 ±6.5
7.8 ± 6.4
11.2 ±6.9
9.1 ±6.8
8.8 ±7.1
5.6 ± 6.0
9.6 ±7.4
12.1 ±6.9
16.1 ±8.1
8.9 ±6.4
99.05351 10.2 ±6.8
99.05352 15.6 ±7.3
99.05353
99.05354
• —
99.05242
99.05243
99.05244
99.05245
99.05246
12.4 ±7.1
11.2 ±6.8
8.9 ±6.6
5.6 ±6.0
15.1 ±7.5
11.7 ±6.9
8.4 ±6.5
counting error)
Gross Beta
32.2 ±5.1
31.4±5.1
27.4 ±5.4
30.6 ±5.5
26.4 ± 5.4
30.2 ± 5.4
3 1.6 ±5.6
31.7±5.8
32.6 ±5.4
25.6 ± 5.3
32.3 ± 5.7
28.4 ± 5.6
29.4 ± 4.8
24.6 ±4.7
28.5 ± 4.9
25.0 ±4.7
25.3 ± 4.6
27.9 ±4.9
25.8 ± 4.7
25.4 ± 4.8
31.7 ±5.0
26.8 ±4.8
105
-------
TABLE A.12 - Continued
Sample ID
NLHF117-C
NLHF117-C
NLHF117-C
NLHF117-C
NLHF117-C
NLHF117-C-DU
NLHF117-C-DU
NLHF117-C-DU
NLHF117-C-DU
NLHF117-C-DU
NLHF 122-C
NLHF 122-C
NLHF 122-C
NLHF 122-C
NLHF131-C
NLHF131-C
NLHF 131-C
NLHF 131-C
NLHF 131-C
NLHF 165-C
NLHF 165-C
NLHF 165-C
Core Slice
(cm)
00-05
05-10
10-15
15-24
24-34
00-05
05-10
10-15
15-30
30-45
00-05
05-10
10-15
15-25
00-05
05-10
10-15
15-28
28-42
00-05
05-10
10-15
NARELID
99.05341
99.05342
99.05343
99.05344
99.05345
99.05331
99.05332
99.05333
99.05334
99.05335
99.05346
99.05347
99.05348
99.05349
99.05326
99.05327
99.05328
99.05329
99.05330
99.05229
99.05230
99.05231
Activity
(pCi/g-dry ± 2o counting error)
Gross Alpha
4.7 ± 6.4
7.8 ± 6.2
6.3 ± 6.3
6.8 ±6.1
6.2 ± 6.2
8.6 ± 6.6
8.9 ± 6.6
5.3 ± 6.1
7.1 ±6.1
11.8 ±6.9
7.1 ± 6.2
8.7 ±6.6
14.2 ±7.1
9.0 ± 6.6
10.3 ±6.6
11.5 ±7.0
8.4 ± 6.5
8.7 ±6.6
10.8 ±6.7
7.2 ± 6.3
4.7±5.9
12.5 ±7.0
Gross Beta
27.5 ±5.3
20.4 ±5.1
20.6 ± 4.5
27.1 ±4.8
27.5 ±4.8
27.0 ± 4.9
29.0 ± 4.9
27.1 ±4.8
30 .3 ± 4.9
32,1 ±5.7
35.9 ±5.2
24.3 ± 4.7
30.8 ±5.0
28.9 ± 4.9
25.6 ±4.7
29.7 ±5.1
31.0 ±5.0
29.4 ±5.0
27.5 ± 4.8
27.6 ±4.9
27.0 ± 4.7
29.7 ±5.0
106
-------
TABLE A.12 - Continued
1
Sample ID
NLHF 165-C
NLHF 176-C
NLHF 176-C
NLHF 176-C
NLHF 176-C
NLHF 176-C
NLHF180-C
NLHF 180-C
NLHF 180-C
NLHF 180-C
NLHF 180-C
NLHF 192-C
NLHF 192-C
NLHF 192-C
NLHF 192-C
NLHF 192-C
NLHF 193-C
NLHF 193-C
NLHF 193-C
NLHF 193-C
NLHF 193-C
NLHF201-C
Core Slice
(cm)
15-35
00-05
05-10
10-15
15-30
30-53
00-05
05-10
10-15
15-30
30-46
00-05
05-10
10-15
15-27
27-39
00-05
05-10
10-15
15-30
30-52
00-05
NAREL ID
99.05232
99.05257
99.05258
99.05259
99.05260
99.05261
99.05233
99.05234
99.05235
99.05236
99.05237
99.05252
99.05253
99.05254
99.05255
99.05256
99.05247
99.05248
99.05249
99.05250
99.05251
99.05360
Activity
(pCi/g-dry ± 2o counting error)
Gross Alpha
11.5 ±6.7
10.2 ±6.8
8.6 ±6.4
13.2 ±7.1
15.5 ±7.3
13.2 ±7.0
7.2 ± 6.3
9.3 ± 6.5
12.4 ±7.0
11.4 ±6.7
13.7 ±7.4
11.1 ±6.8
6.3 ± 8.0
11.3 ±7.3
10.0 ±7.3
12.6 ±7.0
7.9 ±6.3
11.2 ±7.0
10.3 ±8.6
9.3 ±7.1
8.7 ±7.2
13.3 ± 7.0
Gross Beta
28.3 ± 4.9
25.7 ±4.8
28.2 ± 4.9
31.1±5.1
30.3 ±5.0
27.5 ± 4.8
26.0 ± 4.8
30.3 ± 4.9
23.8 ±4.7
22.5 ± 4.5
25.8 ± 4.9
28.6 ±5.5
21.7±5.5
28.2 ± 5.5
24.5 ± 5.5
30.8 ± 5.6
25.5 ± 4.7
27.6 ±4.9
29.4 ± 5.9
29.7 ±5.5
26.3 ± 5.7
30.9 ±5.0
107
-------
TABLE A.12 - Continued
Sample ID
NLHF201-C
NLHF 201-C
NLHF201-C
NLHF 201-C
NLHF 205-C
NLHF 205-C
NLHF 205-C
NLHF 205-C
NLHF221-C
NLHF 221-C
NLHF221-C
NLHF 221-C
NLHF 221-C
Core Slice
(cm)
05-10
10-15
15-25
25-36
00-05
05-10
10-15
15-36
00-05
05-10
10-15
15-33
33-52
NARELID
99.05361
99.05362
99.05363
99.05364
99.05238
99.05239
99.05240
99.05241
99.05365
99.05366
99.05367
99.05368
99.05369
Activity
(pCi/g-dry ± 2a counting error)
Gross Alpha
8.0 ± 6.3
7.7 ±6.5
9.0 ±6.8
4.5 ±5.8
11.3 ±6.9
12.4±7.1
6.1 ±6.1
8.9 ±6.5
11.6 ±6.8
9.9 ± 6.9
10.1 ±6.5
7.8 ±6.3
5.0 ±6.1
Gross Beta
32.3 ± 5.0
28.5 ± 4.9
27.1 ± 5.0
26.4 ±4.8
23.0 ± 4.6
20.5 ± 4.6
22.8 ±4.6
21. 5 ±4.5
23.8 ± 4.6
25.6 ± 4.8
26.1 ±4.7
27.6 ±4.8
20.8 ± 4.5
BACKGROUND SAMPLES
NLHF 237-C-BG
NLHF 237-C-BG
NLHF 237-C-BG
NLHF 237-C-BG
NLHF 237-C-BG
NLHF 237-C-DU-BG
NLHF 237-C-DU-BG
NLHF 237-C-DU-BG
00-05
05-10
10-15
15-28
28-41
00-05
05-10
10-15
99.05336
99.05337
99.05338
99.05339
99.05340
99.05355
99.05356
99.05357
9.8 ±7.1
IO.I±6.7
9.3 ± 7.0
10.2 ±6.6
12.6 ± 7.5
8.8 ± 6.7
10.0 ±6.6
8.1 ±6.5
22.4 ± 5.2
25.9 ±5.0
25.8 ±5.2
29.2 ± 5.5
26.8 ± 5.4
27.6 ± 4.9
26.0 ±4.7
24.8 ±4.7
108
-------
TABLE A,12 - Continued
Sample ID
NLHF237-C-DU-BG
NLHF 237-C-DU-BG
Core Slice
(cm)
15-25
25-36
NARELID
99.05358
99.05359
Activity
(pCl/g-dry ± 2o counting error)
Gross Alpha Gross Beta
12.2 ±6.9 24.0 ±4.6
11.7±7.1 23.6±4.7
109
-------
TABLE A.13
Gamma Spectrometry Results for Biota Samples
Uranium and Actinium Decay Chains
Sample ID
NAREL
ID
Activity (pCi/g-wet ± 2o
^Th
^-Pa
H*Ra
214Pb
2HBi
counting error)
IMRa
mPb
'"Bi
IMT1
STUDY SAMPLES
NLHFOOS-BM
NLHF008-BSF
NLHFQ27-BSF
NLHF037-BBK.
NLHF041-BM
NLHF065-BM
NLHF073-BB
NLHF 083-BBK
NLHFI04-BBK
NLHF 104-BM
NLHFU3-BBK
NLHF 133-BM
NLHF170-BSH
NLHF 193-BB
NLHF 197-BM
NLHF 197-BSF
NLHF214-BM
NLHF218-BB
NLHF218-BB-DU
99.05511
99.05513
99.05504
99.05509
99.05499
99.05225
99.0550!
99.05502
99.05512
99.05510
99.05507
99.05508
99.05500
99.05226
99.05224
99.05227
99.05503
99.05505
99.05506
ND
ND
KD
ND
ND
0.172 ±0.052
0.087 i 0.050
ND
0.119±0.059
ND
ND
ND
ND
ND
ND
ND
0.066 ±0.020
0.1 56 ±0.025
0.108*0.020
ND
ND
ND
ND
ND
ND
0.45 ±0.22
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.055 ±0.057
0,127 ±0.089
0.058 ±0.053
ND
ND
ND
0.074 ± 0.069
0.079 ± 0.075
ND
0.057 ± 0.064
ND
ND
0.16 ±0.1 1
ND
ND
ND
0,055 ±0.037
O.I 36 ±0.043
0,1 07 ±0.042
0.0153 ±0.0043
ND
ND
ND
ND
0.0118 ±0.0041
0.0320 ± 0.0052
ND
0,0192±0.0074
0.0189 i 0.0051
ND
ND
0.0268 ±0.0098
0.0290 ±0.0039
ND
0.0064 ±0.0060
ND
0.0354 ±0.0039
0.0292 ±0.0036
0.018] ±0.0041
0.0066 ±0.0079
ND
0.0175*0.0083
ND
0.01 IS ±0.0034
0.0266*0.0055
ND
0.0201 ± 0,0072
0.0226 ± 0.0049
ND
0.0080 ±0,0033
0,0235 ±0.0089
0.0365 ±0.0037
0.0127 ±0.0034
ND
ND
0.0289 ±0,0035
0.0265 ±0,0033
0.0290 ± 0.0053
ND
ND
0.053 ±0.014
ND
ND
0.1 050 ±0.0074
0.094 ±0.0 13
0.054 ±0.011
ND
0.041 ±0.012
ND
0.225 ±0.01 7
0.0745 ±0.0056
ND
ND
ND
0.1 160 ±0.0053
0.0901 ±0.0047
0.0227 ± 0.0046
0.0129 ±0.0079
0.0066 ± 0.0035
0.032 ± 0.010
0.0064 ±0.0037
0.0156 ±0.0045
0.0122 ±0.0050
0.01 83 ±0.0086
0.0320 ± 0.0076
0.0240 ± 0.0054
ND
0.0075 ±0.0037
0.0542 ± 0.0094
0.0205 ± 0.0047
0.0069 ±0.0038
0.0 120 ±0.0063
0.0101 ±0.0025
0.0338 ± 0.0033
0.0288 ±0.0030
0.026 ±0.021
ND
ND
ND
ND
ND
0,021 ±0.024
ND
ND
ND
ND
ND
0.080 ±0.064
ND
ND
0.027 ± 0.037
ND
0.035 ± 0.019
0.019 ±0.020
0.0075 ±0.0022
0.0039 ±0.0041
0.0016 ±0.0017
0.0092 * 0.0049
ND
0.0046 ±0.0018
0.0030 ±0.0029
0.0032 ± 0.0045
0.0093 ± 0.0039
0.0073 ±0.0026
0.0046 ± 0.0047
0.0024 ±0.0018
0.0160 ±0.0051
0.0076*0.0018
0.0025 ±0.0021
ND
0.0032 ±0.0015
0.01 23 ±0,0017
0.0081 ±0.0015
-------
TABLE A.13 - Continued
c . ._ NAREL
Sample ID
NLHF236-BMG 99.05325
NLHF 244-BMG 99.05324
Activity (pCi/g-wet ±
«4Th ^^ >«Ra ZUpb
ND ND ND ND
ND ND ND ND
»
-------
TABLE A.14
Gamma Spectrometry Results for Biota Samples
Other Gamma Emitting Radionuclides
Sample ID
NAREL ID
Activity (pCi/g-wet ± 2o counting error)
7Be
"Co
"'Cs
131,
WK
STUDY SAMPLES
NLHF 008-BM
NLHF008-BSF
NLHF 027-BSF
NLHF037-BBK
NLHF 041-BM
NLHF 065-BM
NLHF 073-BB
NLHF 083-BBK
NLHF 104-BBK
NLHF104-BM
NLHF133-BBK
NLHF 133-BM
NLHF 170-BSH
NLHF 193-BB
NLHF 197-BM
99.05511
99.05513
99.05504
99.05509
99.05499
99.05225
99.05501
99.05502
99.05512
99.05510
99.05507
99.05508
99.05500
99.05226
99.05224
0.041 ± 0.017
ND
ND
0.088 ±0.031
0.03 5 ±0.0 14
0.148 ±0.018
0.164 ±0.019
0,319 ±0.036
0.081 ±0.025
0.057 ± 0.020
0.035 ± 0.034
0.024 ±0.0 17
0.409 ±0.043
0.31 8 ±0.022
0.083 ±0.018
< 0.004
< 0.007
< 0.003
< 0.009
< 0.005
< 0.003
< 0.004
< 0.009
< 0.008
< 0.005
<0.010
< 0.004
< 0.011
< 0.003
< 0.004
ND
ND
ND
0.0039 ± 0.0041
ND
ND
ND
0.0058 ± 0.0036
0.0046 ± 0.0039
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.0412 ±0.0072
ND
0.0053 ± 0.0037
ND
0.0372 ± 0.0082
0.1 000 ±0.0082
0.009 1 ±0.0046
0.1070 ±0,0094
0.0055 ± 0.0033
ND
0.0046 ±0.0040
ND
1.440 ±0.048
1.140 ±0.070
1.390 ±0.045
7.47 ±0.1 8
0.892 ± 0.039
0.952 ±0.03 8
0,600 ± 0.042
6.14±0.15
6.67 ±0.14
0.898 ± 0.043
7.67 ±0.17
1.010 ±0.040
12.80 ±0.22
0.735 ±0.033
0.850 ±0.039
-------
TABLE A.14 - Continued
Sample ID
NLHF 197-BSF
NLHF 214-BM
NLHF218-BB
NLHF218-BB-DU
NLHF 236-BMG
NLHF 244-BMG
NAREL ID
99.05227
99,05503
99.05505
99.05506
99.05325
99,05324
Activity (pCi/g-wet ± 2o counting error)
7Be
ND
0.067 ±0.0 12
0.8 14 ±0.026
0.704 ± 0.024
0.548 ± 0.039
0.690 ±0.03 8
"Co
< 0.006
< 0.004
< 0.003
< 0.003
< 0.007
< 0.005
IJ7Cs
ND
ND
0.0039 ±0.0017
0.0026 ±0.00 14
ND
ND
Ulj
ND
ND
0.0120 ±0.0031
0.0086 ± 0.0027
0.0087 ± 0.0044
ND
40K
1.100 ±0.062
0.856 ± 0.035
0.582 ± 0.029
0.493 ± 0.026
2.320 ± 0.079
2.720 ± 0.082
BACKGROUND SAMPLES
NLHF234-BMG-BG
99.05228
0.1 90 ±0.031
< 0.007
ND
ND
2.570 ± 0.086
Note: "ND" indicates the radionuclide was not detected by gamma spectrometry. "< X" indicates the radionuclide was not detected and
X was the minimum detectable concentration for the nuclide in this sample. No other gamma-emitting radionuclides were detected in these
samples.
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TABLE A.15
Gross Alpha and Gross Beta Activity Results for Biota Samples
Sample ID
NARELID
Activity
(pCi/g-wet ± 2a counting error)
Gross Alpha
Gross Beta
STUDY SAMPLES
NLHF 008-BM
NLHF008-BSF
NLHF 027-BSF
NLHF 037-BBK
NLHF041-BM
NLHF 065-BM
NLHF 073-BB
NLHF 083-BBK
NLHF 104-BBK
NLHF 104-BM
NLHF 133-BBK
NLHF 133-BM
NLHF 170-BSH
NLHF 193-BB
NLHF 197-BM
NLHF 197-BSF
NLHF214-BM
NLHF218-BB
NLHF218-BB-DU
NLHF 236-BMG
NLHF 244-BMG
99.05511
99.05513
99.05504
99.05509
99.05499
99.05225
99.05501
99.05502
99.05512
99.05510
99.05507
99.05508
99.05500
99.05226
99.05224
99.05227
99.05503
99.05505
99.05506
99.05325
99.05324
0.03 ± 0.77
0.52 ± 0.46
0.56 ± 0.44
0.29 ±0.20
-0.04 ±0.3 8
0.68 ± 0.70
0.4 ±1.0
0.17 ±0.10
0.37 ± 0.20
0.06 ± 0.67
0.16 ±0.12
-0.44 ±0.51
0.96 ± 0.30
0.50 ± 0.73
0.26 ± 0.76
0.20 ±0.31
0.32 ± 0.77
1.3 ±1.1
0.70 ± 0.67
0.1 36 ±0.076
0.019 ± 0.059
1.70 ±0.98
2.69 ±0.61
3. 82 ±0.66
10.17 ±0.58
1.42 ±0.92
1.73 ±0.86
0.5 ±1.2
5.77 ±0.32
8.61 ±0.51
2.1 ±1.2
8.44 ± 0.41
0.8 ±1.1
11. 76 ±0.60
1.61 ±0.87
1.2 ±1.0
2.01 ± 0.47
0.80 ± 0.98
1.52 ±0.94
1.41 ±0.74
2.40 ±0.17
3. 04 ±0.21
BACKGROUND SAMPLES
NLHF 234-BMG-BG
99.05228
0.1 19 ±0.084
2.76 ±0.20
114
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