ML14323A663
| ML14323A663 | |
| Person / Time | |
|---|---|
| Site: | Salem, Hope Creek  |
| Issue date: | 11/19/2014 |
| From: | Public Service Enterprise Group |
| To: | Office of Nuclear Reactor Regulation |
| Shared Package | |
| ML14323A662 | List: |
| References | |
| LR-N14-0231 | |
| Download: ML14323A663 (118) | |
Text
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM PSEG Nuclear LLC, SALEM and HOPE CREEK GENERATING STATIONS 2013 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT Revision 1 JANUARY 1 TO DECEMBER 31, 2013
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TABLE OF CONTENTS I. Summary............................................................................................................................ 1 II. The Radiological Environmental Monitoring Program...................................................... 5 A. Objectives of the Operational REMP.................................................................... 6 B. Implementation of the Objectives.......................................................................... 6 III. Program Description........................................................................................................ 7 A. Data Interpretation................................................................................................. 7 B. Program Exceptions.............................................................................................. 9 C. Program Changes............................................................................................... 11 D. Quality Assurance Program................................................................................ 12 E. Summary of Results: Inter-laboratory Comparison Program............................ 12 IV. Results and Discussion................................................................................................. 16 A. Atmospheric......................................................................................................... 17
- 1. Air Particulates.......................................................................................... 17
- 2. Air Iodine................................................................................................... 18 B. Direct Radiation................................................................................................... 18 C. Terrestrial............................................................................................................ 20
- 1. Milk............................................................................................................ 21
- 2. Well Water (Ground Water)...................................................................... 22
- 3. Potable Water (Drinking Water)............................................................... 23
- 4. Vegetables................................................................................................ 25
- 5. Fodder Crops............................................................................................ 26
- 6. Soil............................................................................................................ 27
- 7. Beef and Game........................................................................................ 28 D. Aquatic................................................................................................................. 29
- 1. Surface Water........................................................................................... 30
- 2. Fish........................................................................................................... 32
- 3. Blue Crab.................................................................................................. 33
- 4. Sediment................................................................................................... 33 E. Land Use Survey................................................................................................. 34 V. Annotations to Previous AREOR................................................................................... 35 VI. Hope Creek Technical Specification Limit for Primary Water Iodine Concentrations.. 36 VII. Conclusions.................................................................................................................. 36 VIII. References................................................................................................................... 37
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TABLE OF CONTENTS (contd)
Appendix A - Program Summary....................................................................................... A-1 Appendix B - Sample Designation and Locations............................................................. B-1 Appendix C - Data Tables................................................................................................. C-1 Appendix D - Summary of Interlaboratory Comparison Program Results from Eckert &
Ziegler Analytics (EZA), Environmental Resource Associates (ERA) and Department of Energy (DOE) Mixed Analyte Performance Evaluation Program (MAPEP)....................................................................................... D-1
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LIST OF TABLES Table B-1 Sampling Locations................................................................................. B-4 Table B-2 Salem and Hope Creek Generating Stations Radiological Environmental Monitoring Program......................................................... B-8 Table C-1 Concentrations of Gamma Emitters in Quarterly Composites of Air Particulates, 2013.................................................................................... C-3 Table C-2 Concentrations of Gross Beta Emitters in Air Particulates, 2013............. C-5 Table C-3 Concentrations of Iodine-131 in Filtered Air, 2013................................... C-7 Table C-4 Direct Radiation Measurements - Quarterly Dosimetry Results, 2013.... C-9 Table C-5 Concentrations of Iodine-131 and Gamma Emitters in Milk, 2013........... C-10 Table C-6 Concentrations of Gross Alpha and Gross Beta Emitters and Tritium in Well Water, 2013...................................................................... C-12 Table C-7 Concentrations of Gamma Emitters in Well Water, 2013......................... C-13 Table C-8 Concentrations of Gross Alpha and Gross Beta Emitters and Tritium in Raw and Treated Potable Water (2F3), 2013........................... C-14 Table C-9 Concentrations of Iodine-131 and Gamma Emitters in Raw and Treated Potable Water (2F3), 2013......................................................... C-15 Table C-10 Concentrations of Gamma Emitters in Vegetables, 2013........................ C-16 Table C-11 Concentrations of Gamma Emitters in Fodder Crops, 2013.................... C-18 Table C-12 Concentrations of Gamma Emitters in Soil, 2013.................................... C-19 Table C-13 Concentrations of Gamma Emitters in Beef and Game, 2013................. C-20
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LIST OF TABLES (contd)
Table C-14 Concentrations of Gross Beta Emitters in Surface Water, 2013.............. C-21 Table C-15 Concentrations of Tritium in Surface Water, 2013................................... C-22 Table C-16 Concentrations of Gamma Emitters in Surface Water, 2013................... C-23 Table C-17 Concentrations of Gamma Emitters in Edible Fish, 2013......................... C-26 Table C-18 Concentrations of Gamma Emitters in Crabs, 2013................................. C-27 Table C-19 Concentrations of Gamma Emitters in Sediment, 2013........................... C-28 Table D-1 EZA Environmental Radioactivity Cross Check Program Teledyne Brown Engineering, 2013......................................................................... D-3 Table D-2 DOEs Mixed Analyte Performance Evaluation Program (MAPEP)
Teledyne Brown Engineering, 2013......................................................... D-6 Table D-3 ERA Environmental Radioactivity Cross Check Program Teledyne Brown Engineering, 2013......................................................................... D-7 LIST OF MAPS Map B-1 Salem and Hope Creek Generating Stations Radiological Environmental Monitoring Program On-Site Sampling Locations............ B-13 Map B-2 Salem and Hope Creek Generating Stations Radiological Environmental Monitoring Program Off-Site Sampling Locations............ B-14 LIST OF FIGURES Figure 1 Gross Beta Activity in Air Particulates 1990 through 2013....................... C-29
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LIST OF FIGURES (contd)
Figure 2 Iodine-131 Activity in Milk 1990 through 2013......................................... C-30 Figure 3 Gross Beta Activity in Surface Water 1990 through 2013........................ C-31 Figure 4 Tritium Activity in Surface Water 1990 through 2013............................... C-32 Figure 5 Cesium-137 and Co-60 Activity in Aquatic Sediment 1990 through 2013......................................................................................................... C-33 Figure 6 Cesium-137 Activity in Soil 1974 through 2013 (Triennial)...................... C-34
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LIST OF ACRONYMS OR TERMS USED IN THIS TEXT (in alphabetical order)
AREOR Annual Radiological Environmental Operating Report percent A
Acceptable a posteriori a posteriori - The terms a posteriori ("from the later") and a priori ("from the earlier") are used to distinguish two types of knowledge, justification, or argument a priori a priori - The terms a priori ("from the earlier") and a posteriori ("from the later") are used to distinguish two types of knowledge, justification, or argument AIO Air Iodine analyte the substance being identified and measured in a chemical analysis APT Air Particulates BaLa-140 BariumLathanum-140 Be-7 Beryllium-7 Bq Bequerels C
Control Co-57 Colbalt-57 Co-60 Colbalt-60 Cs-134 Cesium-134 Cs-137 Cesium-137 DOE Department of Energy dpm Dissintergrations per minute ECH Crabs ERA Environmental Resource Associates ESF Fish ESS Sediment Eu-152 Europium-152 EZA Eckert & Ziegler Analytics, Inc.
Fe-59 Iron-59 FPL Broad Leafy Vegetation FPV Vegetables GAM Game GEL GEL Laboratories Gr-A Gross Alpha Gr-B Gross Beta H-3 Tritium HCGS Hope Creek Generating Station I-131 Iodine-131 IDM Immersion Dose Monitor ISFSI Independent Spent Fuel Storage Installation K-40 Potassium-40 kg kilogram L
Liter
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LLD Lower Limit of Detection LTS Laboratory Testing Services m3 cubic meter MAPEP Mixed Analyte Performance Evaluation Program MDC Minimum Detectable Concentration mL Milliliter MLK Milk Mn-54 Manganese -54 mR milliRoentgen - a unit of radiation, used to measure the exposure of somebody or something to X-rays and gamma rays, defined in terms of the ionization effect on air.
mrem millirem - a unit for measuring amounts of radiation, equal to the effect that one roentgen of X-rays or gamma-rays would produce in a human being. It is used in radiation protection and monitoring.
MWe Megawatt Electric MWt Megawatt Thermal N
Not Acceptable NCR Noncomformance Report NEI Nuclear Energy Institute NELAC National Environmental Laboratory Conference NRC U.S. Nuclear Regulatory Commission ODCM Offsite Dose Calculation Manual pCi Picocuries PE Performance Evaluation PSEG Public Service Enterprise Group PT Performance Testing PWR Potable (drinking) Water - Raw PWT Potable (drinking) Water PWT Potable (drinking) Water - Treated QA Quality Assurance Ra-226 Radium - 226 REMP Radiological Environmental Monitoring Program RGPP Radiological Groundwater Protection Program SA Salem SAR Safety Analysis Report SGS Salem Generating Station SOL Soil SOP Standard Operating Procedures Sr-89 Strontium - 89 Sr-90 Strontium - 90 Std. Qtr.
Standard Quarter = 92 days SWA Surface Water TBE Teledyne Brown Engineering
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TEDA Triethylene-diamine Th-232 Thorium-232 TLD Thermoluminescent Dosimeter - A TLD measures ionizing radiation exposure by measuring the intensity of visible light emitted from a crystal in the detector when the crystal is heated. The intensity of light emitted is dependent upon the radiation exposure.
TS Technical Specifications uCi Microcuries USEPA United States Environmental Protection Agency VGT Fodder Crops W
Warning WWA Ground (well) Water Zn-65 Zinc-65 ZrNb-95 ZirconiumNiobium-95
I.
Summary During normal operations of a nuclear power generating station there are permitted releases of small amounts of radioactive material to the environment. To monitor and determine the effects of these releases, a Radiological Environmental Monitoring Program (REMP) has been established for the PSEG Nuclear LLC, Salem Generating Station (SGS) and Hope Creek Generating Station (HCGS). The results of the REMP are published annually, providing a summary and interpretation of the data collected.
Public Service Enterprise Groups (PSEG) Laboratory & Testing Services (LTS) was responsible for the collection of environmental samples during 2013. Teledyne Brown Engineering (TBE) performed the analysis of environmental samples during 2013. Duplicate samples for laboratory quality assurance (QA) were sent to GEL Laboratories. Mirion Technologies provided the dosimetry services.
The REMP is based on NRC guidance as reflected in the SGSs and HCGSs Offsite Dose Calculation Manual (ODCM), with regards to sample media, sampling locations, sampling frequency and analytical sensitivity requirements. Indicator and control locations were established for comparison purposes to distinguish radioactivity of plant origin from natural or other "man-made" environmental radioactivity. The environmental monitoring program also verifies projected and anticipated radionuclide concentrations in the environment and related exposures from releases of radionuclides from SGS and HCGS. This program satisfies the requirements of Section IV.B.2 of Appendix I to 10 CFR 50 and provides surveillance of all appropriate critical exposure pathways to man.
The detection capabilities, required by the SGSs and HCGSs ODCM, were achieved for the 2013 reporting period, with minor exceptions as described in
this report. Exceptions to the program are noted and the PSEG corrective action identifier was included in parenthesis. The data that were collected in 2013 demonstrates that both SGS and HCGS were operated in compliance with each plants respective Technical Specifications and ODCMs. The REMP objectives were also met.
Most of the radioactive materials noted in this report are either naturally occurring in the environment such as potassium (K) 40 or beryllium (Be) 7, or a result of non-nuclear generating station activity, such as atmospheric nuclear weapons testing or medical wastes. Measurements made in the vicinity of SGS and HCGS were compared to background or control measurements and the preoperational REMP study performed before SGS Unit 1 became operational.
Samples of air particulates, air iodine, milk, surface, ground (well) water and potable (drinking) water, vegetables, fodder crops, soil, fish, crabs and sediment were collected and analyzed. External radiation dose measurements were also made in the vicinity of SGS/HCGS using passive dosimeters.
The REMP complies with the following Stations SAR document sections:
Unit Technical Specifications ODCM SGS U1 6.8.4.h 3/4. 12.1 6.9.1.7 SGS U2 6.8.4.h 3/4. 12.1 6.9.1.7 HCGS U1 6.8.4.h 3/4. 12.1 6.9.1.6 To demonstrate this compliance samples obtained from various media were analyzed for one or more of the following: gamma emitting isotopes, tritium (H-3), iodine-131 (I-131), gross alpha, gross beta and immersion dose. The results of these analyses were used to assess the environmental impact of
SGS and HCGS operations, thereby demonstrating compliance with the respective SGSs and HCGSs Technical Specifications and ODCMs and the applicable Federal regulations.
There were a total of 1623 analyses on 1288 environmental samples during 2013. Of the total number of analyses and environmental samples, direct radiation dose measurements were made using 218 sets of direct reading dosimeters.
In addition to the naturally occurring isotopes (i.e. Be-7, K-40, Ra-226, and Th-232), cesium-137 was detected on the vegetables in two of the on-site gardens. These broadleaf vegetation samples had low concentrations of Cs-137 (up to 19 pCi/kg), which is similar to the 2012 results from the site gardens. There were no releases of gaseous cesium from either SGS or HCGS in 2012 or 2013. Cesium-137, from the atmospheric nuclear weapons testing, is routinely found in sediment and soil samples. Soil samples taken from the gardens in January had Cs-137 that were lower to that reported in previous years. The on-site gardens are encased in small boxes to prevent animals from foraging, and, since the samples are not rinsed, the data indicate that the soil contaminated the broadleaf vegetation. The maximum bounding dose from the contamination would be 0.16 mrem assuming that an individual consumed 26 kg (57 pounds) of the vegetation.
Dose measurements are made with quarterly passive dosimeters at onsite and offsite locations around the SGS/HCGS. The direct radiation component was determined by comparing badges on the site boundary (5S1, 10S1, 11S1, 15S1and 15S2) to the designated controls (3G1 and 14G1). The range of the site boundary dosimeters, with an annual dose between 43mR and 52 mR were lower than the control locations of 57 mR and 61 mR. The direct radiation dose is determined by subtracting the control data from the badge data; therefore, there was no measurable direct radiation to a Member of the Public at the site boundary. The reason that the site badges are lower
is that the surrounding waters lower the radon concentration and limit terrestrial radiation. This was comparable to the levels prior to station operation which had an average of 55 milliroentgen per year for 1973 to 1976.
The ambient radiation levels as measured by the two site boundary locations 1S1 and 16S2 ranged from 34.3 mR/Std. Qtr. to 37 mR/Std. Qtr. The doses at these two locations were influenced by the radiation shine from the dry cask storage located in the nearby Independent Spent Fuel Storage Installation (ISFSI). The Federal Regulations 40 CFR 190 and 10 CFR 72.104 both limit the dose to a real member of the public to 25 mrem to the total body. To demonstrate compliance to these regulations, the maximum dose that a hypothetical individual member of the public was calculated at 4.7 mrem, which was well below the Federal limits for exposure.
Following the guidance in Nuclear Energy Institutes (NEI) 07-07, the results of the annual report of the Radiological Groundwater Protection Program (RGPP), formerly reported in this report, have been moved to the Annual Radiological Effluent Release Report.
The concentration of radioactive material in the environment that could be attributable to SGS and HCGS operations was only a small fraction of the concentration of naturally occurring and man-made radioactivity. The data obtained from the 2013 REMP were comparable to the results obtained during the preoperational phase of the program. Combined with historical results collected since commercial operation, it can be concluded that the levels and fluctuations were as expected and therefore, we conclude that the operation of SGS and HCGS had no significant radiological impact on the environment.
II.
The Radiological Environmental Monitoring Program Lower Alloways Creek Township, Salem County, New Jersey is the site of SGS and HCGS. SGS consists of two operating pressurized water nuclear power reactors. SGS Unit One has a net rating of 1180 megawatt electric (MWe) and SGS Unit Two has a net rating of 1178 MWe. The licensed core power for both units is 3460 megawatt thermal (MWt). HCGS is a boiling water nuclear power reactor, which has a net rating of 1216 MWe. The licensed core power is 3840 MWt.
The Generating Stations are located on a man-made peninsula on the east bank of the Delaware River. It was created by the deposition of hydraulic fill from dredging operations. The surrounding environment is characterized mainly by the Delaware River Estuary and Bay, extensive tidal marshlands, and low-lying meadowlands. These land types make up approximately 85%
of the land area within five miles of the site, with most of the remaining land used for agriculture. More specific information on the demography, hydrology, meteorology, and land use of the area may be found in the SGSs and HCGSs Environmental Reports, Environmental Statements and the Updated Final Safety Analysis Reports.
Since 1968, a radiological environmental monitoring program (REMP) has been conducted at SGS and HCGS. Starting in December 1972, a more extensive radiological monitoring program was initiated in preparation for the operation of SGS Unit 1. The operational REMP was initiated in December 1976 when SGS Unit 1 achieved criticality.
An overview of the 2013 REMP is provided in Table B-2, Salem and Hope Creek Generating Stations Radiological Environmental Monitoring Program.
Radioanalytical data from samples collected under this program were compared with results from the preoperational phase and historical results during operations. Differences between these periods were examined
statistically to determine the effects of station operations. This report presents the results from January 1 through December 31, 2013, for the SGS/HCGS REMP.
A.
Objectives of the Operational REMP
- 1.
To fulfill the requirements of the Radiological Surveillance sections of the SGS and HCGS ODCMs.
- 2.
To determine whether any significant increase occurred in the concentration of radionuclides in critical pathways.
- 3.
To verify the models used by SGS and HCGS to predict the radioactive inventory in the surrounding environment.
- 4.
To detect any change in ambient gamma radiation levels.
- 5.
To verify that SGS and HCGS operations do not have detrimental effects on the health and safety of the public or on the environment.
B.
Implementation of the Objectives
- 1.
Samples of various media were selected for monitoring due to the radiological dose impact to human and other organisms.
The selection of samples was based on:
(a)
Established critical pathways for the transfer of radionuclides through the environment to man, and (b)
Experience gained during the preoperational phase.
Sampling locations were determined based on site meteorology, Delaware River Bay estuarine hydrology, local demography, and land uses.
- 2.
Sampling locations are divided into two classes: indicator and control. Indicator stations are those which are expected to manifest station effects. Control samples are collected at locations which are believed to be unaffected by station operations, usually at 15 to 30 kilometers (9.3 to 18.6 miles) away from the generating stations. Fluctuations in the levels of radionuclides and direct radiation at indicator stations are evaluated with respect to analogous fluctuations at control stations. Indicator and control station data are also evaluated relative to preoperational data.
- 3.
Appendix A, Program Summary, describes and summarizes the analytical results in accordance with Section 6.9.1.7 of the SGS ODCM and Section 6.9.1.6 of the HCGS ODCM.
- 4.
Appendix B, Sample Designation and Locations, describes the coding system which identifies sample type and location. Table B-1 Sampling Locations, lists the station codes, locations, latitude, longitude and the types of samples collected at each station.
- 5.
The sampling locations are indicated on Maps B-1, Onsite Sampling Locations and B-2, Offsite Sampling Locations.
III.
Program Description A.
Data Interpretation Results of analyses are grouped according to sample type and presented in Appendix C, Data Tables. All results above the Lower Limit of Detection (LLD) are at a confidence level of +/- 2 sigma. This represents the range of values into which 95% of repeated analyses of
the same sample should fall. As defined in U.S. Nuclear Regulatory Commission Regulatory Guide 4.8, LLD is the smallest concentration of radioactive material in a sample that will yield a net count (above system background) that will be detected with 95% probability, with only 5% probability of falsely concluding that a blank observation represents a "real signal". The equation for determining LLD is:
)
exp(
22
.2 66
.4 t
Y V
E S
LLD b
4.66 is the statistical factor from NUREG 1302 Sb is the standard deviation of the background counting rate or of the counting rate of a blank sample as appropriate, as counts per minute, E
is the counting efficiency, as counts per disintegration, V is the sample size in units of mass or volume, 2.22 is the number of disintegrations per minute per picocurie, Y
is the fractional radiochemical yield, when applicable, is the radioactive decay constant for the particular radionuclide (sec-1), and t
for environmental samples is the elapsed time between sample collection, or end of the sample collection period, and time of counting (sec).
The LLD is an a priori number, which represents the capability of the measurement system (including instrumentation, procedure and sample type) and not as an after the fact criteria for the presence of activity. All analyses are designed to achieve the required SGS/HCGS detection limits for environmental sample analysis.
The Minimum Detectable Concentration (MDC) is defined as above with the exception that the measurement is an a posteriori (after the
fact) estimate of the presence of activity. The MDC is generally lower than the LLD.
The grouped data were averaged and standard deviations calculated.
The +/- 2 sigma deviations of the averaged data represent sample and not analytical variability. For reporting and calculation of averages, any positive result occurring at or below the LLD is considered to be at that level.
B.
Program Exceptions On 06/28/13, sample 11A1, taken at the SGS plant discharge, indicated positive tritium results of 374 pCi/L. There was a permitted release from SGS during the time of sampling. The results support the predicted concentration of tritium from the plant effluent permit.
(80106424)
When changing the 16E1 air sampler on 11/18/13, the sampler was not running. The sampler ran for approximately 51.5 hours5.787037e-5 days <br />0.00139 hours <br />8.267196e-6 weeks <br />1.9025e-6 months <br /> for the week. The motor in the sampler was replaced and returned to service. During 2014, PSEG plans to systematically replace all of the sampler motors that have not already been replaced. (80106424)
The air sampler at station 6S1 had a 109.8 hour9.259259e-5 days <br />0.00222 hours <br />1.322751e-5 weeks <br />3.044e-6 months <br /> outage (fuse blown and replaced) for the week of 07/08/13 to 07/15/13. (70154305)
Surface water samples collected 02/05/13 from locations 16F1 and 1F2 had positive I-131 results, 1.7 pCi/L and 1.5 pCi/L, respectively.
Both of these locations are 7 miles upstream of SGS and HCGS and approximately a mile and a half apart. Liquid permits for the sampling period were reviewed and indicated no I-131 was released from either SGS or HCGS. Since these sample locations are upstream of the nuclear complex and taken in the latter part of the ebb (outgoing) tide,
the most likely source of the contamination is the result of a medical procedure. Positive I-131 activity has been previously identified in the Delaware River as a result of medical procedures. (70151909)
The LLD for BaLa-140 of 15 pCi/L was missed on two surface water samples collected 02/05/13 from locations 11A1 and 1F2 due to a laboratory error. The specific error was that one of the laboratory gamma spectroscopy detector that was used to count these two samples had an incorrect setting established to calculate the MDC.
The detector value was set at 3.29 instead of 4.66. This resulted in all MDC values being calculated 41.6% lower. After a thorough investigation by the laboratory all affected client sample were reprocessed and revised reports were issued. The issue was documented by the vendors internal corrective action program nonconformance 13-07 report.
During the week of 04/29/13 to 05/06/13, the fuse blew in the temporary air sampler installed at station 16S1. Due to the low air volume for sample SA-AIO-16S1 the vendor lab could not meet the LLD of 7E-02 pCi/m3. A value of <8.34E-02 pCi/m3 for I-131 was calculated and reported. The vendor lab also could not meet the Gross Beta LLD of 1E-02 pCi/m3. A value of <1.7E-02 pCi/m3 was calculated and reported. A new fuse was installed and the air sampler returned to service. Permanent air samplers were installed in December of 2013. (70154305)
Cesium-137 (Cs-137) was detected in two of the site garden December 2013 samples. Stations 15S1 and 1S1 had detectable concentrations of 13 pCi/kg (wet) and 19 pCi/kg (wet), respectively. If the cesium was from plant effluents, there would be other isotopes detected, notably cobalt-60 (Co-60), that are more prevalent in the effluent streams. Cesium-137, attributed to atmospheric nuclear weapons testing, was detected in the garden soil samples earlier this
year. Since the samples are not washed, it is likely that the contamination was from the soil, similar to Cs-137 found in 2012 in the site garden samples. (70163130)
During the 4th quarter, TLDs from station 7F2 and station 16S3 could not be located. They have been replaced and the location of the dosimeter moved slightly to prevent further loss. (80106424)
C.
Program Changes Revision 27 of the SGS ODCM and the HCGS ODCM went into effect December 16, 2013 and December 20, 2013, respectively. (see 2013 SGS/HCGS ARERR for details). As part of that change several additional sampling locations were added to the REMP:
Air sample locations 7S1 and 15S2.
TLD locations 8S1, 9S1, 12S1, 13S1, 14S1, 16S3 and 8F1 Broadleaf sample locations 1S1, 16S1, 16S2 and 10D1.
In 2013, temporary stations with sample location IDs 6S1 and 16S1 were installed as test locations. These test locations were eventually added to the ODCM as permanent locations 7S1 and 15S2, which will be sampled starting in 2014. Results from stations 6S1 and 16S1 are included in this report as part of air sampling results and designated as such when reported in Appendices A, B and C. Permanent locations 7S1 and 15S2 are listed in Table B-1, but were not sampled in 2013.
Sample results in 2013 for TLD locations 8S1, 9S1, 12S1, 13S1, 14S1, 16S3 and 8F1 as well as broadleaf sample locations 1S1, 16S1, 16S2 and 10D1 are also included in Appendices A, B and C even though the samples were not officially added to the ODCMs until
December 2013. In the appendices, a marker has been added to help identify these new stations.
Two of the new TLD locations (12S1 and 13S1) were close to the site boundary, but became inaccessible during the summer months (second and third quarters) due to heavy vegetation. Consequently, they were relocated inside of the protected area.
D.
Quality Assurance Program Teledyne Brown Engineering The quality of the results obtained by TBE is ensured by the implementation of the Quality Assurance Program as described in the Teledyne Brown Engineering Quality Assurance Manual and the Teledyne Brown Engineering Procedure Manual.
E.
Summary of Results: Inter-laboratory Comparison Program The testing laboratory analyzed Performance Evaluation (PE) samples of air particulate, air iodine, milk, soil, vegetation and water matrices, as appropriate for 185 analyses. (Appendix D, Tables D-1 through D-3)
The PE samples, supplied by Eckert & Ziegler Analytics, Inc (EZA),
Environmental Resource Associates (ERA) and Department of Energys (DOE) Mixed Analyte Performance Evaluation Program (MAPEP), were evaluated against the following acceptance criteria:
- 1.
EZA Evaluation Criteria EZAs evaluation report provides a ratio of reported result and EZAs known value. Since flag values are not assigned by EZA, TBE evaluates the reported ratios based on internal QC requirements, which are based on the DOE MAPEP criteria.
- 2.
ERA Evaluation Criteria ERAs evaluation report provides an acceptance range for control and warning limits with associated flag values. ERAs acceptance limits are established per the United States Environmental Protection Agency (USEPA), National Environmental Laboratory Conference (NELAC) performance testing (PT) program requirements or ERAs standard operating procedure (SOP) for the Generation of Performance Acceptance Limits, as applicable. The acceptance limits are either determined by a regression equation specific to each analyte or a fixed percentage limit promulgated under the appropriate regulatory document.
- 3.
DOE Evaluation Criteria MAPEPs evaluation report provides an acceptance range with associated flag values.
The MAPEP defines three levels of performance: Acceptable (flag = A), Acceptable with Warning (flag = W), and Not Acceptable (flag = N). Performance is considered acceptable when a mean result for the specified analyte is +/- 20% of the reference value. Performance is acceptable with warning when a mean result falls in the range from +/- 20% to +/- 30% of the
reference value (i.e., 20% < bias < 30%). If the bias is greater than 30%, the results are deemed not acceptable.
Teledyne Brown Engineering For the TBE laboratory, 178 out of 185 analyses performed met the specified acceptance criteria. Seven analyses (Sr-89 and Sr-90 in milk, Co-57, Zn-65 and Sr-90 in soil, Cs-134 in air particulate and Sr-90 in vegetation [two low warning in a row]) did not meet the specified acceptance criteria or internal QA requirements for the following reasons:
- 1.
Teledyne Brown Engineerings Analytics September 2013 Sr-89 in milk result of 63.9 pCi/L was lower than the known value of 96.0 pCi/L. The failure was a result of analyst error and was specific to the Analytics sample. Client samples for the associated time period were evaluated and no client samples were affected by this failure. Nonconformance Report (NCR) 13-15
- 2.
Teledyne Brown Engineerings Analytics September 2013 Sr-90 in milk result of 8.88 pCi/L was lower than the known value of 13.2 pCi/L. The failure was a result of analyst error and was specific to the Analytics sample. Client samples for the associated time period were evaluated and no client samples were affected by this failure. NCR 13-15
- 3. & 4. Teledyne Brown Engineerings MAPEP September 2013 Co-57 and Zn-65 in soil were evaluated as failing the false positive test. While MAPEP evaluated the results as failures, the gamma software listed the results as non-identified nuclides.
The two nuclides would never have been reported as detected nuclides to a client. MAPEP does not allow laboratories to put
in qualifiers for the submitted data nor less than results.
MAPEP evaluates results based on the relationship between the activity and the uncertainty. MAPEP spiked the soil sample with an extremely large concentration of Eu-152, which was identified by the gamma software as an interfering nuclide, resulting in forced activity results that were evaluated by MAPEP as detected Co-57 and Zn-65. No client samples were affected by these failures. NCR 13-14
- 5.
Teledyne Brown Engineerings MAPEP September 2013 Sr-90 in soil result of 664 Bq/kg was higher than the known value of 460 Bq/kg, exceeding the upper control limit of 598 Bq/kg. An incorrect Sr-90 result was entered into the MAPEP database.
The correct Sr-90 activity of 322 Bq/kg would have been evaluated as acceptable with warning. No client samples were affected by this failure. NCR 13-14
- 6.
Teledyne Brown Engineerings MAPEP September 2013 Cs-134 in air particulate activity of -0.570 Bq/sample was evaluated as a failed false positive test, based on MAPEPs evaluation of the result as a significant negative value at three standard deviations. A negative number would never have been reported as a detected nuclide to a client, therefore no client samples were affected by this failure. NCR 13-14
- 7.
Teledyne Brown Engineerings MAPEP September 2013 Sr-90 in vegetation result was investigated due to two low warnings in a row. It appears the September sample was double spike with carrier, resulting in a low activity. With a recovery of about 50%
lower, the Sr-90 result would have fallen within the acceptance range. No client samples were affected by this issue. NCR 13-14
IV.
Results and Discussion The analytical results of the 2013 REMP samples are divided into categories based on exposure pathways: atmospheric, direct radiation, terrestrial, and aquatic. The analytical results for the 2013 REMP are summarized in Appendix A, Program Summary. The data for individual samples are presented in Appendix C, Data Tables. The data are compared to the formal pre-operational environmental monitoring program data (1973-1976) and to historical data during operations. The data collected demonstrates that the SGSs and HCGSs REMP was conducted in compliance with the Technical Specifications and SGSs and HCGSs ODCM.
The REMP for the SGS/HCGS Site has historically included samples and analyses not specifically required by the SGSs and HCGSs ODCM. These analyses are referenced throughout the report as Management Audit samples. Laboratory Testing Services continues to collect these samples.
The summary tables in this report include these additional samples and analyses.
These Management Audit Samples are samples that are taken to augment the radiological effluent monitoring program, but do not have a regulatory basis nor do they fulfill any regulatory requirement. The following is a list and quantity of the Management audit samples collected in 2013:
Food crops (29)
Well water (13)
Potable water (raw and treated (24)
Fodder crops (5)
Soil (9)
Beef and game (1)
A.
Atmospheric Air particulates samples were collected on Schleicher-Schuell No. 25 glass fiber filters with low-volume air samplers.
Iodine was collected from the air by adsorption on triethylene-diamine (TEDA) impregnated charcoal cartridge connected in series after the air particulate filters. Air sample volumes were measured with calibrated dry-gas meters. The displayed volumes were corrected to standard temperature and pressure.
- 1.
Air Particulates Air particulate (APT) samples were collected weekly at seven indicator locations (16E1, 16S1, 1F1, 2F6, 5D1, 5S1 and 6S1),
one duplicate station (5S2) and one control location (14G1).
The duplicate station sample was shipped to the QC laboratory GEL for analysis. Each weekly sample collected was analyzed for gross beta. Quarterly composites of the weekly samples from each station were analyzed for specific gamma emitters.
Gross Beta Gross beta activity was detected in 355 of 356 of the indicator station samples at concentrations ranging from 5E-03 to 30E-03 pCi/m3 with an average concentration of 13E-03 pCi/m3, and in 52 of 52 of the control station samples at concentrations ranging from 8E-03 to 26E-03 pCi/m3 with an average of 15E-03 pCi/m3. The maximum preoperational level detected was 920E-03 pCi/m3 with an average concentration of 74E-03 pCi/m3. (Table C-2, Appendix C) [Figure 1 - Results for gross beta analysis from 1990 to current year are plotted as quarterly averages, with an inset depicting the period 1973 to 2013].
Gamma Spectrometry Gamma spectroscopy was performed on each of the 32 quarterly composite samples.
Beryllium-7, attributed to cosmic ray activity in the atmosphere, was detected in all 28 indicator station composites at concentrations ranging from 66E-03 to 159E-03 pCi/m3 with an average concentration of 103E-03 pCi/m3, and in the four control station composites ranging in concentration from 69E-03 to 151E-03 pCi/m3 with an average concentration of 105E-03 pCi/m3. The maximum preoperational level detected was 330E-03 pCi/m3 with an average concentration of 109E-03 pCi/m3. Naturally occurring potassium-40 was detected in one of 28 indicator station composites at a concentration of 56E-03 pCi/m3. All other gamma emitters were less than the MDC.
(Table C-I, Appendix C).
- 2.
Air Iodine Filtered air iodine samples (AIO) were collected weekly at seven indicator locations (16E1, 16S1, 1F1, 2F6, 5D1, 5S1 and 6S1), one duplicate station (5S2) and one control location (14G1). The duplicate station sample was shipped to the QC laboratory GEL for analysis. Each sample was analyzed for I-131. Iodine-131 was not detected in any indicator or control samples. The maximum preoperational level detected was 42E-03 pCi/m3. (Table C-3, Appendix C)
B.
Direct Radiation Ambient radiation levels in the environs were measured with a pair of thermoluminescent dosimeters (TLD) supplied and processed by
Mirion Technologies. Packets containing these passive dosimeters were placed in the owner-controlled area and around the Site at various distances and in each land based meteorological sector and analyzed quarterly. Emphasis was placed on special interest areas such as population centers, nearby residences, and schools.
A total of 58 Immersion Dose Monitor (IDM) locations were established to monitored for direct radiation during 2013, including 20 on-site locations (2S2, 2S4, 3S1, 4S1, 5S1, 6S2, 7S1, 8S1, 9S1, 10S1, 11S1, 12S1, 13S1, 14S1, 15S1, 15S2, 16S1, 16S3, 1S1 and 16S2), 32 off-site locations within the 10 mile zone (1F1, 2E1, 2F2, 2F5, 2F6, 3E1, 3F2, 3F3, 4D2, 4F2, 5D1, 5F1, 6F1, 7F2, 8F1, 9F1, 10D1, 10F2, 11E2, 11F1, 12E1, 12F1, 13E1, 13F2, 13F3, 13F4, 14D1, 14F2, 15D1, 15F3, 16E1 and 16F2) and six control locations beyond 10 miles (3G1, 14G1, 1G3, 3H1, 10G1 and 16G1).
Each location has two TLDs, containing two thermoluminescent phosphors of calcium fluoride (CaF) and Lithium Fluoride (LiF) phosphors.
The average quarterly dose rate for the off-site dosimeters was 14.2 mR/Std. Qtr. Excluding locations 1S1 and 16S2, the onsite site boundary locations average quarterly dose rate was 13.3 mR/Std. Qtr.
The control locations average quarterly dose rate was 14.1 mR/Std.
Qtr. No significant differences were noted between the three groups.
(Table C-4, Appendix C)
The ambient radiation levels as measured by the two site boundary locations 1S1 and 16S2 ranged from 34.3 mR/Std. Qtr. to 37 mR/Std.
Qtr. The doses at these two locations were influenced by the radiation shine from the dry cask storage located in the nearby Independent Spent Fuel Storage Installation (ISFSI). Assuming a nominal
background of 52 mR/year (13 mR/Std. Qtr.) the maximum dose in this areas that could potentially affect a member of the population was calculated using the annual air exposure from location 16S2 (148 mR/year) as 86.4 mrem per year (148 mR/year - 52 mR/year
- 0.9 mrem/mR).
40 CFR 190 and 10 CFR 72.104 both limit the dose to a real member of the public to 25 mrem to the total body. The nearest resident in the North sector is greater than five miles and 4.2 miles in the NNW sector, respectively from SGS/HCGS. To demonstrate compliance to these regulations, an individual member of the public is assumed to enter the site boundary area near the ISFSI for 20 days per year. The dose that this hypothetical individual would receive was calculated at 4.7 mrem/year (86.4 mrem/year
- 20 days / 365 days), which is well below the federal limits for exposure.
The preoperational average for the quarterly TLD readings was 4.4 milliroentgen per standard month or 13.2 milliroentgen per standard quarter. The results of the direct radiation measurements for 2013 confirmed that the radiation levels in the vicinity of the SGS and HCGSs were similar to previous years.
C.
Terrestrial Terrestrial REMP sampling includes the collection of milk, well water, potable water, vegetation, fodder crops and soil samples.
Milk samples (MLK) were taken semi-monthly when cows were on pasture and monthly when cows were not grazing on open pasture from three indicator locations (13E3, 14F4, 2G3) and one control location (3G1). Animals are considered on pasture from April to November of each year. Samples were collected in new polyethylene
containers, frozen and transported in ice chests with no preservatives added to the milk.
Well water samples (WWA) were collected monthly from one location (3E1). Separate raw (PWR) and treated potable water (PWT) samples were collected monthly from one location (2F3). Each monthly composite was prepared by daily compositing by the City of Salem Water and Sewer Department. All samples were collected in new polyethylene containers.
Locally grown vegetables (FPV) were collected at the time of harvest at eight locations (2F9, 3H5, 15F4, 1G1, 2G2, 3F6, 3F8 and 13E3);
fodder crops (VGT) were sampled at four locations (13E3, 14F4, 2G3 and 3G1); and broad leaf vegetation (FPL) was sampled at five locations (10D1, 15S1, 16S1, 1S1 and 6S1). The vegetables and fodder samples are additional samples (Management Audit) taken to enhance the radiological monitoring program. There is no dairy farm within three miles of SGS and HCGS and there is only one dairy within five miles. Therefore, broadleaf vegetation is grown, maintained and harvested by LTS personnel in the late fall. All samples were weighed, packaged and shipped to TBE for analysis.
- 1.
Milk Milk samples were collected at four local dairy farms (two farms in NJ and two in Delaware). Each sample was analyzed for I-131 and gamma emitters.
Iodine-131 Iodine-131 was not detected above MDC in any of the 80 samples analyzed. The maximum preoperational level detected was 65 pCi/L, which occurred following a period of
atmospheric nuclear weapons tests. (Table C-5, Appendix C)
[Figure 2 - results from 1990 to 2013 are plotted as quarterly averages, with an inset graph depicting the period 1973 to 2013.]
Gamma Spectrometry Naturally occurring K-40 was detected in all 80 samples with concentrations for the 60 indicator station samples ranging from 1,162 pCi/L to 1,564 pCi/L with an average concentration of 1,344 pCi/L, and the 20 control station sample concentrations ranging from 1,149 pCi/L to 1,417 pCi/L, with an average concentration of 1,273 pCi/L. The maximum preoperational level detected was 2,000 pCi/L with an average concentration of 1,437 pCi/L. All other gamma emitters were less than the MDC. (Table C-5, Appendix C)
- 2.
Well Water (Ground Water)
Although wells in the vicinity of SGS/HCGS are not directly affected by plant operations, well water samples were collected monthly from one farm (3E1). Samples from this well are considered Management Audit samples.
Gross Alpha Gross alpha activity was not detected above the MDC in any of the well water samples. The maximum preoperational level detected was 9.6 pCi/L. (Table C-6, Appendix C)
Gross Beta Gross beta activity was detected in one of 13 well water samples at a concentration of 1.8 pCi/L. As with the 2012
gross beta results, the 2013 results are lower than the preoperational results which ranged from <2.1 pCi/L to 38 pCi/L, with an average value of 9 pCi/L. The downward trend may be attributed to the REMP participant installing a water treatment system for this well in February, 2009. (Table C-6, Appendix C)
Tritium Tritium activity was not detected above the MDC in any of the well water samples. The maximum preoperational level detected was 380 pCi/L. (Table C-6, Appendix C)
Gamma Spectrometry Naturally occurring potassium-40 and radium-226 were not detected in any of the well water samples. The maximum preoperational level detected were 30 pCi/L and 2.0 pCi/L, respectively. All other gamma emitters were less than the MDC. (Table C-7, Appendix C)
- 3.
Potable Water (Drinking Water)
Both raw and treated potable water samples were collected and composited by The City of Salem Water and Sewer Department personnel. Each sample consisted of daily aliquots composited into a monthly sample. The raw water source for this plant is Laurel Lake and its adjacent wells. These are Management Audit samples as no liquid effluents discharged from SGS/HCGS directly affect this pathway.
Gross Alpha No gross alpha activity was detected in any of the raw or
treated water samples. The maximum preoperational level detected was 2.7 pCi/L. (Table C-8, Appendix C)
Gross Beta Gross beta activity was detected in 11 of the 12 raw water samples and 11 of the 12 treated water samples. The concentrations for the raw samples ranged from 3.4 pCi/L to 7.3 pCi/L. Concentrations for the treated water ranged from 2.9 pCi/L to 5.9 pCi/L. The average concentration for both raw and treated water was 4.7 pCi/L. The maximum preoperational level detected was 9.0 pCi/L with an average concentration of 4.2 pCi/L. (Table C-8, Appendix C)
Tritium Tritium activity was not detected in any of the raw or treated water samples. The maximum preoperational level detected was 350 pCi/L with an average of 179 pCi/L. (Table C-8, Appendix C)
Iodine-131 Iodine-131 measurements were performed to an LLD of 1.0 pCi/L. Iodine-131 activity was not detected in any of the raw or treated water samples. No preoperational data were available for comparison, since I-131 was not analyzed as a specific radionuclide analysis prior to 1989. Since that time all results have been below the MDC. (Table C-9, Appendix C)
Gamma Spectrometry Naturally occurring K-40 was not detected in any of the raw or treated water samples. No preoperational data were available
for comparison. Naturally occurring Ra-226 was not detected in any raw or treated water samples. The maximum preoperational level detected was 1.4 pCi/L. All other gamma emitters were less than the MDC. (Table C-9, Appendix C)
- 4.
Vegetables There are no farm products that are irrigated with water in which liquid plant effluents have been discharged.
A variety of food products are sampled from around the plant; however, the variety is dependent on the farmers preference.
These vegetables are collected as Management Audit samples.
In addition, broadleaf vegetation was grown by LTS personnel and planted at four onsite locations and one offsite location in Delaware at 3.9 miles SSW. These broad leaf vegetable samples are collected since there are no milk farms operating within the five km radius of SGS/HCGS. The closest milk farm (13E3) is located in Odessa, DE at 5.0 miles (7.88 km).
All samples (vegetable and broadleaf) were analyzed for gamma emitters and included asparagus, cabbage, peaches, sweet corn, peppers, tomatoes and soy beans. These samples were from eight indicator stations (20 samples) and three control stations (10 samples). The results for these samples are discussed below.
Gamma Spectrometry Naturally occurring Be-7, attributed to cosmic ray activity in the atmosphere, was detected in four of the 20 indicator station samples (cabbage), with concentrations ranging from 228 pCi/kg (wet) to 372 pCi/kg (wet), with an average concentration of 279 pCi/kg (wet). It was not detected in any of the control
station samples. No preoperational data were available for comparison.
Naturally occurring K-40 was detected in all 20 indicator samples, with concentrations ranging from 1,603 pCi/kg (wet) to 13,750 pCi/kg (wet) with an average concentration of 3,100 pCi/kg (wet), and in all 10 control station samples at concentrations ranging from 1,269 pCi/kg (wet) to 2,433 pCi/kg (wet) with an average concentration of 1,963 pCi/kg (wet). The maximum preoperational level detected was 4,800 pCi/kg (wet) with an average concentration of 2,140 pCi/kg (wet).
(Table C-10, Appendix C)
Cesium-137 was detected in two indicator samples (cabbage) with concentrations of 13 and 19 pCi/kg (wet), with an average concentration of 16 pCi/kg (wet), which is below the SGS and HCGS ODCMs LLD value of 80 pCi/kg (wet). The results of this sample are discussed in the beginning summary section.
All other gamma emitters were less than the MDC.
- 5.
Fodder Crops Although not required by the SGS and HCGS ODCMs, four samples of silage normally used as cattle feed were collected from three indicator stations and one control station. It was determined that these products could be an element in the food-chain pathway. These fodder crops are collected as Management Audit samples and analyzed for gamma emitters.
All four locations from which samples were collected are milk sampling stations.
Gamma Spectrometry Naturally occurring Be-7, attributed to cosmic ray activity in the atmosphere, was detected in all three indicator samples at concentrations ranging from 196 pCi/kg (wet) to 249 pCi/kg (wet) with an average concentration of 231 pCi/kg (wet), and in the control station sample at 193 pCi/kg (wet). The maximum preoperational level detected for silage was 4,700 pCi/kg (wet) with an average concentration of 2,000 pCi/kg (wet).
Naturally occurring K-40 was detected in all three indicator samples at concentrations ranging from 2,968 pCi/kg (wet) to 4,052 pCi/kg (wet) with an average concentration of 3,554 pCi/kg (wet), and in the control station sample at a concentration of 713 pCi/kg (wet). Preoperational results averaged 7,000 pCi/kg (wet). All other gamma emitters were less than the MDC. (Table C-11, Appendix C)
- 6.
Soil Soil is sampled every three years at nine locations, and analyzed for gamma emitters. These Management Audit samples were collected in areas that have been relatively undisturbed since the last collection (2010) in order to determine any change in the radionuclide inventory of the area.
(Table C-12, Appendix C)
Gamma Spectrometry Naturally occurring K-40 was detected in all nine samples at concentrations ranging from 5,038 pCi/kg (dry) to 18,510 pCi/kg (dry) with an average concentration of 10,980 pCi/kg (dry). The
maximum preoperational level detected was 24,000 pCi/kg (dry) with an average of 10,000 pCi/kg (dry).
Cesium-137 was detected in six of the nine samples at concentrations ranging from 45 pCi/kg (dry) to 227 pCi/kg (dry) with an average concentration of 130 pCi/kg (dry). The maximum preoperational level detected was 2,800 pCi/kg (dry) with an average of 800 pCi/kg (dry). [Figure 6 - Results for the Cs-137 analyses from 1974 to current year are plotted as the triennial average.] (Table C-12, Appendix C)
Naturally occurring Ra-226 was detected in five of the nine samples at concentrations ranging from 1,324 pCi/kg (dry) to 2,595 pCi/kg (dry) with an average concentration of 2,100 pCi/kg (dry). The maximum preoperational level detected was 1,500 pCi/kg (dry) with an average of 870 pCi/kg (dry).
Naturally occurring Th-232 was detected in all nine samples at concentrations ranging from 350 pCi/kg (dry) to 1,207 pCi/kg (dry) with an average concentration of 702 pCi/kg (dry). The maximum preoperational level detected was 1,400 pCi/kg (dry) with an average of 740 pCi/kg (dry). (Table C-12, Appendix C)
- 7. Beef and Game Although not required by the SGS or HCGS ODCMs, one muskrat sample was collected from one indicator station. The game sample was collected as a Management Audit sample and analyzed for gamma emitters.
Gamma Spectrometry Naturally occurring K-40 was detected at a concentration of 3,307 pCi/kg (wet). No preoperational data were available for comparison. All other gamma emitters were less than the MDC. (Table C-13, Appendix C)
D.
Aquatic Environmental Consulting Services, Inc (ECSI) collected all aquatic samples (with the exception of the 6S2 shoreline sediment). This sample set includes edible fish, shoreline and riverbed sediment, surface water and crab.
Surface water samples were collected offshore. The technicians collect the samples in new polyethylene containers that were rinsed twice with the sample medium prior to collection. The surface water samples were transported to TBE for analysis.
Edible fish were taken by gill nets while crabs were caught in commercial traps. These samples were processed by separating the flesh from the bone and shell. The flesh was placed in sealed containers and frozen before being transported in ice chests to TBE for analysis.
Sediment samples collected by ECSI were taken with a bottom grab sampler and frozen in sealed polyethylene containers before being transported in ice chests to TBE. For the river bottom sediment, a marine GPS was used to locate the correct site and the sampling boat was maneuvered over the area until the correct amount of sample was obtained (grabbed) with the sediment dredge. Personnel from LTS collected and prepared the location 6S2 shoreline sediment sample (an onsite location).
For this location, a square area, measuring one meter on each side was staked out and then divided into a grid of nine smaller boxes, three per side. A one inch deep scoop from the center of each of the small grids was taken. All the aliquots were combined and the total sample transported in the ice chest to TBE.
- 1.
Surface Water Surface water samples were collected monthly at four indicator stations and one control station in the Delaware River Bay Estuary. One location (11A1) is at the outfall area (which is the area where liquid radioactive effluents from SGS are discharged into the Delaware River), one is downstream from the outfall area (7E1), and one is directly west of the outfall area at the mouth of the Appoquinimink River (12C1). Two upstream locations are in the Delaware River (1F2) and at the mouth of the Chesapeake and Delaware Canal (16F1), the latter being sampled when the flow is from the Canal into the river.
Station 12C1, directly west, at the mouth of the Appoquinimink River, serves as the operational control. Location 12C1 was chosen as the control location because the physical characteristics of this station more closely resemble those of the outfall area than do those at the farther upstream location (1F2). As discussed in the pre-operational summary report, due to the tidal nature of this Delaware River Bay Estuary, there are flow rate and salinity variations in the River. These variations will account for differences in concentrations of K-40 and the associated gross beta results due to K-40.
Gross Beta Gross beta activity was detected in all of the 48 indicator station samples with concentrations ranging from 5 pCi/L to 264 pCi/L and an average concentration of 94 pCi/L, and in all 12 of the control station samples with concentrations ranging from 4 pCi/L to 264 pCi/L and an average concentration of 102 pCi/L. The maximum preoperational level detected was 110 pCi/L with an average concentration of 32 pCi/L. (Table C-14, Appendix C) [Figure 3 - Quarterly results for all locations are plotted for the years 1990 to 2013, with an inset graph depicting the period 1973 to 2013.]
Tritium Tritium activity was detected in one of 48 indicator samples with a concentration of 265 pCi/L and was not detected in any of the control samples. The maximum preoperational level detected was 600 pCi/L, with an average concentration of 210 pCi/L.
There is no dose from this radioactive material because the exposure pathway is drinking water and the Delaware River is salt/brackish at this point. (Table C-15, Appendix C) [Figure 4
- Quarterly positive results from 1990 to 2013 are plotted, with an inset graph depicting the period 1973 to 2013.]
Gamma Spectrometry Naturally occurring K-40 was detected in 20 of the 48 indicator station samples at concentrations ranging from 47 pCi/L to 177 pCi/L with an average concentration of 97 pCi/L, and in five of the 12 control station samples at concentrations ranging from 60 pCi/L to 137 pCi/L and an average of 104 pCi/L. The
maximum preoperational level detected for K-40 was 200 pCi/L with an average concentration of 48 pCi/L.
Iodine-131 Iodine-131 was detected in two of the 48 indicator samples at concentrations of 1.5 pCi/L and 1.7 pCi/L. See Program Exceptions Section for explanation. All other gamma emitters were less than the MDC. (Table C-16, Appendix C)
- 2.
Fish Edible species of fish were collected semi-annually at two indicator stations and one control station and analyzed for gamma emitters in edible flesh. Samples included channel catfish, white perch, black drum and striped bass.
Gamma Spectrometry Naturally occurring K-40 was detected in all four indicator station samples at concentrations ranging from 3,480 pCi/kg (wet) to 4,755 pCi/kg (wet) with an average concentration of 3,963 pCi/kg (wet), and all three control station samples at concentrations ranging from 3,407 pCi/kg (wet) to 4,705 pCi/kg (wet) with an average concentration of 4,132 pCi/kg (wet). The maximum preoperational level detected was 13,000 pCi/kg (wet) with an average concentration of 2,900 pCi/kg (wet). All other gamma emitters were less than the MDC. (Table C-17, Appendix C)
- 3.
Blue Crab Blue crab samples were collected twice during the season at one indicator and one control station. The edible portions were analyzed for gamma emitters.
Gamma Spectroscopy Naturally occurring K-40 was detected in both indicator station samples at concentrations of 2,599 pCi/kg (wet) and 4,316 pCi/kg (wet) with an average concentration of 3,458 pCi/kg (wet), and in both control station samples at concentrations of 2,803 pCi/kg (wet) and 2,868 pCi/kg (wet) with an average concentration of 2,836 pCi/kg (wet). The maximum preoperational level detected was 12,000 pCi/kg (wet) with an average concentration of 2,835 pCi/kg (wet). All other gamma emitters were less than the MDC. (Table C-18, Appendix C)
- 4.
Sediment Sediment samples were collected semi-annually from six indicator stations and one control station. Location 6S2 is the only shoreline sediment sample location and is directly subject to tidal fluctuations.
Gamma Spectroscopy Naturally occurring K-40 was detected in all 12 indicator station samples at concentrations ranging from 2,662 pCi/kg (dry) to 20,940 pCi/kg (dry), with an average concentration of 11,078 pCi/kg (dry), and at both control stations samples at concentrations of 16,470 pCi/kg (dry) and 17,430 pCi/kg (dry) with an average concentration of 16,950 pCi/kg (dry). The
maximum preoperational level detected was 21,000 pCi/kg (dry) with an average concentration of 15,000 pCi/kg (dry).
Cesium-137 was not detected in any of the indicator or control samples. The maximum preoperational level detected was 400 pCi/kg (dry) with an average concentration of 150 pCi/kg (dry).
(Figure 5 - Semi-annual positive results from 1990 to 2013 are plotted, with an inset graph depicting the period 1977 to 2013.)
Naturally occurring Ra-226 was detected in five of the 12 indicator station samples at concentrations ranging from 2,403 pCi/kg (dry) to 3,441 pCi/kg (dry) with an average concentration of 2,792 pCi/kg (dry), and in one of the two control station samples at a concentration of 3,228 pCi/kg (dry). The maximum pre-operational level detected was 1,200 pCi/kg (dry) with an average concentration of 760 pCi/kg (dry).
Naturally occurring Th-232 was detected in all 12 indicator station samples at concentrations ranging from 166 pCi/kg (dry) to 1,233 pCi/kg (dry) with an average concentration of 802 pCi/kg (dry), and in both of the control station samples at concentrations of 869 pCi/kg (dry) and 1168 pCi/kg (dry) with an average concentration of 1,019 pCi/kg (dry). The maximum pre-operational level detected was 1,300 pCi/kg (dry) with an average concentration of 840 pCi/kg (dry). All other gamma emitters were less than the LLD. (Table C-19, Appendix C)
E.
Land Use Survey SYNOPSIS OF 2013 LAND USE CENSUS A land use census was conducted in each of the 16 meteorological sectors to identify, within a distance of 8 km (5 miles), the location of the
nearest milk animal, the nearest residence and the nearest garden of greater than 50 m2 (500 ft2) producing broad leaf vegetation. In accordance with SGS and HCGS ODCMs, the census was performed using a door to door survey, visual survey, Google Earth and by consulting with local agricultural authorities.
A comparison of the identified locations from the 2013 table with the 2012 table shows that there was no change to the nearest milk animal, nearest resident, or nearest vegetable garden (>500 ft2) with broadleaf vegetation identified. Therefore, no formal dose evaluation or changes to the SGS and HCGS ODCMs are required. The 2013 Land Use Census results are summarized below:
Meteorological Sector Milk Animal August, 2013 Km (miles)
Nearest Residence August, 2013 Km (miles)
Vegetable Garden August, 2013 Km (miles)
Meat Animal August, 2013 Km (miles)
N None None None None NNE None 8.0 (5.0)
None 6.8 (4.2)
NE None 6.2 (3.9)
None None ENE None 6.2 (3.9)
None None None None ESE None None None None SE None None None None SSE None None None None S
None None None None SSW None 6.2 (3.9)
None None SW None 6.9 (4.3) 7.3 (4.6) 7.3 (4.6)
WSW None 7.1 (4.4)
7.8 (4.9) 6.5 (4.0)
None None WNW None 5.5 (3.4)
None None NW None 5.9 (3.7)
None None NNW None 6.8 (4.2)
None None V.
Annotations to Previous AREOR In the 2012 Annual Radiological Environmental Operating Report Table C-3, the air sample result for the SA-AIO-5S2 for the week of 04/09/12 - 04/16/12 was incorrectly reported as <0, instead of <14.
The "control station" notation in Table C-4 of the 2012 AREOR incorrectly lists six control stations. Only stations 3G1 and 14G1 should have been labeled as controls. (70151506)
In the 2012 Annual Radiological Environmental Operating Report Table C-16, the values for I-131 for July through December were incorrectly reported.
All values for I-131 were below the LLD value of 1 pCi/L. (70157113)
VI.
Hope Creek Technical Specification Limit for Primary Water Iodine Concentrations The Hope Creek primary water chemistry results for 2013 were reviewed.
The specific activity of the primary coolant did not exceed 0.2 microcuries per gram Dose Equivalent I-131 (DEI), and the DEI generally ranged from 1E-05 to 2E-05 microcuries per gram. Therefore, the iodine concentrations in the primary coolant did not exceed the Tech Spec limit specified in section 3.4.5.
VII.
Conclusions The Radiological Environmental Monitoring Program for SGS and HCGS was conducted during 2013 in accordance with the SGS and HCGS ODCMs.
The LLD values required by the SGS and HCGS ODCMs were achieved with minor exceptions for this reporting period (See Appendix A and Appendix C).
The objectives of the program were also met during this period. The data collected assist in demonstrating that SGS and HCGS were operated in compliance with the SGS and the HCGS ODCMs requirements.
The concentration of radioactive material in the environment that could be attributable to SGS and HCGS operations was only a small fraction, when compared to the concentration of naturally occurring and man-made radioactivity in the environment. Since these results were comparable to the results obtained during the preoperational phase of the program, which ran
from 1973 to 1976, and with historical results collected since commercial operation, PSEG Nuclear Personnel have concluded that the operation of the SGS and HCGS had no significant radiological impact on the environment.
From the results obtained, it can be concluded that the levels and fluctuations of radioactivity in environmental samples were as expected.
VIII.
References
[1]
Radiation Management Corporation. "Artificial Island Radiological Environmental Monitoring Program - Preoperation Summary - 1973 through 1976". RMC-TR-77-03, 1978.
[2]
Public Service Enterprise Group. "Offsite Dose Calculation Manual"-
Salem Generating Station. Revision 26.
[3]
Public Service Enterprise Group. "Offsite Dose Calculation Manual"-
Hope Creek Generating Station. Revision 26.
[4]
U.S. Nuclear Regulatory Commission: Branch Technical Position -
Regulatory Guide 4.8, An Acceptable Radiological Monitoring Program, Revision 1, November 1979.
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APPENDIX A PROGRAM
SUMMARY
A-1
Intentionally left blank A-2
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION DOCKET NO. 50-272/-311 HOPE CREEK GENERATING STATION DOCKET NO. 50-354 SALEM COUNTY, NEW JERSEY January 1, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)
OF ANALYSES DETECTION (RANGE)
DISTANCE AND DIRECTION (RANGE)
(RANGE)
REPORTED PERFORMED (LLD)*
MEASUREMENTS I. AIRBORNE GR-B 408 10 13 (355/356)
SA-APT-14G1 C 15 (52/52) 15 (52/52) 0 AIR PARTICULATE (5/30) 11.8 MILES WNW (8/26)
(8/26)
(E-3 pCi/m3)
GAMMA 32 BE-7 NA 103 (28/28)
SA-APT-16S1***
116 (4/4) 105 (4/4) 0 (66/159) 0.53 MILES NNW (89/144)
(69/151)
K-40 NA 56 (1/28)
SA-APT-16S1***
56 (1/4)
<LLD 0
0.53 MILES NNW CS-134 50
<LLD
<LLD 0
CS-137 60
<LLD
<LLD 0
AIR IODINE GAMMA 408 (E-3 pCi/m3)
I-131 70
<LLD
<LLD 0
II. DIRECT DIRECT RADIATION TLD-QUARTERLY 226 NA 14.7 (202/202)
SA-IDM-16S2 37 (4/4) 14.1 (24/24) 0 (mR/standard quarter)
(7/39) 0.6 MILES N OF SITE (33/39)
(10/17)
III. TERRESTRIAL MILK I-131 80 1
<LLD
<LLD 0
(pCi/L)
GAMMA 80 K-40 NA 1344 (60/60)
SA-MLK-14F4 1367 (20/20) 1273 (20/20) 0 (1162/1564) 7.6 MILES WNW (1200/1564)
(1149/1417)
A-3
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION DOCKET NO. 50-272/-311 HOPE CREEK GENERATING STATION DOCKET NO. 50-354 SALEM COUNTY, NEW JERSEY January 1, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)
OF ANALYSES DETECTION (RANGE)
DISTANCE AND DIRECTION (RANGE)
(RANGE)
REPORTED PERFORMED (LLD)*
MEASUREMENTS MILK (cont'd)
CS-134 15
<LLD
<LLD 0
(pCi/L)
CS-137 18
<LLD
<LLD 0
BALA140 15
<LLD
<LLD 0
RA-226 NA
<LLD
<LLD 0
WELL WATER GR-A 13 3
<LLD NA 0
(pCi/L)
GR-B 13 4
1.8 (1/13)
SA-WWA-3E1 1.8 (1/13)
NA 0
4.2 MILES NE H-3 13 200
<LLD NA 0
GAMMA 13 K-40 NA
<LLD NA 0
MN-54 15
<LLD NA 0
CO-58 15
<LLD NA 0
A-4
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION DOCKET NO. 50-272/-311 HOPE CREEK GENERATING STATION DOCKET NO. 50-354 SALEM COUNTY, NEW JERSEY January 1, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)
OF ANALYSES DETECTION (RANGE)
DISTANCE AND DIRECTION (RANGE)
(RANGE)
REPORTED PERFORMED (LLD)*
MEASUREMENTS WELL WATER (cont'd)
FE-59 30
<LLD NA 0
(pCi/L)
CO-60 15
<LLD NA 0
ZN-65 30
<LLD NA 0
ZRNB-95 15
<LLD NA 0
I-131 1
<LLD NA 0
CS-134 15
<LLD NA 0
CS-137 18
<LLD NA 0
BALA140 15
<LLD NA 0
RA-226 NA
<LLD NA 0
POTABLE WATER GR-A 24 3
<LLD NA 0
(pCi/L)
A-5
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION DOCKET NO. 50-272/-311 HOPE CREEK GENERATING STATION DOCKET NO. 50-354 SALEM COUNTY, NEW JERSEY January 1, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)
OF ANALYSES DETECTION (RANGE)
DISTANCE AND DIRECTION (RANGE)
(RANGE)
REPORTED PERFORMED (LLD)*
MEASUREMENTS POTABLE WATER (cont'd)
GR-B 24 4
4.7 (22/24) 2F3 4.8 (11/12)
NA 0
(pCi/L)
(2.9/7.3) 8.0 MILES NNE (3.4/7.3)
H-3 24 200
<LLD NA 0
GAMMA 24 K-40 NA
<LLD NA 0
MN-54 15
<LLD NA 0
CO-58 15
<LLD NA 0
FE-59 30
<LLD NA 0
CO-60 15
<LLD NA 0
ZN-65 30
<LLD NA 0
ZRNB-95 15
<LLD NA 0
I-131 1
<LLD NA 0
A-6
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION DOCKET NO. 50-272/-311 HOPE CREEK GENERATING STATION DOCKET NO. 50-354 SALEM COUNTY, NEW JERSEY January 1, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)
OF ANALYSES DETECTION (RANGE)
DISTANCE AND DIRECTION (RANGE)
(RANGE)
REPORTED PERFORMED (LLD)*
MEASUREMENTS POTABLE WATER (cont'd)
CS-134 15
<LLD NA 0
(pCi/L)
CS-137 18
<LLD NA 0
BALA140 15
<LLD NA 0
RA-226 NA
<LLD NA 0
VEGETATION GAMMA 30 (pCi/kg wet)
BE-7 NA 279 (4/20)
SA-FPL-10D1 372 (1/1)
<LLD 0
(228/372) 3.9 MILES SSW K-40 NA 3100 (20/20)
SA-VGT-14F4 13750 (1/1) 1963 (10/10) 0 (1603/13750) 7.6 MILES WNW (1269/2433)
I-131 60
<LLD
<LLD 0
CS-134 60
<LLD
<LLD 0
CS-137 80 16 (2/20)
SA-FPL-1S1 19 (1/1)
<LLD 0
(13/19) 0.57 MILES N RA-226 NA
<LLD
<LLD 0
A-7
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION DOCKET NO. 50-272/-311 HOPE CREEK GENERATING STATION DOCKET NO. 50-354 SALEM COUNTY, NEW JERSEY January 1, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)
OF ANALYSES DETECTION (RANGE)
DISTANCE AND DIRECTION (RANGE)
(RANGE)
REPORTED PERFORMED (LLD)*
MEASUREMENTS VEGETATION (cont'd)
TH-232 NA
<LLD
<LLD 0
(pCi/kg wet)
FODDER CROPS GAMMA 4
(pCi/kg wet)
BE-7 NA 231 (3/3)
SA-VGT-2G3 249 (1/1) 193 (1/1) 0 (196/249) 11.8 MILES NNE K-40 NA 3554 (3/3)
SA-VGT-14F4 4052 (1/1) 713 (1/1) 0 (2968/4052) 7.6 MILES WNW I-131 60
<LLD
<LLD 0
CS-134 60
<LLD
<LLD 0
CS-137 80
<LLD
<LLD 0
RA-226 NA
<LLD
<LLD 0
TH-232 NA
<LLD
<LLD 0
SOIL GAMMA 9
(pCi/kg dry)
BE-7 NA
<LLD
<LLD 0
K-40 NA 11034 (7/7)
SA-SOL-13E3 18510 (1/1) 10790 (2/2) 0 (5038/18510) 5.0 MILES W (9139/12440)
A-8
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION DOCKET NO. 50-272/-311 HOPE CREEK GENERATING STATION DOCKET NO. 50-354 SALEM COUNTY, NEW JERSEY January 1, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)
OF ANALYSES DETECTION (RANGE)
DISTANCE AND DIRECTION (RANGE)
(RANGE)
REPORTED PERFORMED (LLD)*
MEASUREMENTS SOIL (cont'd)
CS-134 150
<LLD
<LLD 0
(pCi/kg dry)
CS-137 180 138 (4/7)
SA-SOL-10D1 227 (1/1) 114 (2/2) 0 (45/227) 3.9 MILES SSW (78/150)
RA-226 NA 2002 (3/7)
SA-SOL-3G1 C 2595 (1/1) 2247 (2/2) 0 (1324/2511) 16.5 MILES NE (1898/2595)
TH-232 NA 646 (7/7)
SA-SOL-3G1 C 1207 (1/1) 896 (2/2) 0 (350/1053) 16.5 MILES NE (584/1207)
BEEF AND GAME GAMMA 1
(pCi/kg wet)
BE-7 NA
<LLD NA 0
K-40 NA 3307 (1/1)
SA-GAM-5C1 3307 (1/1)
NA 0
3.14 MILES ENE I-131 60
<LLD NA 0
CS-134 60
<LLD NA 0
CS-137 80
<LLD NA 0
IV. AQUATIC SURFACE WATER GR-B 60 4
94 (48/48)
SA-SWA-7E1 145 (12/12) 102 (12/12) 0 (pCi/L)
(5/264) 4.5 MILES SE (22/264)
(4/264)
A-9
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION DOCKET NO. 50-272/-311 HOPE CREEK GENERATING STATION DOCKET NO. 50-354 SALEM COUNTY, NEW JERSEY January 1, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)
OF ANALYSES DETECTION (RANGE)
DISTANCE AND DIRECTION (RANGE)
(RANGE)
REPORTED PERFORMED (LLD)*
MEASUREMENTS SURFACE WATER (cont'd)
H-3 60 200 265 (1/48)
SA-SWA-11A1 265 (1/12)
<LLD 0
(pCi/L) 0.2 MILES SW GAMMA 60 K-40 NA 97 (20/48)
SA-SWA-7E1 112 (5/12) 104 (5/12) 0 (47/177) 4.5 MILES SE (84/177)
(60/137)
MN-54 15
<LLD
<LLD 0
CO-58 15
<LLD
<LLD 0
FE-59 30
<LLD
<LLD 0
CO-60 15
<LLD
<LLD 0
ZN-65 30
<LLD
<LLD 0
ZRNB-95 15
<LLD
<LLD 0
I-131 1
1.6 (2/48)
SA-SWA-16F1 1.7 (1/12)
<LLD 0
(1.5/1.7) 6.9 MILES NNW CS-134 15
<LLD
<LLD 0
A-10
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION DOCKET NO. 50-272/-311 HOPE CREEK GENERATING STATION DOCKET NO. 50-354 SALEM COUNTY, NEW JERSEY January 1, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)
OF ANALYSES DETECTION (RANGE)
DISTANCE AND DIRECTION (RANGE)
(RANGE)
REPORTED PERFORMED (LLD)*
MEASUREMENTS SURFACE WATER (cont'd)
CS-137 18
<LLD
<LLD 0
(pCi/L)
BALA140 15
<LLD
<LLD 0
FISH GAMMA 7
(pCi/kg wet)
K-40 NA 3963 (4/4)
SA-ESF-7E1 4402 (2/2) 4132 (3/3) 0 (3480/4755) 4.5 MILES SE (4048/4755)
(3407/4705)
MN-54 130
<LLD
<LLD 0
CO-58 130
<LLD
<LLD 0
FE-59 260
<LLD
<LLD 0
CO-60 130
<LLD
<LLD 0
ZN-65 260
<LLD
<LLD 0
CS-134 130
<LLD
<LLD 0
CS-137 150
<LLD
<LLD 0
A-11
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION DOCKET NO. 50-272/-311 HOPE CREEK GENERATING STATION DOCKET NO. 50-354 SALEM COUNTY, NEW JERSEY January 1, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)
OF ANALYSES DETECTION (RANGE)
DISTANCE AND DIRECTION (RANGE)
(RANGE)
REPORTED PERFORMED (LLD)*
MEASUREMENTS FISH (cont'd)
RA-226 NA
<LLD
<LLD 0
(pCi/kg wet)
BLUE CRABS GAMMA 4
(pCi/kg wet)
K-40 NA 3458 (2/2)
SA-ECH-11A1 3458 (2/2) 2836 (2/2) 0 (2599/4316) 0.2 MILES SW (2599/4316)
(2803/2868)
MN-54 130
<LLD
<LLD 0
CO-58 130
<LLD
<LLD 0
FE-59 260
<LLD
<LLD 0
CO-60 130
<LLD
<LLD 0
ZN-65 260
<LLD
<LLD 0
CS-134 130
<LLD
<LLD 0
CS-137 150
<LLD
<LLD 0
RA-226 NA
<LLD
<LLD 0
A-12
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION DOCKET NO. 50-272/-311 HOPE CREEK GENERATING STATION DOCKET NO. 50-354 SALEM COUNTY, NEW JERSEY January 1, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)
OF ANALYSES DETECTION (RANGE)
DISTANCE AND DIRECTION (RANGE)
(RANGE)
REPORTED PERFORMED (LLD)*
MEASUREMENTS SEDIMENT GAMMA 14 (pCi/kg dry)
BE-7 NA
<LLD
<LLD 0
K-40 NA 11078 (12/12)
SA-ESS-16F1 20485 (2/2) 16950 (2/2) 0 (2662/20940) 6.9 MILES NNW (20030/20940)
(16470/17430)
CS-134 150
<LLD
<LLD 0
CS-137 180
<LLD
<LLD 0
RA-226 NA 2792 (5/12)
SA-ESS-12C1 C 3228 (1/2) 3228 (1/2) 0 (2403/3441) 2.5 MILES WSW TH-232 NA 802 (5/12)
SA-ESS-16F1 1093 (2/2) 1019 (2/2) 0 (166/1233) 6.9 MILES NNW (1017/1168)
(869/1168)
- LLD LISTED IS THE LOWER LIMIT OF DETECTION WHICH WE ENDEAVORED TO ACHIEVE DURING THIS REPORTING PERIOD.
- TEMPORARY SAMPLING LOCATION A-13
Intentionally left blank A-14
APPENDIX B SAMPLE DESIGNATION AND LOCATIONS B-1
Intentionally left blank B-2
SAMPLE DESIGNATION The PSEGs Laboratory Testing Services (LTS) identifies samples by a three part code.
The first two letters are the program identification code. Because of the proximity of the Salem and Hope Creek Stations a common environmental surveillance program is being conducted. The identification code, "SA", has been applied to Salem and Hope Creek stations. The next three letters are for the media sampled.
AIO = Air Iodine IDM = Immersion Dose (TLD)
APT = Air Particulate MLK = Milk ECH = Hard Shell Blue Crab PWR = Potable Water (Raw)
ESF = Edible Fish PWT = Potable Water (Treated)
ESS = Sediment SOL = Soil FPL = Green Leaf Vegetables SWA = Surface Water FPV = Vegetables (Various)
VGT = Fodder Crops (Various)
GAM = Game (Muskrat)
WWA= Well Water The last four symbols are a location code based on direction and distance from a standard reference point. The reference point is located at the midpoint between the center of the Salem 1 and Salem 2 containments. Of these, the first two represent each of the sixteen angular sectors of 22.5 degrees centered about the reactor site. Sector one is divided evenly by the north axis and other sectors are numbered in a clockwise direction as follows:
1 = N 5 = E 9 = S 13 = W 2 = NNE 6 = ESE 10 = SSW 14 = WNW 3 = NE 7 = SE 11 = SW 15 = NW 4 = ENE 8 = SSE 12 = WSW 16 = NNW The next digit is a letter which represents the radial distance from the reference point:
S
= On-site location E
=
4-5 miles off-site A
= 0-1 miles off-site F
=
5-10 miles off-site B
1-2 miles off-site G
10-20 miles off-site C
= 2-3 miles off-site H
=
>20 miles off-site D
= 3-4 miles off-site The last number is the station numerical designation within each sector and zone; e.g.,
1,2,3,...etc. For example, the designation SA-WWA-3E1 would indicate a sample in the Salem and Hope Creek program (SA), consisting of well water (WWA), which had been collected in sector number 3, centered at 45 degrees (north east) with respect to the midpoint between Salem 1 and 2 containments at a radial distance of 4 to 5 miles off-site, (therefore, radial distance E). The number 1 indicates that this is sampling station
- 1 in that particular sector.
B-3
TABLE B-1 SAMPLING LOCATIONS Specific information about the individual sampling locations are given in Table B-1. Maps B-1 and B-2 show the locations of sampling stations with respect to the Site. A Portable Global Positioning System (GPS) was used to provide the coordinates of sampling locations.
STATION CODE STATION LOCATION LATITUDINAL LONGITUDINAL SAMPLE TYPE DEG. MIN. SEC DEG. MIN. SEC 1S1 0.55 mi. N 39 260 75 222 IDM, FPL***
2S2 0.40 mi. NNE; lamp pole 65 near HC switch yard 39 98 75 10 IDM 2S4 0.60 mi. NNE; in the equipment laydown area 39 110 75 992 IDM 3S1 0.58 mi. NE 39 140 75 678 IDM 4S1 0.60 mi. ENE; site access road near intersection to TB-02 39 023 75 544 IDM 5S1 0.86 mi. E; site access road 39 668 75 187 IDM, AIO, APT 5S2 0.86 mi. E; site access road, duplicate sample 39 668 75 187 AIO, APT 6S1 0.17mi. ESE; area around Helicopter Pad 39 698 75 979 AIO*, APT*, FPL***
6S2 0.23mi. ESE; area around helicopter pad 39 719 75 912 IDM, ESS, SOL 7S1 0.12 mi. SE; station personnel gate 39 720 75 15 IDM, AIO**, APT**
8S1 0.12 mi. SSE; fuel oil storage 39 676 75 055 IDM***
9S1 0.12 mi. S; fuel oil storage 39 636 75 091 IDM***
10S1 0.14 mi. SSW; circ. water bldg.
39 700 75 160 IDM 11S1 0.09 mi. SW; circ. water bldg.
39 719 75 225 IDM 12S1 0.09 mi. WSW; outside security fence 39 756 75 236 IDM***
13S1 0.09 mi. W; outside security fence 39 801 75 267 IDM***
14S1 0.10 mi. NNW; outside security fence 39 893 75 280 IDM***
15S1 0.57 mi. NW; near river and barge slip 39 161 75 525 IDM, FPV 15S2 0.59 mi. NW; near river 39 12 75 32 IDM, AIO**, APT**
16S1 0.57 mi. NNW; on road near fuel oil storage tank 39 215 75 432 IDM, AIO*, APT*, FPL***
16S2 0.60 mi. NNW; near security firing range 39 16 75 17 IDM, FPL***
16S3 1.0 mi. NNW; consolidated spoils facility 39 350 75 550 IDM***
11A1 0.20 mi. SW; Salem outfall area 39 59 75 25 ESS, SWA, ECH, ESF 11A1A 0.15 mi. SE; Located in the plant barge slip area 39 41 75 02 Alternate SWA B-4
TABLE B-1 (contd)
SAMPLING LOCATIONS STATION CODE STATION LOCATION LATITUDINAL LONGITUDINAL SAMPLE TYPE 15A1 0.65 mi. NW; Hope Creek outfall area 39 67 75 19 ESS 16A1 0.24 mi. NNW; South Storm Drain outfall 39 24 75 58 ESS 5C1 3.14 mi. ENE 39 250 75 430 GAM 12C1 2.5 mi. WSW; West bank of Delaware River 39 22 75 08 ESS, SWA, ECH, ESF 12C1A 3.7 mi. WSW; Located at the tip of Augustine Beach Boat Ramp 39 17 75 48 Alternate SWA 4D2 3.7 mi. ENE; Alloway Creek Neck Road 39 292 75 175 IDM 5D1 3.5 mi. E; local farm 39 396 75 334 IDM, AIO, APT 10D1 3.9 mi. SSW; Taylors Bridge Spur 39 613 75 733 IDM, FPL***, SOL 14D1 3.4 mi. WNW; Bay View, Delaware 39 26 75 521 IDM 15D1 3.8 mi NW; Rt. 9, Augustine Beach, DE 39 125 75 28 IDM 2E1 4.4 mi. NNE; local farm 39 380 75 428 IDM 3E1 4.2 mi. NE; local farm 39 098 75 646 IDM, WWA 7E1 4.5 mi. SE; River Bank 1.0 mi. W of Mad Horse Creek 39 08 75 64 ESS, SWA, ESF 7E1A 8.87 mi. SE; Located at the end of Bayside Road 39 57 75 24 Alternate SWA 11E2 5.0 mi. SW; Rt. 9 39 328 75 546 IDM 12E1 4.4 mi. WSW; Thomas Landing 39 862 75 968 IDM 13E1 4.2 mi. W; Diehl House Lab 39 989 75 735 IDM 13E3 5.0 mi. W; local farm 39 17 75 30 MLK, FPL***, VGT, SOL 16E1 4.1 mi. NNW; Port Penn 39 762 75 580 IDM, AIO, APT, SOL 1F1 5.8 mi. N; Fort Elfsborg 39 693 75 124 IDM, AIO, APT, 1F2 7.1 mi. N; midpoint of Delaware R.
39 08 75 54 SWA 2F2 8.5 mi. NNE; Salem Substation 39 522 75 120 IDM 2F3 8.0 mi. NNE; City of Salem Water and Sewage Department 39 40 75 18 PWR, PWT 2F5 7.4 mi. NNE; Salem High School 39 448 75 514 IDM 2F6 7.3 mi. NNE; PSE&G Training Center, Salem NJ 39 713 75 819 IDM, AIO, APT 2F9 7.5 mi. NNE; Local Farm, Tilbury Rd, Salem 39 55 75 30 FPV, SOL 2F10 9.2 mi. NNE; Local Farm, South Broadway (Rt. 49) Pennsville 39 35 75 35 FPV, FPL***
3F2 5.1 mi. NE; Hancocks Bridge, NJ Munc Bldg 39 410 75 578 IDM 3F3 8.6 mi. NE; Quinton Township Elem. School NJ 39 616 75 - 24 - 735 IDM B-5
TABLE B-1 (contd)
SAMPLING LOCATIONS STATION CODE STATION LOCATION LATITUDINAL LONGITUDINAL SAMPLE TYPE 3F6 6.5 mi. NE; Local Farm, Salem/Hancocks Bridge Road 39 03 75 00 FPV 3F7 7.2 mi. NE; Local Farm, Beasley Neck Road, RD#3 39 07 75 46 FPV 3F8 9.3 mi. NE; Circle M Orchard 39 987 75 468 FPV 4F2 6.0 mi. ENE; Mays Lane, Harmersville, NJ 39 953 75 076 IDM 5F1 6.5 mi. E; Canton, NJ 39 360 75 031 IDM,SOL 6F1 6.4 mi. ESE; Stow Neck Road 39 396 75 148 IDM 7F2 9.1 mi. SE; Bayside, NJ 39 971 75 261 IDM 8F1 9.7 mi. SE; Woodland Beach, DE 39 933 75 463 IDM***
9F1 5.3 mi. S; off Route #9, DE 39 042 75 95 IDM 10F2 5.8 mi. SSW; Rt. 9 39 034 75 152 IDM 11F1 6.2 mi. SW; Taylors Bridge, DE 39 766 75 632 IDM 12F1 9.4 mi. WSW; Townsend Elementary School, DE 39 778 75 311 IDM 13F2 6.5 mi W; Odessa, DE 39 297 75 372 IDM 13F3 9.3 mi. W; Redding Middle School, Middletown, Delaware 39 215 75 543 IDM 13F4 9.8 mi. W; Middletown, DE 39 857 75 111 IDM 14F2 6.7 mi. WNW; Rt 13 and Boyds Corner Rd 39 979 75 042 IDM 14F4 7.6 mi. WNW; local farm 39 44 75 52 MLK, VGT, SOL 15F3 5.4 mi. NW 39 987 75 586 IDM 15F4 7.0 mi. NW; local farm; Port Penn Road; Delaware 39 21 75 31 FPV 16F1 6.9 mi. NNW; C&D Canal 39 55 75 25 ESS, SWA 16F1A 6.84 mi. NNW; Located at the C&D Canal Tip 39 34 75 56 Alternate SWA 16F2 8.1 mi. NNW; Delaware City Public School 39 314 75 429 IDM 1G1 10.9 mi. NNE; Rte. 49, South Broadway 39 113 75 178 FPV 1G3 19 mi. N; N. Church St. Wilmington, Del 39 287 75 512 IDM 2G2 13.5 mi. NNE; Local Farm; Pointers Auburn Road (Rt. 540),
Salem, NJ 08079 39 19 75 10 FPV 2G3 11.8 mi. NNE; Local Milk Farm 39 21 75 53 MLK, VGT, SOL 2G4 11.3 mi. NNE; large family garden; Rt 45 & Welchville Rd, Mannington, NJ 39 02 75 21 FPV 3G1 17 mi. NE; local farm 39 913 75 804 IDM, MLK, VGT, SOL B-6
TABLE B-1 (contd)
SAMPLING LOCATIONS STATION CODE STATION LOCATION LATITUDINAL LONGITUDINAL SAMPLE TYPE 9G1 10.3 mi. S; Local Farm, Woodland Beach Rd., Smyrna, Delaware 39 47 75 50 FPV 9G2 10.7 mi. S; Local Farm, Woodland Beach Road, Smyrna, Delaware 39 39 75 11 FPV 10G1 12 mi. SSW; Smyrna, Delaware 39 223 75 095 IDM 14G1 11.8 mi. WNW; Rte. 286, Bethel Church Rd., DE 39 290 75 495 AIO,APT,IDM 16G1 15 mi. NNW; Wilmington Airport 39 637 75 570 IDM 3H1 32 mi. NE; National Park, NJ 39 599 75 96 IDM 3H5 25 mi. NE; Farm Market, Rt 77 39 040 75 380 FPV NOTE: All station locations are referenced to the midpoint of the two Salem Units Containments. The coordinates of this location are: Latitude N 39° 46.5 and Longitude W 75° 10.6.
All Vegetables (FPV & FPL) and Vegetation (VGT), are management audit samples. They are not required by the Salem & Hope Creek Stations Tech Specs nor listed in the Stations ODCMs.
Vegetable samples are not always collected in consecutive years from the same farmer due to crop rotation.
- Temporary sampling location - see Program Changes
- Permanent sampling location - added to ODCMs in December 2013. Not sampled in 2013.
- New sampling location - see Program Changes B-7
TABLE B-2 SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (Program Overview)
EXPOSURE PATHWAY AND/OR SAMPLE NUMBER OF REPRESENTATIVE SAMPLES AND SAMPLE LOCATIONS SAMPLING AND COLLECTION FREQUENCY TYPE/FREQUENCY* OF ANALYSIS
- 1.
DIRECT RADIATION Dosimeters Fifty-eight routine*** monitoring stations with two or more dosimeters placed as follows:
An inner ring of stations, at least one in meteorological sector in the general area of the site boundary.
An outer ring of stations, at least one in each meteorological sector in the 3.4 - 9.8 mile range from the site.
The balance of the stations placed in special interest areas such as population centers, nearby residences, and schools and in six areas beyond 10 miles to serve as control stations.
Quarterly Gamma dose/ quarterly B-8
TABLE B-2 (cont'd)
SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM EXPOSURE PATHWAY AND/OR SAMPLE NUMBER OF REPRESENTATIVE SAMPLES AND SAMPLE LOCATIONS SAMPLING AND COLLECTION FREQUENCY TYPE/FREQUENCY* OF ANALYSIS
- 2.
ATMOSPHERIC
- a. Air Particulate
- b. Air Iodine 3 samples from close to the Site Boundary: 5S1, 6S1***,
16S1***.
One duplicate sample from close to the site boundary:
5S2 3 Samples in different land based sectors: 1F1, 2F6, 5D1.
1 Sample from the vicinity of a community: 16E1.
1 Sample from a control location, as for example 15 - 30 km distant (9.3 - 18.6 miles) and in the least prevalent wind direction: 14G1.
Continuous sampler operation with sample collection weekly or more frequently if required by dust loading Gross Beta / weekly Gamma isotopic analysis /
quarterly composite Iodine-131 / weekly
- 3.
TERRESTRIAL
- a. Milk Samples from milking animals in 3 locations within 5 km distance (3.1 miles). If there are none, then, 1 sample from milking animals in each of 3 areas between 5 - 8 km distant (3.1 - 5.0 miles): 13E3, 14F4, 2G3(1).
1 Sample from milking animals at a control location 15 -
30 km distant (9.3 - 18.6 miles): 3G1.
Semi-monthly (when animals are on pasture)
Monthly (when animals are on pasture)
Gamma scan / semi-monthly Iodine-131 / semi-monthly Gamma scan / monthly Iodine-131 / monthly B-9
TABLE B-2 (cont'd)
SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM EXPOSURE PATHWAY AND/OR SAMPLE NUMBER OF REPRESENTATIVE SAMPLES AND SAMPLE LOCATIONS SAMPLING AND COLLECTION FREQUENCY TYPE/FREQUENCY*
OF ANALYSIS
- b. Well Water (Ground)
Samples from one or two sources only if likely to be affected. (Although wells in the vicinity of SGS/HCGS are not directly affected by plant operations, 3E1 farms well, is sampled as management audit sample
).
Monthly Gamma Scan / monthly Gross alpha / monthly Gross beta / monthly Tritium / monthly
- c. Potable Water (Drinking Water)
One sample of the nearest water supply affected by its discharge (No potable water samples are required as liquid effluents discharged from SGS/HCGS do not directly affect this pathway). However, for management audit samples one raw and one treated sample from a public water supply (City of Salem Water and Sewer Department) is collected:
2F3.
Monthly (composited daily)
Gross alpha / monthly Gross beta / monthly Tritium / monthly Gamma scan / monthly Iodine-131 / monthly
- d. Vegetables One sample of each principal class of food products from area that is irrigated by water in which liquid plant wastes have been discharged (The Delaware River at the location of SGS/HCGS is a brackish water source and is not used for irrigation of food products). Management audit samples Annually (at harvest) are collected from various locations during harvest: 2F9, 2F10, 3F6, 3F7, 2G2, 9G1, 9G2, and 3H5. In addition, Broad leaf vegetation (cabbage and kale) was planted &
collected onsite (1S1***, 15S1, 16S1***, 16S2***) and across the river, 10D1***, in lieu of having a milk farm within 5 km (3.1 miles) of the Site(1).
Gamma scan / on collection B-10
TABLE B-2 (cont'd)
SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM EXPOSURE PATHWAY AND/OR SAMPLE NUMBER OF REPRESENTATIVE SAMPLES AND SAMPLE LOCATIONS SAMPLING AND COLLECTION FREQUENCY TYPE/FREQUENCY*
OF ANALYSIS
- e. Fodder Crops Although not required by SGS/HCGS ODCM, a sample of crops normally used as cattle feed (silage) were collected from our milk farms as management audit samples
- 14F4, 3G1, 2G3, 13E3.
Annually (at harvest)
Gamma scan / on collection
- f. Soil Although not required by SGS/HCGS ODCM, samples of soil are collected as management audit samples Every 3 years
- 6S2, 2F9, 5F1, 10D1, 16E1, 13E3, 14F4, 2G3, 3G1 (2010-2013-2016)
Gamma scan / on collection (Samples were collected in 2010).
4.
AQUATIC ENVIRONMENT
- a. Surface Water One sample upstream: 1F2.
One sample downstream: 7E1.
One sample outfall: 11A1.
One sample cross-stream (mouth of Appoquinimink River):
12C1(2).
And an additional location in the Chesapeake & Delaware Canal: 16F1.
Monthly Gross Beta / monthly Gamma scan / monthly Tritium / monthly**
- b. Edible Fish One sample of each commercially and recreationally important species in vicinity of plant discharge area: 11A1.
One sample of same species in area not influenced by plant discharge: 12C1(2).
And an additional location downstream: 7E1.
Semi-annually Gamma scan (flesh) / on collection B-11
TABLE B-2 (cont'd)
SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM EXPOSURE PATHWAY AND/OR SAMPLE NUMBER OF REPRESENTATIVE SAMPLES AND SAMPLE LOCATIONS SAMPLING AND COLLECTION FREQUENCY TYPE/FREQUENCY*
OF ANALYSIS
- c. Blue Crabs
- d. Sediment One sample of each commercially and recreationally important species in vicinity of plant discharge area 11A1.
One sample of same species in area not influenced by plant discharge 12C1(2).
One sample from downstream area: 7E1.
One sample from cross-stream area and control location:
12C1(2).
One sample from outfall area: 11A1.
One sample from upstream, the C & D Canal: 16F1.
One sample from shoreline area: 6S2.
One sample from Cooling Tower Blowdown discharge:
15A1.
One sample south storm drain discharge line: 16A1.
Semi-annually Semi-annually Gamma scan (flesh) /on collection Gamma scan / on collection
- Except for Dosimeters, the quarterly analysis is performed on a composite of individual samples collected during the quarter.
- Includes new sampling locations - See Program Changes (1) While these milk locations are not within the 5 km range, they are the closest farms in the Site vicinity.
Since broad leaf vegetation is acceptable in lieu of milk collections, LTS personnel planted and harvested cabbage at three locations on Site (1S1, 15S1, 16S1) and one in Delaware (10D1).
(2)Station 12C1 was made the operational control (1975) for aquatic samples since the physical characteristics of this station more closely resemble those of the outfall area than do those at the upstream location originally chosen. This is due to the distance from Liston Point, which is the boundary between the Delaware River and Delaware Bay. As discussed extensively in the SGS/HCGS Pre-operational reports, the sampling locations further upstream show significantly lower background levels due to estuarine tidal flow.
B-12
MAP B-1 SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ON-SITE SAMPLING LOCATIONS B-13
MAP B-2 SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM OFF-SITE SAMPLING LOCATIONS B-14
APPENDIX C DATA TABLES C-1
Intentionally left blank C-2
TABLE C-1 CONCENTRATIONS OF GAMMA EMITTERS IN QUARTERLY COMPOSITES OF AIR PARTICULATES, 2013 Results in Units of 10-3 pCi/m3 +/- 2 Sigma STATION ID COLLECTION PERIOD
<----------GAMMA EMITTERS---------->
START STOP Be-7 K-40 Cs-134 Cs-137 SA-APT-14G1 (C) 01/02/13 - 04/01/13 69 +/- 27
< 31
< 2
< 2 04/01/13 - 07/01/13 151 +/- 32
< 31
< 2
< 2 07/01/13 - 09/30/13 96 +/- 27
< 20
< 2
< 1 09/30/13 - 12/30/13 105 +/- 26
< 21
< 1
< 1 AVERAGE*
105 +/- 68 SA-APT-16E1 01/02/13 - 04/01/13 78 +/- 31
< 21
< 1
< 1 04/01/13 - 07/01/13 111 +/- 47
< 16
< 2
< 2 07/01/13 - 09/30/13 146 +/- 32
< 31
< 1
< 1 09/30/13 - 12/30/13 108 +/- 30
< 11
< 2
< 2 AVERAGE*
110 +/- 56 SA-APT-16S1**
01/28/13 - 04/01/13 125 +/- 42
< 37
< 3
< 3 04/01/13 - 07/01/13 144 +/- 37 56 +/- 18
< 3
< 2 07/01/13 - 09/30/13 107 +/- 22
< 21
< 2
< 2 09/30/13 - 12/30/13 89 +/- 34
< 45
< 3
< 2 AVERAGE*
116 +/- 47 56 +/- 0 SA-APT-1F1 01/02/13 - 04/01/13 80 +/- 31
< 35
< 2
< 2 04/01/13 - 07/01/13 112 +/- 32
< 29
< 2
< 1 07/01/13 - 09/30/13 99 +/- 28
< 15
< 1
< 2 09/30/13 - 12/30/13 81 +/- 29
< 50
< 2
< 2 AVERAGE*
93 +/- 30 SA-APT-2F6 01/02/13 - 04/01/13 103 +/- 38
< 16
< 2
< 2 04/01/13 - 07/01/13 108 +/- 29
< 30
< 2
< 1 07/01/13 - 09/30/13 95 +/- 28
< 24
< 1
< 1 09/30/13 - 12/30/13 76 +/- 24
< 27
< 2
< 1 AVERAGE*
96 +/- 28
- THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES
- TEMPORARY SAMPLE LOCATION - SEE PROGRAM CHANGES SECTION FOR EXPLANATION (C) CONTROL STATION C-3
TABLE C-1 CONCENTRATIONS OF GAMMA EMITTERS IN QUARTERLY COMPOSITES OF AIR PARTICULATES, 2013 Results in Units of 10-3 pCi/m3 +/- 2 Sigma STATION ID COLLECTION PERIOD
<----------GAMMA EMITTERS---------->
START STOP Be-7 K-40 Cs-134 Cs-137 SA-APT-5D1 01/02/13 - 04/01/13 112 +/- 28
< 36
< 3
< 2 04/01/13 - 07/01/13 121 +/- 32
< 44
< 2
< 2 07/01/13 - 09/30/13 105 +/- 38
< 24
< 2
< 2 09/30/13 - 12/30/13 102 +/- 35
< 24
< 3
< 2 AVERAGE*
110 +/- 17 SA-APT-5S1 01/02/13 - 04/01/13 82 +/- 27
< 29
< 1
< 1 04/01/13 - 07/01/13 104 +/- 25
< 21
< 1
< 1 07/01/13 - 09/30/13 83 +/- 27
< 31
< 2
< 2 09/30/13 - 12/30/13 66 +/- 23
< 28
< 2
< 2 AVERAGE*
84 +/- 31 SA-APT-6S1**
01/28/13 - 04/01/13 70 +/- 25
< 23
< 2
< 2 04/01/13 - 07/01/13 159 +/- 28
< 22
< 2
< 1 07/01/13 - 09/30/13 109 +/- 37
< 41
< 2
< 2 09/30/13 - 12/30/13 120 +/- 27
< 32
< 1
< 1 AVERAGE*
115 +/- 74
- THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES
- TEMPORARY SAMPLE LOCATION - SEE PROGRAM CHANGES SECTION FOR EXPLANATION C-4
TABLE C-2 CONCENTRATIONS OF GROSS BETA EMITTERS IN AIR PARTICULATES, 2013 Results in units of 10-3 pCi/m3 +/- 2 sigma COLLECTION PERIOD CONTROL INDICATOR START STOP SA-APT-14G1 SA-APT-1F1 SA-APT-2F6 SA-APT-5D1 SA-APT-5S1 SA-APT-6S1**
01/02/13 - 01/07/13 25 +/- 5 27 +/- 5 24 +/- 4 30 +/- 5 21 +/- 4 (1) 01/07/13 - 01/14/13 21 +/- 4 23 +/- 4 23 +/- 3 22 +/- 4 20 +/- 3 (1) 01/14/13 - 01/21/13 16 +/- 3 15 +/- 3 11 +/- 3 16 +/- 3 11 +/- 3 (1) 01/21/13 - 01/28/13 17 +/- 3 13 +/- 3 17 +/- 3 12 +/- 3 14 +/- 3 (1) 01/28/13 - 02/04/13 22 +/- 4 21 +/- 3 20 +/- 3 21 +/- 4 19 +/- 3 24 +/- 3 02/04/13 - 02/11/13 20 +/- 4 17 +/- 3 16 +/- 3 16 +/- 3 13 +/- 3 10 +/- 2 02/11/13 - 02/19/13 13 +/- 2 14 +/- 2 13 +/- 2 11 +/- 2 13 +/- 2 7 +/- 1 02/19/13 - 02/27/13 8 +/- 3 10 +/- 3 8 +/- 3 6 +/- 3 7 +/- 3 7 +/- 2 02/27/13 - 03/04/13 10 +/- 4 8 +/- 4 9 +/- 4 7 +/- 4 6 +/- 4 6 +/- 3 03/04/13 - 03/11/13 8 +/- 3 7 +/- 3 6 +/- 3 7 +/- 3 8 +/- 3 9 +/- 3 03/11/13 - 03/18/13 16 +/- 4 16 +/- 4 14 +/- 3 17 +/- 4 11 +/- 3 13 +/- 3 03/18/13 - 03/25/13 9 +/- 3 5 +/- 3 7 +/- 3 7 +/- 3 5 +/- 3 10 +/- 3 03/25/13 - 04/01/13 8 +/- 3 7 +/- 3 7 +/- 2 8 +/- 3 8 +/- 2 8 +/- 2 04/01/13 - 04/08/13 22 +/- 4 15 +/- 3 16 +/- 3 16 +/- 3 10 +/- 3 18 +/- 3 04/08/13 - 04/15/13 14 +/- 3 12 +/- 3 10 +/- 3 11 +/- 3 13 +/- 3 13 +/- 3 04/15/13 - 04/22/13 10 +/- 4 10 +/- 4 10 +/- 3 8 +/- 3 8 +/- 3 8 +/- 3 04/22/13 - 04/29/13 15 +/- 3 13 +/- 3 14 +/- 3 16 +/- 3 14 +/- 3 17 +/- 3 04/29/13 - 05/06/13 9 +/- 3 10 +/- 3 9 +/- 3 8 +/- 3 9 +/- 3 7 +/- 3 05/06/13 - 05/13/13 8 +/- 3 7 +/- 3 8 +/- 3 7 +/- 3 7 +/- 3 8 +/- 3 05/13/13 - 05/20/13 14 +/- 3 13 +/- 3 12 +/- 3 15 +/- 4 12 +/- 3 12 +/- 3 05/20/13 - 05/28/13 13 +/- 3 10 +/- 3 9 +/- 3 10 +/- 3 10 +/- 3 11 +/- 3 05/28/13 - 06/03/13 17 +/- 4 16 +/- 4 15 +/- 4 16 +/- 4 16 +/- 4 12 +/- 3 06/03/13 - 06/10/13 8 +/- 3 7 +/- 3 10 +/- 3 7 +/- 3 6 +/- 3 8 +/- 3 06/10/13 - 06/17/13 14 +/- 3 13 +/- 3 11 +/- 3 12 +/- 3 14 +/- 3 16 +/- 3 06/17/13 - 06/24/13 12 +/- 3 10 +/- 3 10 +/- 3 7 +/- 3 6 +/- 3 9 +/- 3 06/24/13 - 07/01/13 14 +/- 3 11 +/- 3 13 +/- 3 10 +/- 3 6 +/- 3 12 +/- 3 07/01/13 - 07/08/13 8 +/- 3 7 +/- 3 6 +/- 3 6 +/- 3 6 +/- 2 7 +/- 2 07/08/13 - 07/15/13 13 +/- 3 13 +/- 3 12 +/- 3 9 +/- 3 7 +/- 3 14 +/- 7 07/15/13 - 07/22/13 13 +/- 3 13 +/- 3 14 +/- 3 15 +/- 3 12 +/- 3 14 +/- 3 07/22/13 - 07/29/13 13 +/- 3 12 +/- 3 12 +/- 3 13 +/- 3 11 +/- 3 10 +/- 3 07/29/13 - 08/06/13 16 +/- 3 14 +/- 3 15 +/- 3 17 +/- 3 15 +/- 3 18 +/- 3 08/06/13 - 08/13/13 16 +/- 3 13 +/- 3 16 +/- 3 16 +/- 3 13 +/- 3 15 +/- 3 08/13/13 - 08/19/13 10 +/- 3 10 +/- 3 12 +/- 3 10 +/- 3 11 +/- 3 9 +/- 3 08/19/13 - 08/26/13 13 +/- 3 12 +/- 3 10 +/- 3 10 +/- 3 9 +/- 3 9 +/- 3 08/26/13 - 09/03/13 19 +/- 3 18 +/- 3 19 +/- 3 16 +/- 3 18 +/- 3 15 +/- 3 09/03/13 - 09/09/13 17 +/- 3 15 +/- 3 16 +/- 3 16 +/- 3 14 +/- 3 16 +/- 3 09/09/13 - 09/16/13 20 +/- 3 21 +/- 3 20 +/- 3 19 +/- 3 22 +/- 4 19 +/- 3 09/16/13 - 09/23/13 12 +/- 3 15 +/- 5 13 +/- 3 11 +/- 3 11 +/- 3 14 +/- 3 09/23/13 - 09/30/13 11 +/- 3 9 +/- 3 11 +/- 3 10 +/- 3 8 +/- 3 12 +/- 3 09/30/13 - 10/08/13 26 +/- 3 25 +/- 4 29 +/- 3 26 +/- 4 22 +/- 3 26 +/- 3 10/08/13 - 10/16/13 16 +/- 3 16 +/- 3 16 +/- 3 16 +/- 3 12 +/- 3 16 +/- 3 10/16/13 - 10/21/13 19 +/- 4 15 +/- 4 11 +/- 4 13 +/- 4 16 +/- 4 15 +/- 4 10/21/13 - 10/28/13 16 +/- 3 10 +/- 3 13 +/- 3 16 +/- 3 9 +/- 3 12 +/- 3 10/28/13 - 11/04/13 18 +/- 3 21 +/- 4 22 +/- 3 17 +/- 3 18 +/- 3 24 +/- 4 11/04/13 - 11/12/13 13 +/- 3 14 +/- 3 15 +/- 3 15 +/- 3 13 +/- 3 16 +/- 3 11/12/13 - 11/18/13 17 +/- 4 12 +/- 3 10 +/- 3 15 +/- 4 13 +/- 3 13 +/- 3 11/18/13 - 11/25/13 9 +/- 3 8 +/- 3 6 +/- 2 8 +/- 3 6 +/- 2 10 +/- 3 11/25/13 - 12/02/13 17 +/- 3 15 +/- 3 14 +/- 3 12 +/- 3 11 +/- 3 16 +/- 3 12/02/13 - 12/09/13 20 +/- 4 17 +/- 3 21 +/- 4 15 +/- 4 18 +/- 3 14 +/- 3 12/09/13 - 12/16/13 22 +/- 4 16 +/- 3 20 +/- 3 20 +/- 3 16 +/- 3 18 +/- 3 12/16/13 - 12/23/13 19 +/- 4 17 +/- 3 19 +/- 3 20 +/- 4 15 +/- 3 20 +/- 4 12/23/13 - 12/30/13 13 +/- 3 18 +/- 3 13 +/- 3 12 +/- 3 14 +/- 3 12 +/- 3 AVERAGE*
15 +/- 9 14 +/- 10 14 +/- 10 13 +/- 10 12 +/- 9 13 +/- 9
- THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES
- TEMPORARY SAMPLE LOCATION - SEE PROGRAM CHANGES SECTION FOR EXPLANATION (1) SEE PROGRAM CHANGES SECTION FOR EXPLANATION C-5
TABLE C-2 CONCENTRATIONS OF GROSS BETA EMITTERS IN AIR PARTICULATES, 2013 Results in units of 10-3 pCi/m3 +/- 2 sigma COLLECTION PERIOD START STOP SA-APT-16E1 SA-APT-16S1**
01/02/13 - 01/07/13 23 +/- 4 (1) 01/07/13 - 01/14/13 23 +/- 3 (1) 01/14/13 - 01/21/13 15 +/- 3 (1) 01/21/13 - 01/28/13 13 +/- 3 (1) 01/28/13 - 02/04/13 19 +/- 3 22 +/- 3 02/04/13 - 02/11/13 19 +/- 3 14 +/- 3 02/11/13 - 02/19/13 12 +/- 2 10 +/- 2 02/19/13 - 02/27/13 6 +/- 3 11 +/- 3 02/27/13 - 03/04/13 8 +/- 4 12 +/- 4 03/04/13 - 03/11/13 9 +/- 3 7 +/- 3 03/11/13 - 03/18/13 12 +/- 3 17 +/- 3 03/18/13 - 03/25/13 9 +/- 3 9 +/- 3 03/25/13 - 04/01/13 10 +/- 3 8 +/- 2 04/01/13 - 04/08/13 17 +/- 3 16 +/- 3 04/08/13 - 04/15/13 11 +/- 3 12 +/- 3 04/15/13 - 04/22/13 11 +/- 4 12 +/- 3 04/22/13 - 04/29/13 15 +/- 3 17 +/- 3 04/29/13 - 05/06/13 15 +/- 4
< 17 (2) 05/06/13 - 05/13/13 8 +/- 3 8 +/- 3 05/13/13 - 05/20/13 12 +/- 3 14 +/- 3 05/20/13 - 05/28/13 9 +/- 2 13 +/- 3 05/28/13 - 06/03/13 14 +/- 4 12 +/- 3 06/03/13 - 06/10/13 9 +/- 3 8 +/- 3 06/10/13 - 06/17/13 13 +/- 3 12 +/- 3 06/17/13 - 06/24/13 7 +/- 3 9 +/- 3 06/24/13 - 07/01/13 10 +/- 3 11 +/- 3 07/01/13 - 07/08/13 8 +/- 3 9 +/- 3 07/08/13 - 07/15/13 12 +/- 3 14 +/- 3 07/15/13 - 07/22/13 13 +/- 3 20 +/- 3 07/22/13 - 07/29/13 12 +/- 3 12 +/- 3 07/29/13 - 08/06/13 13 +/- 3 17 +/- 3 08/06/13 - 08/13/13 15 +/- 3 17 +/- 3 08/13/13 - 08/19/13 12 +/- 3 12 +/- 3 08/19/13 - 08/26/13 11 +/- 3 16 +/- 3 08/26/13 - 09/03/13 21 +/- 3 19 +/- 3 09/03/13 - 09/09/13 16 +/- 3 18 +/- 3 09/09/13 - 09/16/13 21 +/- 4 26 +/- 4 09/16/13 - 09/23/13 11 +/- 3 13 +/- 3 09/23/13 - 09/30/13 10 +/- 3 11 +/- 3 09/30/13 - 10/08/13 26 +/- 4 29 +/- 4 10/08/13 - 10/16/13 15 +/- 3 22 +/- 4 10/16/13 - 10/21/13 17 +/- 4 15 +/- 4 10/21/13 - 10/28/13 13 +/- 3 13 +/- 3 10/28/13 - 11/04/13 20 +/- 4 24 +/- 4 11/04/13 - 11/12/13 14 +/- 3 12 +/- 3 11/12/13 - 11/18/13 12 +/- 6 13 +/- 4 11/18/13 - 11/25/13 11 +/- 3 8 +/- 3 11/25/13 - 12/02/13 16 +/- 3 15 +/- 3 12/02/13 - 12/09/13 19 +/- 3 18 +/- 3 12/09/13 - 12/16/13 16 +/- 3 18 +/- 3 12/16/13 - 12/23/13 23 +/- 3 23 +/- 4 12/23/13 - 12/30/13 16 +/- 3 14 +/- 3 AVERAGE*
14 +/- 9 14 +/- 10
- THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES
- TEMPORARY SAMPLE LOCATION - SEE PROGRAM CHANGES SECTION FOR EXPLANATION (1) SEE PROGRAM CHANGES SECTION FOR EXPLANATION (2) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION INDICATOR C-6
TABLE C-3 CONCENTRATIONS OF IODINE-131* IN FILTERED AIR, 2013 Results in units of 10-3 pCi/m3 +/- 2 sigma COLLECTION PERIOD CONTROL INDICATOR START STOP SA-AIO-14G1 SA-AIO-1F1 SA-AIO-2F6 SA-AIO-5D1 SA-AIO-5S1 SA-AIO-6S1**
01/02/13 - 01/07/13
< 31
< 27
< 25
< 31
< 25 (1) 01/07/13 - 01/14/13
< 23
< 20
< 19
< 23
< 18 (1) 01/14/13 - 01/21/13
< 14
< 15
< 14
< 13
< 14 (1) 01/21/13 - 01/28/13
< 20
< 16
< 15
< 20
< 15 (1) 01/28/13 - 02/04/13
< 17
< 19
< 19
< 20
< 18
< 12 02/04/13 - 02/11/13
< 21
< 19
< 19
< 19
< 18
< 11 02/11/13 - 02/19/13
< 10
< 12
< 12
< 12
< 11
< 5 02/19/13 - 02/27/13
< 30
< 26
< 26
< 27
< 28
< 23 02/27/13 - 03/04/13
< 28
< 25
< 24
< 26
< 24
< 24 03/04/13 - 03/11/13
< 8
< 8
< 7
< 8
< 7
< 8 03/11/13 - 03/18/13
< 14
< 16
< 15
< 17
< 15
< 14 03/18/13 - 03/25/13
< 21
< 28
< 27
< 26
< 25
< 21 03/25/13 - 04/01/13
< 21
< 16
< 15
< 15
< 14
< 20 04/01/13 - 04/08/13
< 17
< 15
< 14
< 15
< 13
< 15 04/08/13 - 04/15/13
< 20
< 16
< 15
< 16
< 14
< 18 04/15/13 - 04/22/13
< 17
< 16
< 15
< 15
< 14
< 15 04/22/13 - 04/29/13
< 18
< 13
< 15
< 15
< 14
< 18 04/29/13 - 05/06/13
< 19
< 20
< 21
< 20
< 20
< 17 05/06/13 - 05/13/13
< 18
< 22
< 22
< 23
< 23
< 16 05/13/13 - 05/20/13
< 16
< 17
< 18
< 18
< 17
< 14 05/20/13 - 05/28/13
< 25
< 38
< 38
< 39
< 38
< 22 05/28/13 - 06/03/13
< 39
< 30
< 30
< 31
< 29
< 32 06/03/13 - 06/10/13
< 29
< 38
< 38
< 37
< 36
< 26 06/10/13 - 06/17/13
< 25
< 23
< 23
< 23
< 21
< 22 06/17/13 - 06/24/13
< 17
< 22
< 21
< 20
< 19
< 18 06/24/13 - 07/01/13
< 38
< 42
< 41
< 39
< 37
< 34 07/01/13 - 07/08/13
< 37
< 44
< 45
< 43
< 40
< 32 07/08/13 - 07/15/13
< 17
< 23
< 23
< 23
< 22
< 46 07/15/13 - 07/22/13
< 30
< 31
< 32
< 34
< 33
< 27 07/22/13 - 07/29/13
< 28
< 28
< 28
< 29
< 31
< 31 07/29/13 - 08/06/13
< 25
< 17
< 17
< 18
< 19
< 27 08/06/13 - 08/13/13
< 29
< 35
< 35
< 36
< 32
< 31 08/13/13 - 08/19/13
< 29
< 32
< 32
< 35
< 31
< 30 08/19/13 - 08/26/13
< 26
< 28
< 28
< 30
< 27
< 26 08/26/13 - 09/03/13
< 59
< 47
< 46
< 52
< 50
< 59 09/03/13 - 09/09/13
< 45
< 41
< 41
< 45
< 44
< 46 09/09/13 - 09/16/13
< 43
< 42
< 41
< 46
< 46
< 41 09/16/13 - 09/23/13
< 32
< 55
< 30
< 33
< 32
< 38 09/23/13 - 09/30/13
< 26
< 33
< 29
< 32
< 30
< 27 09/30/13 - 10/08/13
< 34
< 43
< 38
< 43
< 40
< 35 10/08/13 - 10/16/13
< 50
< 48
< 41
< 47
< 42
< 53 10/16/13 - 10/21/13
< 38
< 46
< 41
< 47
< 43
< 40 10/21/13 - 10/28/13
< 42
< 39
< 35
< 39
< 35
< 44 10/28/13 - 11/04/13
< 55
< 69
< 60
< 69
< 61
< 56 11/04/13 - 11/12/13
< 30
< 32
< 28
< 32
< 29
< 30 11/12/13 - 11/18/13
< 32
< 37
< 35
< 39
< 35
< 32 11/18/13 - 11/25/13
< 38
< 41
< 40
< 44
< 39
< 38 11/25/13 - 12/02/13
< 50
< 43
< 40
< 44
< 40
< 47 12/02/13 - 12/09/13
< 45
< 31
< 31
< 33
< 29
< 41 12/09/13 - 12/16/13
< 68
< 56
< 59
< 62
< 58
< 68 12/16/13 - 12/23/13
< 55
< 59
< 59
< 63
< 56
< 50 12/23/13 - 12/30/13
< 32
< 29
< 27
< 29
< 26
< 29 AVERAGE
- IODINE-131 RESULTS ARE CORRECTED FOR DECAY TO STOP DATE OF COLLECTION PERIOD & ANALYZED TO AN LLD OF 70 10-3 pCi/m3
- TEMPORARY SAMPLE LOCATION - SEE PROGRAM CHANGES SECTION FOR EXPLANATION (1) SEE PROGRAM CHANGES SECTION FOR EXPLANATION C-7
TABLE C-3 CONCENTRATIONS OF IODINE-131* IN FILTERED AIR, 2013 Results in units of 10-3 pCi/m3 +/- 2 sigma COLLECTION PERIOD INDICATOR START STOP SA-AIO-16E1 SA-AIO-16S1**
01/02/13 -
01/07/13
< 29 (1) 01/07/13 -
01/14/13
< 21 (1) 01/14/13 -
01/21/13
< 13 (1) 01/21/13 -
01/28/13
< 19 (1) 01/28/13 -
02/04/13
< 16
< 12 02/04/13 -
02/11/13
< 19
< 16 02/11/13 -
02/19/13
< 9
< 7 02/19/13 -
02/27/13
< 29
< 6 02/27/13 -
03/04/13
< 27
< 25 03/04/13 -
03/11/13
< 7
< 7 03/11/13 -
03/18/13
< 14
< 13 03/18/13 -
03/25/13
< 21
< 21 03/25/13 -
04/01/13
< 21
< 19 04/01/13 -
04/08/13
< 17
< 15 04/08/13 -
04/15/13
< 20
< 18 04/15/13 -
04/22/13
< 18
< 15 04/22/13 -
04/29/13
< 20
< 18 04/29/13 -
05/06/13
< 20
< 83 (2) 05/06/13 -
05/13/13
< 17
< 16 05/13/13 -
05/20/13
< 15
< 14 05/20/13 -
05/28/13
< 23
< 22 05/28/13 -
06/03/13
< 36
< 32 06/03/13 -
06/10/13
< 26
< 26 06/10/13 -
06/17/13
< 25
< 22 06/17/13 -
06/24/13
< 17
< 16 06/24/13 -
07/01/13
< 38
< 33 07/01/13 -
07/08/13
< 38
< 33 07/08/13 -
07/15/13
< 17
< 17 07/15/13 -
07/22/13
< 30
< 29 07/22/13 -
07/29/13
< 29
< 27 07/29/13 -
08/06/13
< 25
< 26 08/06/13 -
08/13/13
< 29
< 30 08/13/13 -
08/19/13
< 30
< 30 08/19/13 -
08/26/13
< 27
< 27 08/26/13 -
09/03/13
< 61
< 59 09/03/13 -
09/09/13
< 46
< 44 09/09/13 -
09/16/13
< 45
< 43 09/16/13 -
09/23/13
< 33
< 33 09/23/13 -
09/30/13
< 28
< 27 09/30/13 -
10/08/13
< 35
< 35 10/08/13 -
10/16/13
< 53
< 67 10/16/13 -
10/21/13
< 39
< 37 10/21/13 -
10/28/13
< 44
< 42 10/28/13 -
11/04/13
< 54
< 52 11/04/13 -
11/12/13
< 29
< 30 11/12/13 -
11/18/13
< 38
< 33 11/18/13 -
11/25/13
< 39
< 39 11/25/13 -
12/02/13
< 42
< 44 12/02/13 -
12/09/13
< 37
< 38 12/09/13 -
12/16/13
< 61
< 64 12/16/13 -
12/23/13
< 44
< 47 12/23/13 -
12/30/13
< 27
< 31 AVERAGE
- IODINE-131 RESULTS ARE CORRECTED FOR DECAY TO STOP DATE OF COLLECTION PERIOD & ANALYZED TO AN LLD OF 70 10-3 pCi/m3.
- TEMPORARY SAMPLE LOCATION - SEE PROGRAM CHANGES SECTION FOR EXPLANATION (1) SEE PROGRAM CHANGES SECTION FOR EXPLANATION (2) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-8
TABLE C-4 DIRECT RADIATION MEASUREMENTS - QUARTERLY DOSIMITRY RESULTS*, 2013 Results in units of mR/standard quarter STATION ID AVERAGE JAN - MAR APR - JUN JUL - SEP OCT - DEC
+/- 2 S.D.
SA-IDM-1F1 18.3. 4.1 16.0 20.0 17.0 20.0 SA-IDM-2E1 13.8 +/- 2.5 12.0 14.0 14.0 15.0 SA-IDM-2F2 13.5 +/- 4.8 12.0 16.0 11.0 15.0 SA-IDM-2F5 14.5 +/- 3.5 13.0 14.0 14.0 17.0 SA-IDM-2F6 13.0 +/- 3.7 11.0 14.0 12.0 15.0 SA-IDM-2S2 14.5 +/- 3.8 15.0 17.0 13.0 13.0 SA-IDM-2S4 15.0 +/- 4.3 12.0 15.0 16.0 17.0 SA-IDM-3E1 11.8 +/- 3.0 11.0 11.0 11.0 14.0 SA-IDM-3F2 12.8 +/- 2.5 11.0 13.0 13.0 14.0 SA-IDM-3F3 12.3 +/- 3.0 11.0 13.0 11.0 14.0 SA-IDM-3S1 11.3 +/- 3.0 10.0 13.0 10.0 12.0 SA-IDM-4D2 15.0 +/- 3.7 13.0 14.0 16.0 17.0 SA-IDM-4F2 12.8 +/- 3.0 11.0 14.0 12.0 14.0 SA-IDM-4S1 12.5 +/- 2.6 11.0 13.0 12.0 14.0 SA-IDM-5D1 13.8 +/- 3.4 12.0 14.0 13.0 16.0 SA-IDM-5F1 12.5 +/- 2.6 11.0 12.0 13.0 14.0 SA-IDM-5S1 12.3 +/- 3.0 11.0 13.0 11.0 14.0 SA-IDM-6F1 11.3 +/- 1.0 11.0 11.0 11.0 12.0 SA-IDM-6S2 17.8 +/- 3.8 15.0 18.0 19.0 19.0 SA-IDM-7F2 9.7 +/- 2.3 9.0 11.0 9.0 (1)
SA-IDM-7S1 10.8 +/- 2.5 9.0 11.0 11.0 12.0 SA-IDM-8F1***
14.8 +/- 6.2 13.0 12.0 15.0 19.0 SA-IDM-8S1***
10.3 +/- 5.5 12.0 7.0 9.0 13.0 SA-IDM-9F1 17.3 +/- 5.5 14.0 19.0 16.0 20.0 SA-IDM-9S1***
10.8 +/- 4.4 13.0 8.0 10.0 12.0 SA-IDM-10D1 15.0 +/- 3.7 13.0 14.0 16.0 17.0 SA-IDM-10F2 15.0 +/- 3.7 13.0 16.0 14.0 17.0 SA-IDM-10S1 11.8 +/- 2.5 10.0 13.0 12.0 12.0 SA-IDM-11E2 16.3 +/- 5.3 14.0 18.0 14.0 19.0 SA-IDM-11F1 15.3 +/- 4.1 13.0 17.0 14.0 17.0 SA-IDM-11S1 10.8 +/- 3.0 9.0 12.0 10.0 12.0 SA-IDM-12E1 15.8 +/- 4.4 13.0 17.0 15.0 18.0 SA-IDM-12F1 14.5 +/- 4.2 14.0 15.0 12.0 17.0 SA-IDM-12S1***
13.5 +/- 4.2 12.0 (1)
(1) 15.0 SA-IDM-13E1 12.8 +/- 4.1 11.0 14.0 11.0 15.0 SA-IDM-13F2 14.3 +/- 5.3 12.0 17.0 12.0 16.0 SA-IDM-13F3 14.0 +/- 4.3 12.0 14.0 13.0 17.0 SA-IDM-13F4 16.3 +/- 3.4 14.0 17.0 16.0 18.0 SA-IDM-13S1***
18.0 +/- 8.5 15.0 (1)
(1) 21.0 SA-IDM-14D1 13.5 +/- 2.6 12.0 13.0 14.0 15.0 SA-IDM-14F2 15.8 +/- 3.4 14.0 16.0 15.0 18.0 SA-IDM-14S1***
17.8 +/- 4.7 21.0 18.0 16.0 16.0 SA-IDM-15D1 15.3 +/- 4.4 14.0 16.0 13.0 18.0 SA-IDM-15F3 14.8 +/- 3.0 13.0 16.0 14.0 16.0 SA-IDM-15S1 11.8 +/- 3.0 10.0 13.0 11.0 13.0 SA-IDM-15S2 13.0 +/- 2.3 12.0 14.0 12.0 14.0 SA-IDM-16E1 15.0 +/- 2.8 15.0 16.0 13.0 16.0 SA-IDM-16F2 13.3 +/- 4.4 12.0 14.0 11.0 16.0 SA-IDM-16S1 14.3 +/- 3.4 12.0 14.0 15.0 16.0 SA-IDM-16S3***
13.0 +/- 7.2 17.0 12.0 10.0 (1)
SA-IDM-1G3 (C) 13.8 +/- 3.4 12.0 14.0 13.0 16.0 SA-IDM-3G1 (C) 14.3 +/- 3.0 13.0 15.0 13.0 16.0 SA-IDM-3H1 (C) 12.0 +/- 4.6 10.0 14.0 10.0 14.0 SA-IDM-10G1 (C) 15.3 +/- 3.4 13.0 16.0 15.0 17.0 SA-IDM-14G1 (C) 15.3 +/- 3.0 14.0 16.0 14.0 17.0 SA-IDM-16G1 (C) 14.0 +/- 3.7 12.0 15.0 13.0 16.0 SA-IDM-1S1 **
34.3 +/- 5.0 33.0 38.0 33.0 33.0 SA-IDM-16S2 **
37.0 +/- 5.4 38.0 38.0 33.0 39.0
- QUARTERLY ELEMENT TLD RESULTS BY MIRION
- SAMPLE RESULTS ARE AFFECTED BY THE ISFSI
- NEW SAMPLE LOCATION - SEE PROGRAM CHANGES SECTION FOR EXPLANATION (C) CONTROL STATION (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-9
TABLE C-5 CONCENTRATIONS OF IODINE-131* AND GAMMA EMITTERS IN MILK, 2013 Results in units of pCi/L +/- 2 sigma STATION ID COLLECTION PERIOD
<----------GAMMA EMITTERS---------->
START STOP I-131 K-40 Cs-134 Cs-137 BaLa-140 Ra-226 SA-MLK-13E3 01/20/13 - 01/21/13
< 0.7 1388 +/- 124
< 5
< 6
< 8
< 140 SA-MLK-14F4 01/20/13 - 01/21/13
< 0.7 1254 +/- 181
< 8
< 9
< 12
< 169 SA-MLK-2G3 01/20/13 - 01/21/13
< 0.7 1387 +/- 155
< 5
< 6
< 7
< 182 SA-MLK-3G1 (C) 01/20/13 - 01/21/13
< 0.7 1241 +/- 162
< 6
< 7
< 9
< 168 SA-MLK-13E3 02/03/13 - 02/04/13
< 0.6 1312 +/- 132
< 5
< 6
< 9
< 128 SA-MLK-14F4 02/03/13 - 02/04/13
< 0.9 1289 +/- 117
< 5
< 5
< 7
< 137 SA-MLK-2G3 02/03/13 - 02/04/13
< 0.9 1173 +/- 158
< 5
< 6
< 8
< 135 SA-MLK-3G1 (C) 02/03/13 - 02/04/13
< 0.6 1156 +/- 117
< 6
< 6
< 8
< 184 SA-MLK-13E3 03/03/13 - 03/04/13
< 0.8 1217 +/- 116
< 4
< 5
< 8
< 111 SA-MLK-14F4 03/03/13 - 03/04/13
< 0.8 1392 +/- 117
< 5
< 5
< 8
< 124 SA-MLK-2G3 03/03/13 - 03/04/13
< 0.6 1381 +/- 118
< 5
< 4
< 9
< 121 SA-MLK-3G1 (C) 03/03/13 - 03/04/13
< 0.9 1190 +/- 112
< 4
< 4
< 8
< 110 SA-MLK-13E3 04/08/13 - 04/08/13
< 0.4 1409 +/- 160
< 5
< 6
< 8
< 151 SA-MLK-14F4 04/08/13 - 04/08/13
< 0.5 1200 +/- 174
< 8
< 9
< 14
< 167 SA-MLK-2G3 04/08/13 - 04/08/13
< 0.5 1235 +/- 155
< 7
< 7
< 9
< 153 SA-MLK-3G1 (C) 04/08/13 - 04/08/13
< 0.5 1403 +/- 138
< 7
< 9
< 12
< 199 SA-MLK-13E3 04/21/13 - 04/22/13
< 0.4 1302 +/- 129
< 5
< 6
< 11
< 119 SA-MLK-14F4 04/21/13 - 04/22/13
< 0.6 1313 +/- 123
< 5
< 5
< 9
< 133 SA-MLK-2G3 04/21/13 - 04/22/13
< 0.5 1181 +/- 107
< 4
< 4
< 9
< 92 SA-MLK-3G1 (C) 04/21/13 - 04/22/13
< 0.5 1417 +/- 125
< 6
< 7
< 13
< 159 SA-MLK-13E3 05/05/13 - 05/06/13
< 0.6 1383 +/- 140
< 5
< 6
< 9
< 130 SA-MLK-14F4 05/05/13 - 05/06/13
< 0.7 1441 +/- 117
< 5
< 6
< 8
< 141 SA-MLK-2G3 05/05/13 - 05/06/13
< 0.7 1251 +/- 104
< 4
< 5
< 6
< 117 SA-MLK-3G1 (C) 05/05/13 - 05/06/13
< 0.8 1362 +/- 130
< 6
< 6
< 9
< 160 SA-MLK-13E3 05/19/13 - 05/20/13
< 0.5 1243 +/- 175
< 7
< 10
< 11
< 168 SA-MLK-14F4 05/19/13 - 05/20/13
< 0.5 1359 +/- 148
< 6
< 6
< 10
< 150 SA-MLK-2G3 05/19/13 - 05/20/13
< 0.4 1440 +/- 130
< 6
< 6
< 5
< 144 SA-MLK-3G1 (C) 05/19/13 - 05/20/13
< 0.5 1328 +/- 142
< 5
< 6
< 10
< 136 SA-MLK-13E3 06/02/13 - 06/03/13
< 0.6 1425 +/- 127
< 5
< 5
< 8
< 132 SA-MLK-14F4 06/02/13 - 06/03/13
< 0.9 1408 +/- 124
< 4
< 5
< 8
< 127 SA-MLK-2G3 06/02/13 - 06/03/13
< 0.8 1398 +/- 99
< 4
< 3
< 5
< 100 SA-MLK-3G1 (C) 06/02/13 - 06/03/13
< 0.5 1266 +/- 97
< 4
< 4
< 6
< 118 SA-MLK-13E3 06/16/13 - 06/17/13
< 0.8 1268 +/- 171
< 5
< 8
< 13
< 191 SA-MLK-14F4 06/16/13 - 06/17/13
< 0.9 1564 +/- 172
< 6
< 8
< 9
< 163 SA-MLK-2G3 06/16/13 - 06/17/13
< 0.8 1428 +/- 182
< 6
< 7
< 11
< 193 SA-MLK-3G1 (C) 06/16/13 - 06/17/13
< 0.9 1291 +/- 150
< 6
< 6
< 7
< 176 SA-MLK-13E3 07/07/13 - 07/08/13
< 0.7 1221 +/- 144
< 5
< 7
< 8
< 141 SA-MLK-14F4 07/07/13 - 07/08/13
< 0.6 1362 +/- 129
< 5
< 6
< 9
< 140 SA-MLK-2G3 07/07/13 - 07/08/13
< 0.5 1263 +/- 162
< 7
< 8
< 10
< 150 SA-MLK-3G1 (C) 07/07/13 - 07/08/13
< 0.6 1308 +/- 134
< 6
< 6
< 13
< 163
- IODINE-131 RESULTS ARE CORRECTED FOR DECAY TO STOP DATE OF COLLECTION PERIOD & ANALYZED TO AN LLD OF 1.0 pCi/L (C) CONTROL STATION C-10
TABLE C-5 CONCENTRATIONS OF IODINE-131* AND GAMMA EMITTERS IN MILK, 2013 Results in units of pCi/L +/- 2 sigma STATION ID COLLECTION PERIOD
<----------GAMMA EMITTERS---------->
START STOP I-131 K-40 Cs-134 Cs-137 BaLa-140 Ra-226 SA-MLK-13E3 07/21/13 - 07/22/13
< 0.9 1389 +/- 152
< 6
< 7
< 10
< 166 SA-MLK-14F4 07/21/13 - 07/22/13
< 0.7 1488 +/- 159
< 5
< 7
< 9
< 150 SA-MLK-2G3 07/21/13 - 07/22/13
< 0.6 1480 +/- 150
< 5
< 6
< 9
< 166 SA-MLK-3G1 (C) 07/21/13 - 07/22/13
< 0.8 1349 +/- 131
< 5
< 6
< 9
< 150 SA-MLK-13E3 08/18/13 - 08/19/13
< 0.8 1396 +/- 102
< 4
< 5
< 7
< 110 SA-MLK-14F4 08/18/13 - 08/19/13
< 0.8 1312 +/- 103
< 4
< 5
< 7
< 115 SA-MLK-2G3 08/18/13 - 08/19/13
< 0.8 1383 +/- 103
< 4
< 5
< 7
< 103 SA-MLK-3G1 (C) 08/18/13 - 08/19/13
< 0.7 1297 +/- 105
< 3
< 4
< 7
< 86 SA-MLK-13E3 08/25/13 - 08/26/13
< 0.8 1273 +/- 182
< 7
< 8
< 11
< 167 SA-MLK-14F4 08/25/13 - 08/26/13
< 0.9 1256 +/- 162
< 7
< 8
< 9
< 159 SA-MLK-2G3 08/25/13 - 08/26/13
< 0.9 1553 +/- 173
< 7
< 6
< 11
< 156 SA-MLK-3G1 (C) 08/25/13 - 08/26/13
< 0.7 1268 +/- 146
< 6
< 6
< 12
< 133 SA-MLK-13E3 09/02/13 - 09/03/13
< 0.7 1277 +/- 131
< 4
< 5
< 11
< 118 SA-MLK-14F4 09/02/13 - 09/03/13
< 0.8 1530 +/- 149
< 6
< 6
< 13
< 149 SA-MLK-2G3 09/02/13 - 09/03/13
< 0.7 1261 +/- 146
< 5
< 6
< 9
< 145 SA-MLK-3G1 (C) 09/02/13 - 09/03/13
< 0.7 1194 +/- 136
< 6
< 6
< 10
< 151 SA-MLK-13E3 09/15/13 - 09/16/13
< 0.6 1468 +/- 170
< 7
< 9
< 12
< 173 SA-MLK-14F4 09/15/13 - 09/16/13
< 0.7 1506 +/- 187
< 7
< 7
< 9
< 155 SA-MLK-2G3 09/15/13 - 09/16/13
< 0.7 1397 +/- 160
< 7
< 7
< 12
< 166 SA-MLK-3G1 (C) 09/15/13 - 09/16/13
< 0.7 1188 +/- 160
< 6
< 6
< 12
< 150 SA-MLK-13E3 10/07/13 - 10/08/13
< 0.8 1162 +/- 143
< 6
< 7
< 13
< 164 SA-MLK-14F4 10/07/13 - 10/08/13
< 0.7 1315 +/- 138
< 6
< 8
< 12
< 166 SA-MLK-2G3 10/07/13 - 10/08/13
< 0.7 1401 +/- 162
< 6
< 7
< 9
< 186 SA-MLK-3G1 (C) 10/07/13 - 10/08/13
< 0.6 1325 +/- 174
< 5
< 7
< 9
< 165 SA-MLK-13E3 10/20/13 - 10/21/13
< 0.5 1388 +/- 172
< 7
< 8
< 8
< 176 SA-MLK-14F4 10/20/13 - 10/21/13
< 0.6 1368 +/- 164
< 6
< 6
< 14
< 149 SA-MLK-2G3 10/20/13 - 10/21/13
< 0.6 1302 +/- 171
< 7
< 8
< 11
< 182 SA-MLK-3G1 (C) 10/20/13 - 10/21/13
< 0.5 1149 +/- 166
< 5
< 6
< 14
< 122 SA-MLK-13E3 11/17/13 - 11/18/13
< 0.7 1328 +/- 106
< 3
< 4
< 11
< 69 SA-MLK-14F4 11/17/13 - 11/18/13
< 0.7 1444 +/- 91
< 3
< 4
< 11
< 88 SA-MLK-2G3 11/17/13 - 11/18/13
< 0.7 1300 +/- 95
< 4
< 4
< 11
< 102 SA-MLK-3G1 (C) 11/17/13 - 11/18/13
< 0.7 1222 +/- 101
< 3
< 3
< 11
< 87 SA-MLK-13E3 11/24/13 - 11/25/13
< 0.8 1412 +/- 155
< 5
< 7
< 13
< 132 SA-MLK-14F4 11/24/13 - 11/25/13
< 0.7 1285 +/- 133
< 6
< 6
< 12
< 124 SA-MLK-2G3 11/24/13 - 11/25/13
< 0.8 1201 +/- 145
< 5
< 7
< 11
< 146 SA-MLK-3G1 (C) 11/24/13 - 11/25/13
< 0.7 1162 +/- 142
< 6
< 7
< 13
< 179 SA-MLK-13E3 12/01/13 - 12/02/13
< 0.7 1256 +/- 159
< 7
< 8
< 13
< 170 SA-MLK-14F4 12/01/13 - 12/02/13
< 0.7 1261 +/- 148
< 6
< 5
< 10
< 126 SA-MLK-2G3 12/01/13 - 12/02/13
< 0.9 1336 +/- 166
< 6
< 7
< 13
< 178 SA-MLK-3G1 (C) 12/01/13 - 12/02/13
< 0.9 1343 +/- 140
< 8
< 8
< 13
< 214 ANNUAL AVERAGE 1326 +/- 196
- IODINE-131 RESULTS ARE CORRECTED FOR DECAY TO STOP DATE OF COLLECTION PERIOD & ANALYZED TO AN LLD OF 1.0 pCi/L (C) CONTROL STATION C-11
TABLE C-6 CONCENTRATIONS OF GROSS ALPHA AND GROSS BETA EMITTERS AND TRITIUM IN WELL WATER*, 2013 Results in units of pCi/liter +/- 2 sigma STATION ID COLLECTION PERIOD START STOP Gr-A Gr-B H-3 SA-WWA-3E1 01/21/13 - 01/21/13
< 2.1
< 3.3
< 155 02/19/13 - 02/19/13
< 1.6
< 1.6
< 175 03/11/13 - 03/11/13
< 2.7
< 2.3
< 191 03/25/13 - 03/25/13
< 1.7
< 1.9
< 169 04/22/13 - 04/22/13
< 2.6
< 2.2
< 171 05/28/13 - 05/28/13
< 2.6
< 2.3
< 176 06/24/13 - 06/24/13
< 2.5
< 2.2
< 169 07/15/13 - 07/15/13
< 1.0 1.8 +/- 1.1
< 186 08/21/13 - 08/21/13
< 1.3
< 1.5
< 167 09/23/13 - 09/23/13
< 1.7
< 4.0
< 196 10/28/13 - 10/28/13
< 0.8
< 1.2
< 177 11/25/13 - 11/25/13
< 1.6
< 2.0
< 191 12/09/13 - 12/09/13
< 1.3
< 1.6
< 192 AVERAGE**
1.8 +/- 0.0
- MANAGEMENT AUDIT SAMPLE: NOT REQUIRED BY ODCM
- THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES C-12
TABLE C-7 CONCENTRATIONS OF GAMMA EMITTERS IN WELL WATER*, 2013 Results in units of pCi/L +/- 2 sigma, 2013 STATION ID COLLECTION PERIOD
<----------GAMMA EMITTERS---------->
START STOP K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 ZrNb-95 I-131 Cs-134 Cs-137 BaLa-140 Ra-226 SA-WWA-3E1 01/21/13 - 01/21/13
< 43
< 3
< 3
< 6
< 3
< 6
< 3
< 0.6
< 3
< 3
< 5
< 72 02/19/13 - 02/19/13
< 54
< 3
< 3
< 6
< 3
< 6
< 4
< 0.6
< 3
< 3
< 6
< 81 03/11/13 - 03/11/13
< 38
< 5
< 4
< 10
< 5
< 10
< 5
< 0.7
< 4
< 5
< 7
< 130 03/25/13 - 03/25/13
< 47
< 5
< 4
< 11
< 5
< 9
< 5
< 0.4
< 5
< 5
< 9
< 128 04/22/13 - 04/22/13
< 44
< 5
< 5
< 10
< 5
< 9
< 5
< 0.6
< 5
< 5
< 8
< 121 05/28/13 - 05/28/13
< 50
< 5
< 5
< 12
< 6
< 11
< 6
< 0.8
< 6
< 6
< 9
< 179 06/24/13 - 06/24/13
< 56
< 5
< 6
< 11
< 5
< 10
< 7
< 0.4
< 5
< 6
< 11
< 130 07/15/13 - 07/15/13
< 80
< 4
< 4
< 10
< 4
< 9
< 5
< 0.6
< 4
< 5
< 7
< 119 08/21/13 - 08/21/13
< 48
< 6
< 7
< 12
< 5
< 13
< 8
< 0.7
< 7
< 7
< 14
< 158 09/23/13 - 09/23/13
< 156
< 6
< 9
< 16
< 9
< 14
< 8
< 0.6
< 5
< 10
< 14
< 148 10/28/13 - 10/28/13
< 60
< 7
< 7
< 15
< 8
< 13
< 8
< 0.8
< 7
< 8
< 14
< 160 11/25/13 - 11/25/13
< 61
< 7
< 8
< 14
< 7
< 14
< 8
< 0.6
< 5
< 7
< 14
< 149 12/09/13 - 12/09/13
< 52
< 5
< 5
< 12
< 5
< 12
< 6
< 0.8
< 6
< 6
< 10
< 130 AVERAGE
- MANAGEMENT AUDIT SAMPLE: NOT REQUIRED BY ODCM C-13
TABLE C-8 CONCENTRATIONS OF GROSS ALPHA AND GROSS BETA EMITTERS AND TRITIUM IN RAW AND TREATED POTABLE WATER (2F3), 2013 Results in units of pCi/L +/- 2 sigma STATION ID COLLECTION PERIOD START STOP GR-A GR-B H-3 RAW 01/01/13 - 01/31/13
< 0.8
< 1.8
< 176 02/01/13 - 02/28/13
< 2.7 3.5 +/- 1.7
< 166 03/01/13 - 03/31/13
< 0.9 3.6 +/- 1.2
< 199 04/01/13 - 04/30/13
< 0.5 3.4 +/- 1.0
< 180 05/01/13 - 05/31/13
< 1.0 4.6 +/- 1.1
< 186 06/01/13 - 06/30/13
< 1.9 4.4 +/- 1.2
< 184 07/01/13 - 07/31/13
< 2.3 3.5 +/- 1.1
< 160 08/01/13 - 08/31/13
< 2.5 6.5 +/- 1.4
< 190 09/01/13 - 09/30/13
< 1.4 4.9 +/- 1.2
< 179 10/01/13 - 10/31/13
< 1.1 6.1 +/- 1.6
< 177 11/01/13 - 11/30/13
< 1.6 5.6 +/- 1.1
< 178 12/01/13 - 12/31/13
< 1.5 7.3 +/- 1.4
< 162 AVERAGE*
4.8 +/- 2.7 TREATED 01/01/13 - 01/31/13
< 1.1
< 1.9
< 176 02/01/13 - 02/28/13
< 1.2 3.2 +/- 1.3
< 168 03/01/13 - 03/31/13
< 1.3 3.1 +/- 1.3
< 170 04/01/13 - 04/30/13
< 0.4 2.9 +/- 1.0
< 180 05/01/13 - 05/31/13
< 1.0 3.7 +/- 1.1
< 92 06/01/13 - 06/30/13
< 2.4 5.8 +/- 1.3
< 182 07/01/13 - 07/31/13
< 2.6 5.9 +/- 1.3
< 160 08/01/13 - 08/31/13
< 2.2 5.9 +/- 1.2
< 186 09/01/13 - 09/30/13
< 1.2 4.3 +/- 1.0
< 177 10/01/13 - 10/31/13
< 0.6 5.2 +/- 1.0
< 173 11/01/13 - 11/30/13
< 1.5 5.0 +/- 1.1
< 177 12/01/13 - 12/31/13
< 1.0 5.8 +/- 1.0
< 168 AVERAGE*
4.6 +/- 2.4
- THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES C-14
TABLE C-9 CONCENTRATIONS OF IODINE-131* AND GAMMA EMITTERS IN RAW AND TREATED POTABLE WATER (2F3), 2013 Results in units of pCi/L +/- 2 sigma STATION ID COLLECTION PERIOD
<----------GAMMA EMITTERS---------->
START STOP I-131*
K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 ZrNb-95 Cs-134 Cs-137 BaLa-140 Ra-226 SA-PWR-2F3 01/01/13 - 01/31/13
< 0.7
< 56
< 5
< 5
< 13
< 6
< 10
< 6
< 5
< 5
< 6
< 101 SA-PWT-2F3 01/01/13 - 01/31/13
< 0.6
< 39
< 4
< 4
< 8
< 4
< 8
< 4
< 4
< 4
< 6
< 89 SA-PWR-2F3 02/01/13 - 02/28/13
< 0.8
< 24
< 3
< 4
< 9
< 4
< 7
< 4
< 3
< 4
< 6
< 80 SA-PWT-2F3 02/01/13 - 02/28/13
< 0.7
< 53
< 3
< 3
< 6
< 3
< 6
< 4
< 3
< 4
< 6
< 93 SA-PWR-2F3 03/01/13 - 03/31/13
< 0.7
< 78
< 4
< 4
< 10
< 5
< 8
< 4
< 4
< 5
< 9
< 116 SA-PWT-2F3 03/01/13 - 03/31/13
< 0.8
< 30
< 3
< 3
< 9
< 3
< 6
< 4
< 3
< 4
< 7
< 79 SA-PWR-2F3 04/01/13 - 04/30/13
< 0.7
< 17
< 2
< 2
< 4
< 2
< 4
< 2
< 2
< 2
< 5
< 49 SA-PWT-2F3 04/01/13 - 04/30/13
< 0.9
< 14
< 1
< 1
< 4
< 2
< 3
< 1
< 1
< 1
< 3
< 30 SA-PWR-2F3 05/01/13 - 05/31/13
< 0.6
< 22
< 2
< 2
< 5
< 2
< 5
< 2
< 2
< 2
< 5
< 50 SA-PWT-2F3 05/01/13 - 05/31/13
< 0.4
< 36
< 2
< 2
< 4
< 2
< 4
< 2
< 2
< 2
< 4
< 56 SA-PWR-2F3 06/01/13 - 06/30/13
< 0.8
< 107
< 5
< 4
< 9
< 6
< 10
< 6
< 5
< 5
< 10
< 138 SA-PWT-2F3 06/01/13 - 06/30/13
< 0.5
< 89
< 4
< 5
< 11
< 5
< 7
< 6
< 4
< 5
< 9
< 134 SA-PWR-2F3 07/01/13 - 07/31/13
< 0.7
< 97
< 4
< 3
< 8
< 3
< 7
< 4
< 4
< 4
< 6
< 108 SA-PWT-2F3 07/01/13 - 07/31/13
< 0.5
< 73
< 4
< 4
< 8
< 4
< 9
< 5
< 5
< 5
< 7
< 137 SA-PWR-2F3 08/01/13 - 08/31/13
< 0.7
< 94
< 5
< 5
< 14
< 6
< 10
< 5
< 4
< 5
< 13
< 149 SA-PWT-2F3 08/01/13 - 08/31/13
< 0.7
< 50
< 6
< 7
< 16
< 7
< 13
< 8
< 6
< 6
< 13
< 121 SA-PWR-2F3 09/01/13 - 09/30/13
< 0.4
< 46
< 5
< 7
< 11
< 6
< 13
< 7
< 5
< 6
< 11
< 117 SA-PWT-2F3 09/01/13 - 09/30/13
< 0.4
< 27
< 4
< 5
< 11
< 5
< 10
< 4
< 5
< 5
< 8
< 137 SA-PWR-2F3 10/01/13 - 10/31/13
< 0.5
< 55
< 6
< 6
< 12
< 6
< 10
< 7
< 6
< 6
< 14
< 162 SA-PWT-2F3 10/01/13 - 10/31/13
< 0.5
< 120
< 6
< 6
< 12
< 6
< 13
< 6
< 6
< 7
< 13
< 186 SA-PWR-2F3 11/01/13 - 11/30/13
< 0.8
< 49
< 6
< 6
< 13
< 6
< 11
< 7
< 5
< 6
< 14
< 133 SA-PWT-2F3 11/01/13 - 11/30/13
< 0.8
< 32
< 3
< 4
< 9
< 4
< 7
< 4
< 3
< 4
< 9
< 82 SA-PWR-2F3 12/01/13 - 12/31/13
< 0.4
< 35
< 4
< 4
< 10
< 4
< 8
< 5
< 4
< 4
< 11
< 109 SA-PWT-2F3 12/01/13 - 12/31/13
< 0.4
< 75
< 3
< 4
< 9
< 3
< 7
< 4
< 3
< 4
< 9
< 97 AVERAGE
- IODINE-131 RESULTS ARE CORRECTED FOR DECAY TO STOP DATE OF COLLECTION PERIOD & ANALYZED TO AN LLD OF 1.0 pCi/L.
C-15
TABLE C-10 CONCENTRATIONS OF GAMMA EMITTERS IN VEGETABLES*, 2013 Results in units of pCi/kg (wet) +/- 2 sigma STATION ID COLLECTION SAMPLE
<------------GAMMA EMITTERS------------>
PERIOD TYPE Be-7 K-40 I-131 Cs-134 Cs-137 Ra-226 Th-232 SA-FPV-2F9 04/27/13 Asparagus
< 134 2338 +/- 380
< 48
< 14
< 16
< 356
< 67 SA-FPV-2F9 04/28/13 Asparagus
< 156 2054 +/- 359
< 46
< 20
< 21
< 323
< 78 AVERAGE**
2196 +/- 402 SA-FPV-3H5 (C) 05/27/13 Asparagus
< 132 1949 +/- 319
< 35
< 15
< 16
< 346
< 61 AVERAGE**
1949 +/- 0 SA-FPV-15F4 07/24/13 Corn
< 29 2235 +/- 80
< 11
< 3
< 3
< 68
< 13 SA-FPV-1G1 (C) 07/24/13 Corn
< 39 2107 +/- 108
< 14
< 4
< 4
< 108
< 18 SA-FPV-1G1 (C) 07/24/13 Peppers
< 56 2025 +/- 124
< 20
< 6
< 6
< 146
< 24 SA-FPV-1G1 (C) 07/24/13 Tomatoes
< 34 1850 +/- 93
< 13
< 4
< 4
< 74
< 14 SA-FPV-2F9 07/24/13 Corn
< 58 1972 +/- 125
< 20
< 6
< 7
< 123
< 26 SA-FPV-2F9 07/24/13 Tomatoes
< 56 2415 +/- 130
< 19
< 6
< 6
< 121
< 25 SA-FPV-2G2 (C) 07/24/13 Corn
< 36 2051 +/- 84
< 13
< 4
< 4
< 81
< 16 SA-FPV-2G2 (C) 07/24/13 Peppers
< 50 1984 +/- 122
< 17
< 5
< 5
< 129
< 22 SA-FPV-2G2 (C) 07/24/13 Tomatoes
< 51 1904 +/- 110
< 18
< 5
< 5
< 127
< 21 SA-FPV-3F6 07/24/13 Peppers
< 73 2418 +/- 162
< 26
< 7
< 9
< 189
< 30 AVERAGE**
2096 +/- 398
- MANAGEMENT AUDIT SAMPLE: NOT REQUIRED BY ODCM
- THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES (C) CONTROL STATION C-16
TABLE C-10 CONCENTRATIONS OF GAMMA EMITTERS IN VEGETABLES*, 2013 Results in units of pCi/kg (wet) +/- 2 sigma STATION ID COLLECTION SAMPLE
<------------GAMMA EMITTERS------------>
PERIOD TYPE Be-7 K-40 I-131 Cs-134 Cs-137 Ra-226 Th-232 SA-FPV-15F4 08/19/13 Tomatoes
< 120 2083 +/- 306
< 29
< 14
< 14
< 310
< 61 SA-FPV-2F9 08/19/13 Peppers
< 152 2157 +/- 356
< 33
< 19
< 19
< 424
< 84 SA-FPV-3F6 08/19/13 Tomatoes
< 102 2709 +/- 273
< 23
< 10
< 10
< 224
< 43 SA-FPV-15F4 08/20/13 Peppers
< 134 2261 +/- 275
< 28
< 14
< 14
< 291
< 54 SA-FPV-2F9 08/20/13 Peaches
< 121 1603 +/- 264
< 30
< 14
< 14
< 325
< 60 SA-FPV-3F6 08/20/13 Corn
< 131 1908 +/- 242
< 21
< 12
< 15
< 315
< 50 SA-FPV-3F8 08/20/13 Peaches
< 86 1704 +/- 247
< 22
< 10
< 12
< 295
< 39 SA-FPV-3H5 (C) 08/20/13 Corn
< 174 2061 +/- 337
< 38
< 18
< 20
< 383
< 82 SA-FPV-3H5 (C) 08/20/13 Peppers
< 181 2433 +/- 420
< 41
< 22
< 21
< 547
< 85 SA-FPV-3H5 (C) 08/20/13 Tomatoes
< 103 1269 +/- 236
< 26
< 12
< 15
< 289
< 52 SA-FPV-13E3 08/26/13 Corn
< 150 2038 +/- 334
< 41
< 17
< 18
< 348
< 64 AVERAGE**
2021 +/- 795 SA-VGT-14F4 11/01/13 soy beans
< 140 13750 +/- 556
< 60
< 15
< 17
< 229
< 73 SA-FPL-10D1***
12/30/13 Cabbage 372 +/- 131 3428 +/- 321
< 57
< 14
< 16
< 290
< 52 SA-FPL-15S1 12/30/13 Cabbage 228 +/- 81 3697 +/- 201
< 37
< 9 13 +/- 7
< 157
< 39 SA-FPL-16S1***
12/30/13 Cabbage 269 +/- 101 3866 +/- 220
< 46
< 10
< 12
< 228
< 39 SA-FPL-1S1***
12/30/13 Cabbage 249 +/- 111 3665 +/- 239
< 52
< 11 19 +/- 12
< 269
< 46 SA-FPL-6S1***
12/30/13 Cabbage
< 116 3699 +/- 310
< 56
< 11
< 13
< 315
< 47 AVERAGE**
279 +/- 128 3671 +/- 314 16 +/- 9
- MANAGEMENT AUDIT SAMPLE: NOT REQUIRED BY ODCM
- THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES
- NEW SAMPLE LOCATION - SEE PROGRAM CHANGES SECTION FOR EXPLANATION (C) CONTROL STATION C-17
TABLE C-11 CONCENTRATIONS OF GAMMA EMITTERS IN FODDER CROPS*, 2013 Results in units of pCi/kg (wet) +/- 2 sigma STATION ID COLLECTION SAMPLE
<------------GAMMA EMITTERS------------>
DATE TYPE Be-7 K-40 I-131 Cs-134 Cs-137 Ra-226 Th-232 SA-VGT-13E3 12/20/13 Silage 196 +/- 88 2968 +/- 224
< 55
< 8
< 10
< 230
< 38 SA-VGT-14F4 12/20/13 Silage 249 +/- 106 4052 +/- 325
< 60
< 11
< 13
< 283
< 57 SA-VGT-2G3 12/18/13 Silage 249 +/- 102 3643 +/- 219
< 52
< 8
< 9
< 216
< 33 SA-VGT-3G1 (C) 12/18/13 Silage 193 +/- 102 713 +/- 132
< 59
< 8
< 9
< 191
< 26 AVERAGE 222 +/- 63 2844 +/- 2979
- MANAGEMENT AUDIT SAMPLE: NOT REQUIRED BY ODCM C-18
TABLE C-12 CONCENTRATIONS OF GAMMA EMITTERS IN SOIL, 2013 Results in units of pCi/kg (dry) +/- 2 sigma STATION ID COLLECTION
<------------GAMMA EMITTERS------------>
DATE Be-7 K-40 Cs-134 Cs-137 Ra-226 Th-232 SA-SOL-10D1 09/11/13
< 710 12230 +/- 1317
< 20 227 +/- 76
< 1534 1053 +/- 170 SA-SOL-13E3 09/11/13
< 369 18510 +/- 1189
< 33
< 38
< 703 361 +/- 92 SA-SOL-14F4 09/11/13
< 451 12820 +/- 1024
< 43
< 46 2511
+/- 1112 979 +/- 126 SA-SOL-16E1 09/11/13
< 299 15360 +/- 885
< 29 45 +/- 27 1324
+/- 740 648 +/- 90 SA-SOL-2F9 09/11/13
< 597 6663 +/- 922
< 46 169 +/- 77 2172
+/- 1153 644 +/- 128 SA-SOL-2G3 (C) 09/11/13
< 349 9139 +/- 809
< 37 78 +/- 34 1898
+/- 913 584 +/- 100 SA-SOL-3G1 (C) 09/11/13
< 584 12440 +/- 1147
< 53 150 +/- 92 2595 +/- 1406 1207 +/- 178 SA-SOL-5F1 09/11/13
< 358 5038 +/- 787
< 37 111 +/- 48
< 767 489 +/- 115 SA-SOL-6S2 09/11/13
< 375 6619 +/- 872
< 38
< 46
< 1029 350 +/- 115 AVERAGE*
10980 +/- 8925 130 +/- 131 2100 +/- 1031 702 +/- 617
- THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES (C) CONTROL STATION C-19
TABLE C-13 CONCENTRATIONS OF GAMMA EMITTERS IN BEEF AND GAME*, 2013 Results in units of pCi/kg (wet) +/- 2 sigma STATION ID COLLECTION SAMPLE TYPE
<------------GAMMA EMITTERS------------>
DATE Be-7 I-131 K-40 Cs-134 Cs-137 SA-GAM-5C1 01/22/13 Muskrat
< 117
< 29 3307 +/- 376
< 14
< 17 AVERAGE 3307 +/- 0.0
- MANAGEMENT AUDIT SAMPLE: NOT REQUIRED BY ODCM C-20
TABLE C-14 CONCENTRATIONS OF GROSS BETA EMITTERS IN SURFACE WATER, 2013 Results in Units of pCi/L +/- 2 sigma COLLECTION PERIOD CONTROL START STOP SA-SWA-11A1 SA-SWA-12C1 SA-SWA-16F1 SA-SWA-1F2 SA-SWA-7E1 01/08/13 - 01/08/13 93 +/- 28 118 +/- 34 39 +/- 11 27 +/- 6 60 +/- 24 02/05/13 - 02/05/13 35 +/- 14 17 +/- 11 11 +/- 5 10 +/- 3 66 +/- 14 03/05/13 - 03/05/13 128 +/- 22 91 +/- 18 25 +/- 5 43 +/- 14 187 +/- 32 04/03/13 - 04/03/13 130 +/- 21 88 +/- 17 89 +/- 14 47 +/- 9 172 +/- 30 05/06/13 - 05/06/13 78 +/- 10 67 +/- 9 40 +/- 6 34 +/- 5 103 +/- 13 06/05/13 - 06/05/13 49 +/- 15 76 +/- 14 49 +/- 10 36 +/- 7 123 +/- 30 07/06/13 - 07/06/13 12 +/- 3 4 +/- 2 7 +/- 4 5 +/- 3 22 +/- 6 08/15/13 - 08/15/13 83 +/- 7 32 +/- 6 25 +/- 4 20 +/- 3 81 +/- 9 09/03/13 - 09/03/13 87 +/- 14 74 +/- 12 58 +/- 9 38 +/- 6 150 +/- 22 10/08/13 - 10/08/13 205 +/- 18 189 +/- 16 137 +/- 12 125 +/- 10 255 +/- 21 11/05/13 - 11/05/13 208 +/- 28 264 +/- 30 144 +/- 20 119 +/- 15 257 +/- 34 12/02/13 - 12/02/13 239 +/- 27 198 +/- 25 173 +/- 20 114 +/- 16 264 +/- 32 AVERAGE 112 +/- 145 102 +/- 157 66 +/- 112 51 +/- 86 145 +/- 167 C-21
TABLE C-15 CONCENTRATIONS OF TRITIUM IN SURFACE WATER, 2013 Results in Units of pCi/L +/- 2 sigma COLLECTION PERIOD CONTROL START STOP SA-SWA-11A1 SA-SWA-12C1 SA-SWA-16F1 SA-SWA-1F2 SA-SWA-7E1 01/08/13 -
01/08/13
< 156
< 159
< 157
< 161
< 156 02/05/13 -
02/05/13
< 181
< 181
< 188
< 189
< 189 03/05/13 -
03/05/13
< 184
< 187
< 186
< 188
< 189 04/03/13 -
04/03/13
< 182
< 187
< 185
< 183
< 182 05/06/13 -
05/06/13
< 178
< 178
< 177
< 178
< 177 06/05/13 -
06/05/13
< 173
< 176
< 176
< 176
< 174 07/06/13 -
07/06/13 265 +/- 120
< 171
< 169
< 173
< 170 08/15/13 -
08/15/13 162
< 165
< 164
< 166
< 168 09/03/13 -
09/03/13 170
< 170
< 167
< 167
< 165 10/08/13 -
10/08/13 190
< 193
< 191
< 192
< 188 11/05/13 -
11/05/13 164
< 163
< 163
< 166
< 160 12/02/13 -
12/02/13 160
< 186
< 160
< 164
< 162 AVERAGE*
265 +/- 0
- THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES C-22
TABLE C-16 CONCENTRATIONS OF GAMMA EMITTERS IN SURFACE WATER, 2013 Results in Units of pCi/L +/- 2 Sigma, 2013 STATION ID COLLECTION
<------------GAMMA EMITTERS------------>
PERIOD I-131*
K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 ZrNb-95 Cs-134 Cs-137 BaLa-140 SA-SWA-11A1 01/08/13
< 0.7
< 25
< 4
< 4
< 10
< 5
< 10
< 4
< 5
< 5
< 12 02/05/13
< 0.6
< 130
< 10
< 11
< 21
< 8
< 18
< 12
< 10
< 12 (1) < 20 03/05/13
< 0.7 81 +/- 31
< 2
< 2
< 4
< 2
< 4
< 2
< 2
< 2
< 4 04/03/13
< 0.6
< 16
< 2
< 2
< 5
< 2
< 3
< 2
< 2
< 2
< 6 05/06/13
< 0.8 93 +/- 50
< 4
< 4
< 10
< 4
< 8
< 4
< 3
< 3
< 10 06/05/13
< 0.7 109 +/- 62
< 6
< 6
< 11
< 6
< 9
< 5
< 5
< 6
< 10 07/06/13
< 0.6
< 15
< 2
< 2
< 4
< 2
< 4
< 2
< 2
< 2
< 3 08/15/13
< 0.6
< 43
< 5
< 4
< 10
< 5
< 8
< 5
< 4
< 5
< 8 09/03/13
< 0.7
< 40
< 4
< 3
< 10
< 3
< 7
< 5
< 4
< 4
< 8 10/08/13
< 0.7 114 +/- 63
< 5
< 6
< 11
< 6
< 13
< 6
< 5
< 6
< 14 11/05/13
< 0.7
< 47
< 7
< 7
< 16
< 8
< 13
< 7
< 6
< 8
< 12 12/02/13
< 0.7 104 +/- 49
< 4
< 4
< 9
< 4
< 9
< 5
< 4
< 4
< 11 AVERAGE**
100 +/- 26 SA-SWA-12C1 (C) 01/08/13
< 0.8
< 37
< 5
< 4
< 9
< 5
< 11
< 6
< 3.9
< 4
< 11 02/05/13
< 0.6
< 46
< 5
< 6
< 13
< 7
< 10
< 7
< 5.3
< 6
< 13 03/05/13
< 0.8 63 +/- 30
< 2
< 2
< 5
< 2
< 4
< 2
< 2.0
< 2
< 5 04/03/13
< 0.7 60 +/- 28
< 2
< 2
< 5
< 2
< 4
< 2
< 1.9
< 2
< 6 05/06/13
< 0.6
< 43
< 4
< 5
< 12
< 5
< 8
< 4
< 4.1
< 5
< 13 06/05/13
< 0.6
< 55
< 6
< 6
< 15
< 5
< 14
< 6
< 5.2
< 6
< 12 07/06/13
< 0.7
< 14
< 1
< 2
< 4
< 2
< 3
< 2
< 1.4
< 2
< 3 08/15/13
< 0.7
< 50
< 5
< 7
< 15
< 6
< 12
< 7
< 4.7
< 5
< 11 09/03/13
< 0.8
< 47
< 4
< 6
< 12
< 5
< 11
< 5
< 4.3
< 5
< 14 10/08/13
< 0.6 123 +/- 64
< 5
< 6
< 12
< 6
< 9
< 6
< 4.5
< 6
< 11 11/05/13
< 0.7 137 +/- 60
< 5
< 5
< 14
< 5
< 9
< 6
< 3.9
< 6
< 11 12/02/13
< 0.8 137 +/- 44
< 3
< 4
< 8
< 4
< 7
< 4
< 2.9
< 3
< 9 AVERAGE**
104 +/- 78
- IODINE-131 RESULTS ARE CORRECTED FOR DECAY TO STOP DATE OF COLLECTION & ANALYZED TO AN LLD OF 1.0 pCi/L
- THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES (C) CONTROL STATION (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-23
TABLE C-16 CONCENTRATIONS OF GAMMA EMITTERS IN SURFACE WATER, 2013 Results in Units of pCi/L +/- 2 Sigma, 2013 STATION ID COLLECTION
<------------GAMMA EMITTERS------------>
PERIOD I-131*
K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 ZrNb-95 Cs-134 Cs-137 BaLa-140 SA-SWA-16F1 01/08/13
< 0.8 76 +/- 49
< 6
< 5
< 12
< 5
< 9
< 5
< 5
< 5
< 11 02/05/13 (1) 1.7 +/- 0.5
< 99
< 5
< 5
< 14
< 5
< 10
< 5
< 4
< 5
< 10 03/05/13
< 0.7 58 +/- 27
< 2
< 2
< 4
< 2
< 3
< 2
< 2
< 2
< 4 04/03/13
< 0.6 50 +/- 30
< 2
< 2
< 6
< 2
< 4
< 2
< 2
< 2
< 7 05/06/13
< 0.7
< 32
< 4
< 4
< 10
< 4
< 8
< 4
< 4
< 4
< 9 06/05/13
< 0.6
< 62
< 5
< 5
< 15
< 7
< 15
< 5
< 5
< 6
< 14 07/06/13
< 0.7
< 15
< 2
< 2
< 3
< 1
< 3
< 2
< 2
< 2
< 3 08/15/13
< 1.0
< 122
< 7
< 5
< 14
< 7
< 11
< 7
< 5
< 6
< 11 09/03/13
< 0.6 101 +/- 53
< 5
< 5
< 13
< 5
< 11
< 7
< 5
< 6
< 14 10/08/13
< 0.7
< 43
< 3
< 4
< 9
< 4
< 8
< 5
< 4
< 4
< 8 11/05/13
< 0.5 134 +/- 77
< 6
< 6
< 12
< 5
< 10
< 7
< 5
< 6
< 13 12/02/13
< 0.7
< 43
< 4
< 5
< 13
< 4
< 6
< 5
< 4
< 5
< 9 AVERAGE**
1.7 +/- 0.0 84 +/- 69 SA-SWA-1F2 01/08/13
< 0.7
< 48
< 5
< 5
< 12
< 6
< 10
< 6
< 5
< 5
< 13 02/05/13 (1) 1.5
+/- 0.5
< 83
< 9
< 10
< 21
< 9
< 15
< 8
< 7
< 9 (1) < 16 03/05/13
< 0.6 47 +/- 30
< 2
< 2
< 5
< 2
< 4
< 2
< 2
< 2
< 5 04/03/13
< 0.6 93 +/- 27
< 2
< 2
< 5
< 2
< 3
< 2
< 2
< 2
< 5 05/06/13
< 0.7
< 40
< 4
< 4
< 9
< 4
< 9
< 4
< 3
< 4
< 11 06/05/13
< 0.5
< 30
< 4
< 4
< 7
< 4
< 9
< 5
< 4
< 5
< 8 07/06/13
< 0.7 71 +/- 33
< 2
< 2
< 4
< 2
< 4
< 2
< 2
< 2
< 4 08/15/13
< 1.0
< 55
< 6
< 6
< 14
< 6
< 14
< 6
< 6
< 5
< 13 09/03/13
< 0.7
< 39
< 4
< 5
< 11
< 6
< 11
< 6
< 4
< 5
< 13 10/08/13
< 0.7 149 +/- 62
< 5
< 5
< 12
< 5
< 10
< 6
< 5
< 5
< 10 11/05/13
< 0.7
< 44
< 5
< 6
< 12
< 5
< 12
< 6
< 5
< 6
< 11 12/02/13
< 0.6 104 +/- 54
< 4
< 4
< 9
< 4
< 7
< 5
< 4
< 4
< 10 AVERAGE**
1.5 +/- 0.0 93 +/- 77
- IODINE-131 RESULTS ARE CORRECTED FOR DECAY TO STOP DATE OF COLLECTION AND ANALYZED TO AN LLD OF 1.0 pCi/L
- THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES (C) CONTROL STATION (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-24
TABLE C-16 CONCENTRATIONS OF GAMMA EMITTERS IN SURFACE WATER, 2013 Results in Units of pCi/L +/- 2 Sigma, 2013 STATION ID COLLECTION
<------------GAMMA EMITTERS------------>
PERIOD I-131*
K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 ZrNb-95 Cs-134 Cs-137 BaLa-140 SA-SWA-7E1 01/08/13
< 0.7 84 +/- 55
< 3.5
< 3.9
< 7
< 4
< 7
< 4
< 3.6
< 4.3
< 8 02/05/13
< 0.8
< 36
< 5.5
< 6.2
< 15
< 6
< 11
< 7
< 5.3
< 5.8
< 15 03/05/13
< 0.9 86 +/- 27
< 1.4
< 1.5
< 4
< 2
< 3
< 2
< 1.4
< 1.7
< 3 04/03/13
< 0.7
< 34
< 1.6
< 1.9
< 5
< 2
< 3
< 2
< 1.6
< 1.8
< 6 05/06/13
< 0.8
< 43
< 4.1
< 5.2
< 11
< 4
< 8
< 5
< 3.9
< 4.3
< 13 06/05/13
< 0.6
< 37
< 4.9
< 5.0
< 12
< 6
< 10
< 5
< 4.9
< 5.5
< 11 07/06/13
< 0.6
< 20
< 2.2
< 2.3
< 5
< 2
< 4
< 2
< 2.0
< 2.3
< 4 08/15/13
< 0.9
< 46
< 4.3
< 5.7
< 12
< 4
< 11
< 5
< 4.4
< 5.6
< 11 09/03/13
< 0.7
< 50
< 5.6
< 6.3
< 11
< 6
< 10
< 6
< 5.2
< 5.2
< 12 10/08/13
< 0.7 120 +/- 67
< 5.1
< 5.6
< 11
< 6
< 9
< 6
< 5.5
< 5.3
< 14 11/05/13
< 0.7 177 +/- 83
< 6.1
< 5.5
< 14
< 5
< 12
< 7
< 5.6
< 6.3
< 12 12/02/13
< 0.7 94 +/- 50
< 3.9
< 3.7
< 9
< 4
< 9
< 4
< 3.5
< 3.9
< 10 AVERAGE**
112 +/- 78
- IODINE-131 RESULTS ARE CORRECTED FOR DECAY TO STOP DATE OF COLLECTION AND ANALYZED TO AN LLD OF 1.0 pCi/L
- THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES (C) CONTROL STATION C-25
TABLE C-17 CONCENTRATIONS OF GAMMA EMITTERS IN EDIBLE FISH, 2013 Results in Units of pCi/kg (wet) +/- 2 sigma STATION ID COLLECTION
<------------GAMMA EMITTERS------------>
PERIOD K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 Cs-134 Cs-137 Ra-226 SA-ESF-11A1 05/16/13 3480 +/- 797
< 48
< 66
< 150
< 52
< 124
< 61
< 66
< 1322 09/23/13 3569 +/- 773
< 52
< 57
< 125
< 41
< 94
< 52
< 53
< 1206 AVERAGE 3525 +/- 126 SA-ESF-12C1 (C) 05/16/13 4705 +/- 964
< 60
< 59
< 82
< 48
< 135
< 44
< 51
< 1010 09/24/13 4283 +/- 823
< 52
< 53
< 142
< 58
< 119
< 45
< 47
< 755 09/25/13 3407 +/- 882
< 55
< 65
< 122
< 46
< 93
< 48
< 58
< 1140 AVERAGE 4132 +/- 1324 SA-ESF-7E1 05/16/13 4048 +/- 884
< 49
< 50
< 122
< 33
< 109
< 46
< 46
< 1104 09/23/13 4755 +/- 1062
< 61
< 63
< 165
< 72
< 117
< 63
< 60
< 1423 AVERAGE 4402 +/- 1000 (C) CONTROL STATION C-26
TABLE C-18 CONCENTRATIONS OF GAMMA EMITTERS IN CRABS, 2013 Results in Units of pCi/kg (wet) +/- 2 sigma STATION ID COLLECTION
<------------GAMMA EMITTERS------------>
PERIOD K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 Cs-134 Cs-137 Ra-226 SA-ECH-11A1 07/22/13 2599 +/- 1164
< 92
< 96
< 251
< 78
< 176
< 88
< 86
< 1930 08/26/13 4316 +/- 1244
< 70
< 79
< 167
< 68
< 129
< 75
< 77
< 1933 AVERAGE 3458 +/- 2428 SA-ECH-12C1 (C) 07/22/13 2868 +/- 940
< 60
< 67
< 171
< 53
< 97
< 45
< 63
< 1015 08/26/13 2803 +/- 1069
< 95
< 88
< 170
< 77
< 155
< 80
< 77
< 1365 AVERAGE 2836 +/- 92 (C) CONTROL STATION C-27
TABLE C-19 CONCENTRATIONS OF GAMMA EMITTERS IN SEDIMENT, 2013 Results in Units of pCi/kg (dry) +/- 2 Sigma STATION ID COLLECTION
<------------GAMMA EMITTERS------------>
PERIOD Be-7 K-40 Cs-134 Cs-137 Ra-226 Th-232 SA-ESS-11A1 06/28/13
< 293 3104 +/- 562
< 30
< 35
< 756 252 +/- 92 11/25/13
< 713 10170 +/- 1256
< 79
< 67
< 1802 987 +/- 194 AVERAGE*
6637 +/- 9993 620 +/- 1040 SA-ESS-12C1 (C) 06/28/13
< 720 17430 +/- 1819
< 74
< 81
< 1541 1168 +/- 206 11/25/13
< 1185 16470 +/- 2034
< 105
< 126 3228 +/- 2014 869 +/- 258 AVERAGE*
16950 +/- 1358 3228 +/- 0 1019 +/- 422 SA-ESS-15A1 06/28/13
< 533 14080 +/- 1632
< 61
< 87 2549 +/- 1699 1014 +/- 226 11/25/13
< 593 9689 +/- 1329
< 54
< 73
< 1258 812 +/- 161 AVERAGE*
11885 +/- 6210 2549 +/- 0 913 +/- 285 SA-ESS-16A1 06/28/13
< 409 5742 +/- 873
< 40
< 51 2898 +/- 1062 701 +/- 202 11/25/13
< 575 8501 +/- 1241
< 55
< 58 2669 +/- 1241 1094 +/- 182 AVERAGE*
7122 +/- 3902 2784
+/- 324 897 +/- 556 SA-ESS-16F1 06/28/13
< 1030 20030 +/- 2340
< 87
< 119
< 2247 1168 +/- 317 11/25/13
< 1175 20940 +/- 2416
< 94
< 103
< 1965 1017 +/- 288 AVERAGE*
20485 +/- 1287 1093 +/- 214 SA-ESS-6S2 07/08/13
< 291 2662 +/- 474
< 27
< 36
< 578 166 +/- 63 12/16/13
< 397 5257 +/- 705
< 31
< 36
< 755 347 +/- 100 AVERAGE*
3960 +/- 3670 257 +/- 256 SA-ESS-7E1 06/28/13
< 507 14680 +/- 1353
< 49
< 71 2403 +/- 1019 829 +/- 245 11/25/13
< 1063 18080 +/- 2010
< 89
< 108 3441 +/- 1914 1233 +/- 232 AVERAGE*
16380
+/- 4808 2922 +/- 1468 1031 +/- 571
- THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES (C) CONTROL STATION C-28
1.0 10.0 100.0 1000.0 AIR (10-3 pCi/M3)
QUARTERLY AVERAGE FIGURE 1 GROSS BETA ACTIVITY IN AIR PARTICULATE 1990 THROUGH 2013 1
10 100 1000 GROSS BETA IN AIR PARTICULATE 1973 THROUGH 2013 1-Weapons Test 1974 2-Weapons Test 1976 3-Weapons Test 1977 4-Weapons Test 1978 5-Weapons Test 1981 6-Chernobyl 1986 7-2013 data includes temporary sampling locations - see Program Changes section.
(1) (2)(3)(4) (5)
(6)
C-29
-10 0
10 20 pCi/L QUARTERLY AVERAGE FIGURE 2 IODINE-131 ACTIVITY IN MILK 1990 THROUGH 2013
-5 0
5 10 15 20 25 IODINE-131 ACTIVITY IN MILK 1973 THROUGH 2013 1-Weapons Test 1974 2-Weapons Test 1976 3-Weapons Test 1977 4-Weapons Test 1978 5-Weapons Test 1981 6-Chernobyl 1986 (1) (2) (3)(4) (5) (6)
C-30
1 10 100 1000 10000 pCi/L QUARTERLY AVERAGE FIGURE 3 GROSS BETA ACTIVITY IN SURFACE WATER 1990 THROUGH 2013 10 100 1000 GROSS BETA ACTIVITY IN SURFACE WATER 1973 THROUGH 2013 C-31
10.00 100.00 1000.00 10000.00 pCi/L QUARTERLY AVERAGE FIGURE 4 TRITIUM ACTIVITY IN SURFACE WATER 1990 THROUGH 2013 10 100 1000 10000 TRITIUM ACTIVITY IN SURFACE WATER 1973 Through 2013 Effluent Discharge near time of sampling: 07-07-05 1-Weapons Test 1974 2-Weapons Test 1976 3-Weapons Test 1977 4-Weapons Test 1978 5-Weapons Test 1981 6-Chernobyl 1986 C-32
10 100 1000 10000 pCi\\Kg SEMI-ANNUAL AVERAGE FIGURE 5 CESIUM-137 & COBALT-60 ACTIVITY IN AQUATIC SEDIMENT 1990 THROUGH 2013 CS-137 CO-60
- 10 100 1000 10000 CESIUM-137 & COBALT-60 ACTIVITY IN AQUATIC SEDIMENT 1977 THROUGH 2013
C-33
0 100 200 300 400 500 600 700 800 1974 1977 1980 1983 1986 1989 1992 1995 1998 2001 2004 2007 2010 2013 pCu/Kg FIGURE 6 CESIUM-137 ACTIVITY IN SOIL 1974 THROUGH 2013 (TRIENNIAL)
C-34
APPENDIX D
SUMMARY
OF INTERLABORATORY COMPARISON PROGRAM RESULTS FROM ECKERT & ZIEGLER ANALYTICS (EZA), ENVIRONMENTAL RESOURCE ASSOCIATES (ERA), AND DEPARTMENT OF ENERGY (DOE) MIXED ANALYTE PERFORMANCE EVALUATION PROGRAM (MAPEP)
D-1
Intentionally left blank D-2
Identification Reported Known Ratio (c)
Month/Year Number Matrix Nuclide Units Value (a)
Value (b)
TBE/Analytics Evaluation (d)
March 2013 E10477 Milk Sr-89 pCi/L 120 99.7 1.20 A
Sr-90 pCi/L 9.21 11.0 0.84 A
E10478 Milk I-131 pCi/L 87.1 100 0.87 A
Ce-141 pCi/L 186 187 0.99 A
Cr-51 pCi/L 463 472 0.98 A
Cs-134 pCi/L 201 214 0.94 A
Cs-137 pCi/L 262 266 0.98 A
Co-58 pCi/L 200 208 0.96 A
Mn-54 pCi/L 215 208 1.03 A
Fe-59 pCi/L 266 252 1.06 A
Zn-65 pCi/L 311 301 1.03 A
Co-60 pCi/L 384 400 0.96 A
E10480 AP Ce-141 pCi 95.3 95.6 1.00 A
Cr-51 pCi 264 241 1.10 A
Cs-134 pCi 123 109 1.13 A
Cs-137 pCi 142 136 1.04 A
Co-58 pCi 112 106 1.06 A
Mn-54 pCi 115 106 1.08 A
Fe-59 pCi 139 129 1.08 A
Zn-65 pCi 163 153 1.07 A
Co-60 pCi 212 204 1.04 A
E10479 Charcoal I-131 pCi 90.1 92.6 0.97 A
E10481 Water Fe-55 pCi/L 1840 1890 0.97 A
June 2013 E10564 Milk Sr-89 pCi/L 110 95.0 1.16 A
Sr-90 pCi/L 15.8 17.0 0.93 A
E10545 Milk I-131 pCi/L 92.6 95.5 0.97 A
Ce-141 pCi/L 83.1 90.4 0.92 A
Cr-51 pCi/L 253 250 1.01 A
Cs-134 pCi/L 118 125 0.94 A
Cs-137 pCi/L 143 151 0.95 A
Co-58 pCi/L 87.1 94.0 0.93 A
Mn-54 pCi/L 171 172 0.99 A
Fe-59 pCi/L 125 120 1.04 A
Zn-65 pCi/L 220 217 1.01 A
Co-60 pCi/L 169 175 0.97 A
E10547 AP Ce-141 pCi 56.8 56.7 1.00 A
Cr-51 pCi 168 157 1.07 A
Cs-134 pCi 85.2 78.4 1.09 A
Cs-137 pCi 101 94.6 1.07 A
Co-58 pCi 62.7 58.9 1.06 A
Mn-54 pCi 125 108 1.16 A
Fe-59 pCi 85.7 75.0 1.14 A
Zn-65 pCi 169 136 1.24 W
Co-60 pCi 116 110 1.05 A
E10546 Charcoal I-131 pCi 86.5 89.7 0.96 A
TABLE D-1 EZA ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING, 2013 (PAGE 1 OF 3)
D-3
Identification Reported Known Ratio (c)
Month/Year Number Matrix Nuclide Units Value (a)
Value (b)
TBE/Analytics Evaluation (d)
June 2013 E10549 Water Fe-55 pCi/L 1610 1610 1.00 A
September 2013 E10646 Milk Sr-89 pCi/L 63.9 96.0 0.67 N (1)
Sr-90 pCi/L 8.88 13.2 0.67 N (1)
E10647 Milk I-131 pCi/L 93.9 98.3 0.96 A
Ce-141 pCi/L NA (2)
Cr-51 pCi/L 272 277 0.98 A
Cs-134 pCi/L 150 172 0.87 A
Cs-137 pCi/L 125 131 0.95 A
Co-58 pCi/L 105 108 0.97 A
Mn-54 pCi/L 138 139 0.99 A
Fe-59 pCi/L 125 130 0.96 A
Zn-65 pCi/L 264 266 0.99 A
Co-60 pCi/L 187 196 0.95 A
E10672 AP Ce-141 pCi NA (2)
Cr-51 pCi 208 223 0.93 A
Cs-134 pCi 143 139 1.03 A
Cs-137 pCi 106 105 1.01 A
Co-58 pCi 97.0 86.5 1.12 A
Mn-54 pCi 116 112 1.04 A
Fe-59 pCi 98.6 105 0.94 A
Zn-65 pCi 219 214 1.02 A
Co-60 pCi 166 158 1.05 A
E10648 Charcoal I-131 pCi 76.3 71.7 1.06 A
E10673 Water Fe-55 pCi/L 1790 1690 1.06 A
December 2013 E10774 Milk Sr-89 pCi/L 97.3 93.8 1.04 A
Sr-90 pCi/L 13.3 12.9 1.03 A
E10775 Milk I-131 pCi/L 89.7 96.1 0.93 A
Ce-141 pCi/L 99.8 110 0.91 A
Cr-51 pCi/L 297 297 1.00 A
Cs-134 pCi/L 129 142 0.91 A
Cs-137 pCi/L 126 126 1.00 A
Co-58 pCi/L 116 112 1.04 A
Mn-54 pCi/L 167 168 0.99 A
Fe-59 pCi/L 117 110 1.06 A
Zn-65 pCi/L 757 741 1.02 A
Co-60 pCi/L 141 147 0.96 A
E10777 AP Ce-141 pCi 85.1 88.0 0.97 A
Cr-51 pCi 278 238 1.17 A
Cs-134 pCi 123 114 1.08 A
Cs-137 pCi 102 101 1.01 A
Co-58 pCi 84.4 89.9 0.94 A
Mn-54 pCi 132 135 0.98 A
Fe-59 pCi 101 88.3 1.14 A
Zn-65 pCi 506 595 0.85 A
Co-60 pCi 118 118 1.00 A
TABLE D-1 EZA ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM (PAGE 2 OF 3)
TELEDYNE BROWN ENGINEERING, 2013 D-4
Identification Reported Known Ratio (c)
Month/Year Number Matrix Nuclide Units Value (a)
Value (b)
TBE/Analytics Evaluation (d)
December 2013 E10776 Charcoal I-131 pCi 84.7 80.5 1.05 A
E10778 Water Fe-55 pCi/L 2010 1910 1.05 A
(1) Milk, Sr-89/90 - The failure was due to analyst error. No client samples were affected by this failure. NCR 13-15 (2) The sample was not spiked with Ce-141 (a) Teledyne Brown Engineering reported result.
(b) The Analytics known value is equal to 100% of the parameter present in the standard as determined by gravimetric and/or volumetric measurements made during standard preparation.
(c) Ratio of Teledyne Brown Engineering to Analytics results.
(d) Analytics evaluation based on TBE internal QC limits: A= Acceptable, reported result falls within ratio limits of 0.80-1.20.
W-Acceptable with warning, reported result falls within 0.70-0.80 or 1.20-1.30. N = Not Acceptable, reported result falls outside the ratio limits of < 0.70 and > 1.30.
TABLE D-1 EZA ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING, 2013 (PAGE 3 OF 3)
D-5
Identification Reported Known Acceptance Month/Year Number Media Nuclide Units Value (a)
Value (b)
Limits Evaluation (c)
May 2013 RAD-93 Water Sr-89 pCi/L 48.3 41.3 31.6 - 48.4 A
Sr-90 pCi/L 19.3 23.9 17.2 - 28.0 A
Ba-133 pCi/L 81.9 82.1 69.0 - 90.3 A
Cs-134 pCi/L 40.9 42.8 34.2 - 47.1 A
Cs-137 pCi/L 44.0 41.7 37.0 - 48.8 A
Co-60 pCi/L 61.9 65.9 59.3 - 75.0 A
Zn-65 pCi/L 202 189 170 - 222 A
Gr-A pCi/L 34.2 40.8 21.1 - 51.9 A
Gr-B pCi/L 18.0 21.6 13.0 - 29.7 A
I-131 pCi/L 23.8 23.8 19.7 - 28.3 A
U-Nat pCi/L 60.4 61.2 49.8 - 67.9 A
H-3 pCi/L 3970 4050 3450 - 4460 A
MRAD-18 Filter Gr-A pCi/filter Lost during processing November 2013 RAD-95 Water Sr-89 pCi/L 25.5 21.9 14.4 - 28.2 A
Sr-90 pCi/L 14.3 18.1 12.8 - 21.5 A
Ba-133 pCi/L 57.2 54.2 44.7 - 59.9 A
Cs-134 pCi/L 83.3 86.7 71.1 - 95.4 A
Cs-137 pCi/L 201 206 185 - 228 A
Co-60 pCi/L 104 102 91.8 - 114 A
Zn-65 pCi/L 361 333 300 - 389 A
Gr-A pCi/L 29.5 42.8 22.2 - 54.3 A
Gr-B pCi/L 30.1 32.2 20.8 - 39.9 A
I-131 pCi/L 23.1 23.6 19.6 - 28.0 A
U-Nat pCi/L 5.53 6.24 47.0 - 7.44 A
H-3 pCi/L 17650 17700 15500 - 19500 A
MRAD-19 Filter Gr-A pCi/filter 33.0 83.0 27.8 - 129 A
(a) Teledyne Brown Engineering reported result.
(b) The ERA known value is equal to 100% of the parameter present in the standard as determined by gravimetric and/or volumetric measurements made during standard preparation.
(c) ERA evaluation: A=acceptable. Reported result falls within the Warning Limits. NA=not acceptable. Reported result falls outside of the Control Limits. CE=check for Error. Reported result falls within the Control Limits and outside of the Warning Limit.
(PAGE 1 OF 1)
TABLE D-2 ERA ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING, 2013 D-6
Identification Reported Known Acceptance Month/Year Number Media Nuclide Units Value (a)
Value (b)
Range Evaluation (c)
March 2013 13-MaW28 Water Cs-134 Bq/L 21.0 24.4 17.1 - 31.7 A
Cs-137 Bq/L 0.0446 (1)
A Co-57 Bq/L 28.3 30.9 21.6 - 40.2 A
Co-60 Bq/L 18.2 19.56 13.69 - 25.43 A
H-3 Bq/L 506 507 355 - 659 A
Mn-54 Bq/L 25.7 27.4 19.2 - 35.6 A
K-40 Bq/L 2.09 (1)
A Sr-90 Bq/L 10.5 10.5 7.4 - 13.7 A
Zn-65 Bq/L 29.2 30.4 21.3 - 39.5 A
13-GrW28 Water Gr-A Bq/L 2.74 2.31 0.69 - 3.93 A
Gr-B Bq/L 15.6 13.0 6.5 - 19.5 A
13-MaS28 Soil Cs-134 Bq/kg 859 887 621 - 1153 A
Cs-137 Bq/kg 633 587 411 - 763 A
Co-57 Bq/kg 0.256 (1)
A Co-60 Bq/kg 738 691 484 - 898 A
Mn-54 Bq/kg 0.671 (1)
A K-40 Bq/kg 714 625.3 437.7 - 812.9 A
Sr-90 Bq/kg 442 628 440 - 816 W
Zn-65 Bq/kg 1057 995 697 - 1294 A
13-RdF28 AP Cs-134 Bq/sample 1.73 1.78 1.25 - 2.31 A
Cs-137 Bq/sample 2.73 2.60 1.82 - 3.38 A
Co-57 Bq/sample 2.38 2.36 1.65 - 3.07 A
Co-60 Bq/sample 0.0302 (1)
A Mn-54 Bq/sample 4.36 4.26 2.98 - 5.54 A
Sr-90 Bq/sample 1.43 1.49 1.04 - 1.94 A
Zn-65 Bq/sample 3.14 3.13 2.19 - 4.07 A
13-GrF28 AP Gr-A Bq/sample 0.767 1.20 0.36 - 2.04 A
Gr-B Bq/sample 0.871 0.85 0.43 - 1.28 A
13-RdV28 Vegetation Cs-134 Bq/sample
-0.197 (1)
A Cs-137 Bq/sample 7.39 6.87 4.81 - 8.93 A
Co-57 Bq/sample 9.87 8.68 6.08 - 11.28 A
Co-60 Bq/sample 6.08 5.85 4.10 - 7.61 A
Mn-54 Bq/sample
-0.0104 (1)
A Sr-90 Bq/sample 1.28 1.64 1.15 - 2.13 W
Zn-65 Bq/sample 6.84 6.25 4.38 - 8.13 A
September 2013 13-MaW29 Water Cs-134 Bq/L 29.1 30.0 21.0 - 39.0 A
Cs-137 Bq/L 34.5 31.6 22.1 - 41.1 A
Co-57 Bq/L 0.0358 (1)
A Co-60 Bq/L 24.6 23.58 16.51 - 30.65 A
H-3 Bq/L 2.45 (1)
A Mn-54 Bq/L 0.0337 (1)
A K-40 Bq/L 0.193 (1)
A Sr-90 Bq/L 9.12 7.22 5.05 - 9.39 W
Zn-65 Bq/L 38.1 34.6 24.2 - 45.0 A
13-GrW29 Water Gr-A Bq/L 1.13 0.701 0.210 - 1.192 A
Gr-B Bq/L 7.61 5.94 2.97 - 8.91 A
TABLE D-3 DOE'S MIXED ANALYTE PERFORMANCE EVALUATION PROGRAM (MAPEP)
(PAGE 1 OF 2)
TELEDYNE BROWN ENGINEERING, 2013 D-7
Identification Reported Known Acceptance Month/Year Number Media Nuclide Units Value (a)
Value (b)
Range Evaluation (c)
September 2013 13-MaS29 Soil Cs-134 Bq/kg 1150 1172 820 - 1524 A
Cs-137 Bq/kg 1100 977 684 - 1270 A
Co-57 Bq/kg 670 (1)
N (2)
Co-60 Bq/kg 502 451 316 - 586 A
Mn-54 Bq/kg 758 674 472 - 876 A
K-40 Bq/kg 796 633 443 - 823 W
Sr-90 Bq/kg 664 460 322 - 598 N (2)
Zn-65 Bq/kg 210 (1)
N (2) 13-RdF29 AP Cs-134 Bq/sample
-0.570 (1)
N (2)
Cs-137 Bq/sample 2.85 2.7 1.9 - 3.5 A
Co-57 Bq/sample 3.30 3.4 2.4 - 4.4 A
Co-60 Bq/sample 2.41 2.3 1.6 - 3.0 A
Mn-54 Bq/sample 3.65 3.5 2.5 - 4.6 A
Sr-90 Bq/sample 1.40 1.81 1.27 - 2.35 W
Zn-65 Bq/sample 2.90 2.7 1.9 - 3.5 A
13-GrF29 AP Gr-A Bq/sample 0.872 0.9 0.3 - 1.5 A
Gr-B Bq/sample 1.57 1.63 0.82 - 2.45 A
13-RdV29 Vegetation Cs-134 Bq/sample 5.29 5.20 3.64 - 6.76 A
Cs-137 Bq/sample 7.48 6.60 4.62 - 8.58 A
Co-57 Bq/sample 0.0129 (1)
A Co-60 Bq/sample 0.0523 (1)
A Mn-54 Bq/sample 8.78 7.88 5.52 - 10.24 A
Sr-90 Bq/sample 1.63 2.32 1.62 - 3.02 W (2)
Zn-65 Bq/sample 3.18 2.63 1.84 - 3.42 W
(1) False positive test.
(2) Soil, Co-57 & Zn-65 identified by gamma software as not detected, MAPEP evaluated as failing the false positive test. A large concentration of Eu-152 was spiked into the sample, causing interference in the analysis. Gamma software irecognized the interference and identified them as not detected. MAPEP does not allow clients to enter non-detect designation.
Soil, Sr incorrect results were submitted to MAPEP. Should have been 332 bq/kg, which would have passed.
AP, Cs-134 - MAPEP evaluated the -0.570 as a failed false positive test. No client samples were affected by these failures. NCR 13-04 Vegetation, Sr it appears that the carrier was double spiked into the sample, resulting in the low activity for this sample. NCR 13-04 (a) Teledyne Brown Engineering reported result.
(b) The MAPEP known value is equal to 100% of the parameter present in the standard as determined by gravimetric and/or volumetric measurements made during standard preparation.
(c) DOE/MAPEP evaluation: A=acceptable, W=acceptable with warning, N=not acceptable.
(PAGE 2 OF 2)
TABLE D-3 DOE'S MIXED ANALYTE PERFORMANCE EVALUATION PROGRAM (MAPEP)
TELEDYNE BROWN ENGINEERING, 2013 D-8