ML021330145: Difference between revisions

From kanterella
Jump to navigation Jump to search
(StriderTol Bot insert)
 
(StriderTol Bot change)
 
Line 16: Line 16:


=Text=
=Text=
{{#Wiki_filter:PSEG Nuclear LLC P.O. Box 236, Hancocks Bridge, New Jersey 08038-0236 APR 3 0 2002                     0 PSEG Nuclear LLC LRN-02-0147 United States Nuclear Regulatory Commission Document Control Desk Washington, DC 20555 Gentlemen:
{{#Wiki_filter:PSEG Nuclear LLC P.O. Box 236, Hancocks Bridge, New Jersey 08038-0236 APR 3 0 2002 0 PSEG Nuclear LLC LRN-02-0147 United States Nuclear Regulatory Commission Document Control Desk Washington, DC 20555 Gentlemen:
2001 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT SALEM AND HOPE CREEK GENERATING STATIONS DOCKET NOS. 50-272, 50-311 AND 50-354 As required by Section 6.9.1.7 of Appendix A to Facility Operating Licenses DPR-70 and DPR-75 for Salem Generating Station, Unit Nos. 1 and 2, and Section 6.9.1.6 of Appendix A to Facility Operating License NPF-57 for Hope Creek Generating Station, PSEG Nuclear hereby transmits one copy of the 2001 Annual Radiological Environmental Operating Report. This report summarizes the results of the radiological environmental surveillance program for 2001 in the vicinity of the Salem and Hope Creek Generating Stations. The result of this program for 2001 was specifically compared to the Tesult of the pre-operational program.
2001 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT SALEM AND HOPE CREEK GENERATING STATIONS DOCKET NOS. 50-272, 50-311 AND 50-354 As required by Section 6.9.1.7 of Appendix A to Facility Operating Licenses DPR-70 and DPR-75 for Salem Generating Station, Unit Nos. 1 and 2, and Section 6.9.1.6 of Appendix A to Facility Operating License NPF-57 for Hope Creek Generating Station, PSEG Nuclear hereby transmits one copy of the 2001 Annual Radiological Environmental Operating Report. This report summarizes the results of the radiological environmental surveillance program for 2001 in the vicinity of the Salem and Hope Creek Generating Stations. The result of this program for 2001 was specifically compared to the Tesult of the pre-operational program.
If you have any questions or comments on this transmittal, please contact Michael Mosier at (856) 339-5434 C
If you have any questions or comments on this transmittal, please contact Michael Mosier at (856) 339-5434 Sincerely, C
Sincerely, Gabor Salamon Nuclear Safety and Licensing Manager Attachment 95-2168 REV. 7/99
Gabor Salamon Nuclear Safety and Licensing Manager Attachment 95-2168 REV. 7/99


Document Control Desk                   2             APR 0 ZOOZ LRN-02-0147 C   Mr. H. Miller, Administrator - Region I U. S. Nuclear Regulatory Commission 475 Allendale Road King of Prussia, PA 19406 USNRC Senior Resident Inspector - Salem (X24)
Document Control Desk 2
APR 0 ZOOZ LRN-02-0147 C
Mr. H. Miller, Administrator - Region I U. S. Nuclear Regulatory Commission 475 Allendale Road King of Prussia, PA 19406 USNRC Senior Resident Inspector - Salem (X24)
USNRC Senior Resident Inspector - Hope Creek (X24)
USNRC Senior Resident Inspector - Hope Creek (X24)
Mr. G. Wunder, Project Manager - Hope Creek U. S. Nuclear Regulatory Commission Mail Stop 8B3 Washington, DC 20555 Mr. R. Fretz, Project Manager - Salem U. S. Nuclear Regulatory Commission Mail Stop 08B1A Washington, DC 20555 Mr. K. Tosch, Manager IV Bureau of Nuclear Engineering 33 Arctic Parkway - CN415 Trenton, NJ 08625 Mr. K. Kille Delaware Emergency Management Agency 165 Brick Store Landing Road Smyrna, DE 19977
Mr. G. Wunder, Project Manager - Hope Creek U. S. Nuclear Regulatory Commission Mail Stop 8B3 Washington, DC 20555 Mr. R. Fretz, Project Manager - Salem U. S. Nuclear Regulatory Commission Mail Stop 08B1A Washington, DC 20555 Mr. K. Tosch, Manager IV Bureau of Nuclear Engineering 33 Arctic Parkway - CN415 Trenton, NJ 08625 Mr. K. Kille Delaware Emergency Management Agency 165 Brick Store Landing Road Smyrna, DE 19977


o PSEG R ADIOLOtGICAL LN v IK(NINTAJ MONITORiNGi PROGrAM For Salem Generating Station, Unit 1: Docket Neo. 50-1272 Salem Generating Station, U/nit 2: Do&ket N(. 50-311 Hope Creek Generating Station : Docket No. 50-3 54 2001 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT JANUARY 1 TO DECEMBER 31, 200 1 P.'eared b-/
o PSEG R ADIOLOtGICAL LN v IK(NINTAJ MONITORiNGi PROGrAM For Salem Generating Station, Unit 1: Docket Neo. 50-1272 Salem Generating Station, U/nit 2: Do&ket N(. 50-311 Hope Creek Generating Station : Docket No. 50-3 54 2001 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT JANUARY 1 TO DECEMBER 31, 200 1 P.'eared b-/
PSEG MAP ',WOOD
PSEG MAP..-
                  ..-        TESTINU S'7"VICES APRIL 2002
',WOOD TESTINU S'7"VICES APRIL 2002


RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM & HOPE CREEK GENERATING STATIONS 2001 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT JANUARY 1 TO DECEMBER 31, 2001
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM & HOPE CREEK GENERATING STATIONS 2001 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT JANUARY 1 TO DECEMBER 31, 2001
Line 34: Line 36:


==SUMMARY==
==SUMMARY==
.....................................................                                                                1 THE RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ...........                                                               3 Objectives ..............................................                                                               4 Data Interpretation .........................                                             ........                ,. 5 Quality Assurance Program ...................                                                                           5 Results and Discussion .......................                                           ..........                    6 Atmospheric .............................                                             ....      °......            6 Direct Radiation ........................                                           ....        o......          7 Terrestrial .............................                                           ..........                    8 Aquatic .................................                                           .....            °..... 13 Conclusions .................................                                                                         17 REFERENCES ......................................                                             ..........                  29 APPENDIX A - PROGRAM  
THE RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM...........
Objectives..............................................
Data Interpretation.........................
Quality Assurance Program...................
Results and Discussion.......................
Atmospheric.............................
Direct Radiation........................
Terrestrial.............................
Aquatic.................................
Conclusions.................................
REFERENCES......................................
APPENDIX A -
PROGRAM  


==SUMMARY==
==SUMMARY==
....................                                              ....            ...... 31 APPENDIX B - SAMPLE DESIGNATION AND LOCATIONS...                                               ..........                  39 APPENDIX C - DATA TABLES ....................................                                                             47 APPENDIX D            
APPENDIX B -
SAMPLE DESIGNATION AND LOCATIONS...
APPENDIX C -
DATA TABLES....................................
5 5
6 6
7 8
13 17 29 31 39 47 APPENDIX D APPENDIX E -


==SUMMARY==
==SUMMARY==
OF RESULTS FROM ANALYTICS & ENVIRONMENTAL RESOURCE ASSOCIATES INTERLABORATORY COMPARISON PROGRAMS                   .........................................                              79 APPENDIX E -            SYNOPSIS OF LAND USE CENSUS ....................                                                  87 i
OF RESULTS FROM ANALYTICS & ENVIRONMENTAL RESOURCE ASSOCIATES INTERLABORATORY COMPARISON PROGRAMS 79 SYNOPSIS OF LAND USE CENSUS....................
87 i
1 3
4
°......
o......  
°.....  


LIST OF'TABLES TABLE NUMBER               TABLE DESCRIPTION   __                          PAGE
LIST OF'TABLES TABLE NUMBER TABLE DESCRIPTION PAGE
: 1. Salem and Hope Creek Generating Stations' Radiological Environmental Monitoring Program (Program Overview)               18 LIST OF FIGURES FIGURE NUMBER                 FIGURE DESCRIPTION                           PAGE
: 1.
: 1. Gross Beta Activity in Air Particulate 1980 through 2001 (Quarterly).   ........................        21
Salem and Hope Creek Generating Stations' Radiological Environmental Monitoring Program (Program Overview) 18 LIST OF FIGURES FIGURE NUMBER FIGURE DESCRIPTION PAGE
: 2. Ambient Radiation - Off-site vs Control Station 1980 through 2001 (Quarterly)..,           .....................22
: 1.
: 3. Iodine-131 Activity in Milk 1980 through 2001 (Quarterly) ........................           23
Gross Beta Activity in Air Particulate 1980 through 2001 (Quarterly).
: 4. Gross Beta Activity in Surface Water 1980 through 2001 (Quarterly) .........................       .24
21
: 5. Tritium Activity in Surface Water 1980 through 2001 (Quarterly)..                                   25 6A. Cesium-137 Activity in Aquatic Sediment 1980 through 2001 (Semi-Annual) ...........................     26 6B. Cobalt-60 Activity in Aquatic Sediment 1980 through 2001 (Semi-Annual) ............ .............       27
: 2.
: 7. Cesium-137 Activity in Soil 1980 through 2001 (Every Three Years)...................         28 ii
Ambient Radiation - Off-site vs Control Station 1980 through 2001 (Quarterly)..,  
..................... 22
: 3.
Iodine-131 Activity in Milk 1980 through 2001 (Quarterly)........................
23
: 4.
Gross Beta Activity in Surface Water 1980 through 2001 (Quarterly).........................  
.24
: 5.
Tritium Activity in Surface Water 1980 through 2001 (Quarterly)..
25 6A.
Cesium-137 Activity in Aquatic Sediment 1980 through 2001 (Semi-Annual)...........................
26 6B.
Cobalt-60 Activity in Aquatic Sediment 1980 through 2001 (Semi-Annual).........................
27
: 7.
Cesium-137 Activity in Soil 1980 through 2001 (Every Three Years)...................
28 ii


SUTMMARY During normal operations of a nuclear power generating station there are releases of small amount-is 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 environment around Artificial Island where the Salem Generating Stations (SGS) and Hope Creek Generating Station (HCGS) are located. The results of the REMP are published annually, providing a summary and interpretation of the data collected.
SUTMMARY During normal operations of a nuclear power generating station there are releases of small amount-is of. radioactive material to the environment.
PSEG's Maplewood Testing Services (MTS) has been responsible for the collection and analysis of environmental samples during the period of January 1, 2001, through December 31, 2001, and the results are discussed in this report. The REMP for SGS/HCGS was conducted in accordance with the SGS-and HCGS Technical Specifications/Offsite Dose Calculation Manual. The Lower Limit of Detection (LLD) values required by .the Technical Specifications/ODCM were achieved for this reporting period.     The objectives of, the program were also met during this period. The data collected assists in demonstrating that SGS and HCGS were operated in compliance with Technical Specifications/ODCM.
To monitor and determine the effects of these releases a Radiological Environmental-Monitoring Program (REMP) has been established for the environment around Artificial Island where the Salem Generating Stations (SGS) and Hope Creek Generating Station (HCGS) are located.
Most of the radioactive materials noted in this report are normally present in the environment, either naturally, such as potassium-40, or as a result of non-nuclear generating station activity, such as nuclear bomb testing. Measurements made in the vicinity of SGS/HCGS were compared to background or control measurements and the preoperational REMP study performed before Salem Unit 1 became operational. Samples of air particulates, air iodine, milk, surface, ground and drinking water, vegetables, game, fodder crops, fish, crabs, and sediment were collected and analyzed. External radiation dose measurements were also made in the vicinity of SGS/HCGS using thermoluminescent dosimeters.
The results of the REMP are published annually, providing a summary and interpretation of the data collected.
From the results obtained, it can be concluded that the levels and fluctuations of radioactivity in environmental samples were as expected for an estuarine environment. No unusual radiological characteristics were observed in the environs of SGS/HCGS during this reporting period. Since these results were comparable to the results obtained during the preoperational phase of the program, and with historical results collected since commercial operation, we can conclude that the operation of SGS and HCGS had no significant impact on the radiological characteristics of the environs of these stations.
PSEG's Maplewood Testing Services (MTS) has been responsible for the collection and analysis of environmental samples during the period of January 1, 2001, through December 31, 2001, and the results are discussed in this report.
To demonstrate compliance with Technical Specifications/ODCM (Sections 3/4.12.1 & 6.8.4.h -1,2,3), samples were analyzed for one or more of the following: gamma emitting isotopes, tritium (H-3), iodine-131 (1-131), gross beta and gross alpha. The results of these analyses were used to assess the environmental impact of SGS and HCGS operations, 1
The REMP for SGS/HCGS was conducted in accordance with the SGS-and HCGS Technical Specifications/Offsite Dose Calculation Manual.
The Lower Limit of Detection (LLD) values required by.the Technical Specifications/ODCM were achieved for this reporting period.
The objectives of, the program were also met during this period.
The data collected assists in demonstrating that SGS and HCGS were operated in compliance with Technical Specifications/ODCM.
Most of the radioactive materials noted in this report are normally present in the environment, either naturally, such as potassium-40, or as a result of non-nuclear generating station activity, such as nuclear bomb testing.
Measurements made in the vicinity of SGS/HCGS were compared to background or control measurements and the preoperational REMP study performed before Salem Unit 1 became operational.
Samples of air particulates, air iodine, milk, surface, ground and drinking water, vegetables, game, fodder crops, fish, crabs, and sediment were collected and analyzed.
External radiation dose measurements were also made in the vicinity of SGS/HCGS using thermoluminescent dosimeters.
From the results obtained, it can be concluded that the levels and fluctuations of radioactivity in environmental samples were as expected for an estuarine environment.
No unusual radiological characteristics were observed in the environs of SGS/HCGS during this reporting period.
Since these results were comparable to the results obtained during the preoperational phase of the program, and with historical results collected since commercial operation, we can conclude that the operation of SGS and HCGS had no significant impact on the radiological characteristics of the environs of these stations.
To demonstrate compliance with Technical Specifications/ODCM (Sections 3/4.12.1 & 6.8.4.h -1,2,3),
samples were analyzed for one or more of the following: gamma emitting isotopes, tritium (H-3),
iodine-131 (1-131),
gross beta and gross alpha.
The results of these analyses were used to assess the environmental impact of SGS and HCGS operations, 1


thereby demonstrating compliance with 'technical Specifications/ODCM (Section 3/4.11) and applicable Federal and State regulations, and to verify the adequacy of radioactive effluent control systems.
thereby demonstrating compliance with 'technical Specifications/ODCM (Section 3/4.11) and applicable Federal and State regulations, and to verify the adequacy of radioactive effluent control systems.
The results provided in this report are summarized below:
The results provided in this report are summarized below:
M There were a total of 1397 analyses on 1121 environmental samples during 2001. Direct radiation dose measurements were made using 196 thermoluminescent dosimeters (TLDs).
M There were a total of 1397 analyses on 1121 environmental samples during 2001.
* In addition to the detection of naturally-occurring isotopes (i.e. Be-7, K-40, Ra-226 and Th-232) trace levels of Cs-134 and Cs-137 were also detected. The concentrations of these nuclides were well below the Technical Specification reporting limit.
Direct radiation dose measurements were made using 196 thermoluminescent dosimeters (TLDs).
E Dose measurements made with quarterly TLDs at 31 offsite locations around the SGS/HCGS site, averaged 49 millirems for the year 2001.- The average dose measurements at the control locations (background) was 54 millirems for the year. This was comparable to the preoperational phase of the program which had an average of 55 millirems per year for 1973 to 1976.
* In addition to the detection of naturally-occurring isotopes (i.e.
Be-7, K-40, Ra-226 and Th-232) trace levels of Cs-134 and Cs-137 were also detected.
The concentrations of these nuclides were well below the Technical Specification reporting limit.
E Dose measurements made with quarterly TLDs at 31 offsite locations around the SGS/HCGS site, averaged 49 millirems for the year 2001.-
The average dose measurements at the control locations (background) was 54 millirems for the year.
This was comparable to the preoperational phase of the program which had an average of 55 millirems per year for 1973 to 1976.
2
2


THE RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Lower All6ways Creek Township, Salem County, New Jersey is the site of Salem (SGS)and Hope Creek (HCGS)' Generating Stations.     SGS consists of two operating pressurized water nuclear power reactors.
THE RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Lower All6ways Creek Township, Salem County, New Jersey is the site of Salem (SGS)and Hope Creek (HCGS)' Generating Stations.
Salem Unit One has a net rating of; 1133 megawatt electric(MWe) cnd Salem Unit Two has a net rating of"1134 MWe.     The licensed core power for both units is 3459 megawatt thermal (MWt).       HCGS is a boiling water nuclear power reactor, which has a net rating of 1091 MWe (3339 MWt)
SGS consists of two operating pressurized water nuclear power reactors.
SGS/HCGS 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 environment surrounding SGS/HCGS is characterized mainly by the Delaware River 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.
Salem Unit One has a net rating of; 1133 megawatt electric(MWe) cnd Salem Unit Two has a net rating of"1134 MWe.
Most of the 'remaining land is used for agriculture [1,21. More specific information on the demograp1-y, hydrology, meteorology, and land use of the area may be found in the Environmental Reports
The licensed core power for both units is 3459 megawatt thermal (MWt).
[1,2], Environmental Statements [3,4], and the Updated Final Safety Analysis Reports for SGS and HCGS [5,6].
HCGS is a
Since 1968, a radiological environmental monitoring program (REMP) has been conducted at the SGS/HCGS Site.     Starting in December, 1972, more extensive radiological monitoring programs were initiated. The operational REMP was initiated in December, 1976, when Salem Unit 1 achieved criticality.     PSEG's Maplewood Testing Services (MTS) has been involved in the REMP since its     inception.
boiling water nuclear power reactor, which has a net rating of 1091 MWe (3339 MWt)
SGS/HCGS 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 environment surrounding SGS/HCGS is characterized mainly by the Delaware River 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.
Most of the 'remaining land is used for agriculture [1,21.
More specific information on the demograp1-y, hydrology, meteorology, and land use of the area may be found in the Environmental Reports
[1,2],
Environmental Statements [3,4],
and the Updated Final Safety Analysis Reports for SGS and HCGS [5,6].
Since 1968, a radiological environmental monitoring program (REMP) has been conducted at the SGS/HCGS Site.
Starting in December, 1972, more extensive radiological monitoring programs were initiated.
The operational REMP was initiated in December,
: 1976, when Salem Unit 1 achieved criticality.
PSEG's Maplewood Testing Services (MTS) has been involved in the REMP since its inception.
MTS is responsible for the collection of all radiological environmental samples and, from 1973 through June, 1983, conducted a quality assurance program in which duplicates of a portion of those samples analyzed by the primary laboratory were also analyzed by MTS.
MTS is responsible for the collection of all radiological environmental samples and, from 1973 through June, 1983, conducted a quality assurance program in which duplicates of a portion of those samples analyzed by the primary laboratory were also analyzed by MTS.
From January, 1973, through June, 1983, Radiation Management Corporation (RMC) had primary responsibility for the analysis of all samples under the SGS/HCGS REMP and annual reporting of results. RMC reports for the preoperational and operational phase of the program are referenced in this report [7-9].     On July 1, 1983, MTS assumed primary responsibility for the analysis of all samples (except TLDs) and the reporting of results. Teledyne Brown Engineering Environmental Services (TBE), assumed responsibility for third-party QA analyses and TLDs. An additional vendor, Controls for Environmental Pollution Inc. (CEP), was retained to provide third party QA analyses and certain non-routine analyses from May, 1988, until June 1, 1992. Currently, Duke Engineering and Services Environmental Laboratory (DE&SEL) is the third party QA vendor and the laboratory which performs the TLD analyses.     MTS reports for the operational phase from 1983 to 2000 are referenced in this report
From January, 1973, through June, 1983, Radiation Management Corporation (RMC) had primary responsibility for the analysis of all samples under the SGS/HCGS REMP and annual reporting of results. RMC reports for the preoperational and operational phase of the program are referenced in this report [7-9].
[10] .
On July 1, 1983, MTS assumed primary responsibility for the analysis of all samples (except TLDs) and the reporting of results.
Teledyne Brown Engineering Environmental Services (TBE),
assumed responsibility for third-party QA analyses and TLDs. An additional vendor, Controls for Environmental Pollution Inc.
(CEP),
was retained to provide third party QA analyses and certain non-routine analyses from May,
: 1988, until June 1, 1992.
Currently, Duke Engineering and Services Environmental Laboratory (DE&SEL) is the third party QA vendor and the laboratory which performs the TLD analyses.
MTS reports for the operational phase from 1983 to 2000 are referenced in this report
[10].
3
3


An overview of the 2001 Program is provided in Table 1.
An overview of the 2001 Program is provided in Table 1.
Radioanalytical data from samples collected under this program were compared with results from the preoperational phase.     Differences between these periods were examined statistically     to determine the effects of static'n operations. This report presents the results from January 1 t ::ough December 31, 2001, for the SGS/HCGS REMP.
Radioanalytical data from samples collected under this program were compared with results from the preoperational phase.
Differences between these periods were examined statistically to determine the effects of static'n operations.
This report presents the results from January 1 t ::ough December 31, 2001, for the SGS/HCGS REMP.
OBJECTIVES The objectives of the Operational REMP 'are:
OBJECTIVES The objectives of the Operational REMP 'are:
0 To fulfill   the requirements of the Radiological Surveillance sections of the Technical. Specifications/ODCM for SGS/HCGS.
0 To fulfill the requirements of the Radiological Surveillance sections of the Technical. Specifications/ODCM for SGS/HCGS.
N To determine whether any significant increase occurred in the concentration of radionuclides in critical pathways.
N To determine whether any significant increase occurred in the concentration of radionuclides in critical pathways.
* To determine if SGS or HCGS has caused an increase in     the radioactive inventory of long-lived radionuclides.
* To determine if SGS or HCGS has caused an increase in the radioactive inventory of long-lived radionuclides.  
  "* To detect any change in   ambient gamma radiation levels.
"* To detect any change in ambient gamma radiation levels.  
  "* To verify that SGS and HCGS operations have no detrimental effects on the health and safety of the public or on the environment.
"* To verify that SGS and HCGS operations have no detrimental effects on the health and safety of the public or on the environment.
This report, as required by Section 6.9.1.7 of the Salem Technical Specifications/ODCM and Section 6.9.1.6 of the Hope Creek Technical Specifications/ODCM, summarizes the findings of the 2001 REMP. "
This report, as required by Section 6.9.1.7 of the Salem Technical Specifications/ODCM and Section 6.9.1.6 of the Hope Creek Technical Specifications/ODCM, summarizes the findings of the 2001 REMP. "
Results of the four-year preoperational program have been summarized for comparison with subsequent operational reports [8]
Results of the four-year preoperational program have been summarized for comparison with subsequent operational reports [8]
In order to meet the objectives., an operational REMP was developed.
In order to meet the objectives., an operational REMP was developed.
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: (1),     established critical pathways for the transfer of radionuclides through the environment to man, and, (2), experience gained during the preoperational phase.
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: (1),
established critical pathways for the transfer of radionuclides through the environment to man, and, (2),
experience gained during the preoperational phase.
Sampling locations were determined based on site meteorology,,
Sampling locations were determined based on site meteorology,,
Delaware estuarine hydrology, local demography, and land uses.
Delaware estuarine hydrology, local demography, and land uses.
Sampling locations were 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 distance.     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.     Appendix A describes and summarizes, in accordance with .Section 6.9.1.7 of the Salem TS and Section 6.9.1.6 of the Hope Creek TS, the operational program as performed in 2001.
Sampling locations were 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 distance.
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.
Appendix A describes and summarizes, in accordance with.Section 6.9.1.7 of the Salem TS and Section 6.9.1.6 of the Hope Creek TS, the operational program as performed in 2001.
4
4


Appendix B describes the coding system which identifies sample type and location. Table B-l lists the sampling stations and the types of samples collected at each station.:: These sampling stations are indicated on Maps B-I and B-2.
Appendix B describes the coding system which identifies sample type and location.
DATA INTERPRETATION Results of analyses are grouped according to sample type and presented in Appendix C. 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 Regulatory Guide 4.8, LLD is the smallest concentration of radioactive material ýin a sample that will yield a net count (above system background) that will be detected with 95% probability, Vith ýonly 5% probability of falsely concluding that a blank observation represents a '"real signal". LLD is normally calculated as 4.66 times the standard deviation of the background counting rate, or of the blank sample, count, as appropriate, divided by counting efficiency, sample size, 2.22 (dpm per picocurie), the radiochemical yield when applicable, the radioactive decay constant and. the- elapsed time between sample collection and time of counting. The Minimum Detectable Concentration (MDC) is defined as the. smallest concentration of radioactive material that can be dotected at a given confidence level. The MDC differs from the LLD in that the MDC- takes into consideration the interference caused by the presence of other nuclides while the LLD does not-.
Table B-l lists the sampling stations and the types of samples collected at each station.:: These sampling stations are indicated on Maps B-I and B-2.
The grouped data were averaged and standard deviations calculated in accordance with Appendix B of Reference" 16. Thus, the 2 sigma deviations of the averaged data represent sample and not analytical variability. For reporting and calculation of averages, any result occurring at or below the LLD is considered to be at that level.
DATA INTERPRETATION Results of analyses are grouped according to sample type and presented in Appendix C.
When a group of data- was composed of 50% or more LLD values, averages were not calculated.
All results above the Lower Limit of Detection (LLD) are at a confidence level of 2 sigma.
Grab sampling is a useful and acceptable procedure for taking environmental samples of a medium in which the concentration of radionuclides is expected to vary slowly with time or where intermittent sampling is deemed sufficient to'establish the radiological characteristics of the medium. This method, however, is only representative of *the sampled medium for that specific location and instant of time. As a result, variation in the radionuclide concentrations of the samples will normally occur.
This represents the range of values into which 95% of repeated analyses of the same sample should fall.:
As defined in Regulatory Guide 4.8, LLD is the smallest concentration of radioactive material ýin a sample that will yield a net count (above system background) that will be detected with 95% probability, Vith ýonly 5% probability of falsely concluding that a blank observation represents a '"real signal".
LLD is normally calculated as 4.66 times the standard deviation of the background counting rate, or of the blank sample, count, as appropriate, divided by counting efficiency, sample size, 2.22 (dpm per picocurie),
the radiochemical yield when applicable, the radioactive decay constant and. the-elapsed time between sample collection and time of counting.
The Minimum Detectable Concentration (MDC) is defined as the. smallest concentration of radioactive material that can be dotected at a given confidence level.
The MDC differs from the LLD in that the MDC-takes into consideration the interference caused by the presence of other nuclides while the LLD does not-.
The grouped data were averaged and standard deviations calculated in accordance with Appendix B of Reference" 16.
Thus, the 2 sigma deviations of the averaged data represent sample and not analytical variability.
For reporting and calculation of averages, any result occurring at or below the LLD is considered to be at that level.
When a group of data-was composed of 50% or more LLD values, averages were not calculated.
Grab sampling is a useful and acceptable procedure for taking environmental samples of a medium in which the concentration of radionuclides is expected to vary slowly with time or where intermittent sampling is deemed sufficient to'establish the radiological characteristics of the medium.
This method, however, is only representative of *the sampled medium for that specific location and instant of time.
As a result, variation in the radionuclide concentrations of the samples will normally occur.
Since these variations wil'l tend to counterbalance one another, averages based upon repetitive grab samples is considered valid.
Since these variations wil'l tend to counterbalance one another, averages based upon repetitive grab samples is considered valid.
QUALITY ASSURANCE PROGRAM MTS has a quality assurance program designed to ensure confidence in the analytical program. Approximately 20% of the total analytical effort is spent on quality control, including process quality 5
QUALITY ASSURANCE PROGRAM MTS has a quality assurance program designed to ensure confidence in the analytical program.
Approximately 20% of the total analytical effort is spent on quality control, including process quality 5


control, instrument quality control,     interlaboratory cross-check analyses, and data review.
control, instrument quality control, interlaboratory cross-check analyses, and data review.
The quality of the results-obtained by MTS is ensured by the implementation of. the Quality Assurance Program as described in the Maplewood Testing Services Quality Assurance 'Plan [i1 and the Environmental and Chemical Division Procedures Manual.       The internal quality control activity of MTS includes the quality control of instrumentation, equipment and reagents; the use of reference standards in calibration, documentation of established procedures and computer programs, and analysis of duplicate and spiked samples.
The quality of the results-obtained by MTS is ensured by the implementation of. the Quality Assurance Program as described in the Maplewood Testing Services Quality Assurance 'Plan [i1 and the Environmental and Chemical Division Procedures Manual.
The external quality control activity is implemented through participation in both the Analytics and the Environmental Resource Associates Interlaboratory Comparison Programs.         The result's of these Interlaboratory Comparison Programs are listed in Tables D-1 through D-4 in Appendix D.
The internal quality control activity of MTS includes the quality control of instrumentation, equipment and reagents; the use of reference standards in calibration, documentation of established procedures and computer programs, and analysis of duplicate and spiked samples.
RESULTS AND DISCUSSION The analytical results of the 2001 REMP samples are divided into categories based on exposure pathways: atmospheric, direct, terrestrial, and aquatic.       The analytical results for the 2001 REMP are summarized in Appendix A.       The data for individual samples are presented in Appendix C.       The data collected demonstrates that the SGS and HCGS REMP was conducted in compliance with the Technical Specifications/ODCM.
The external quality control activity is implemented through participation in both the Analytics and the Environmental Resource Associates Interlaboratory Comparison Programs.
The REMP for the SGS/HCGS Site has historically included samples and analyses not specifically required by these Stations' Technical Specifications/ODCM.       MTS continues to collect and analyze some of these samples in order to maintain personnel proficiency in performing these non-routine analyses.       These analyses are referenced throughout the report as Management Audit samples.         The summary tables in this report include these additional samples and analyses.
The result's of these Interlaboratory Comparison Programs are listed in Tables D-1 through D-4 in Appendix D.
ATMOSPHERIC Air particulates were collected on Schleicher-Schuell No. 25 glass fiber filters     with low-volume air samplers. Iodine was collected from the air by adsorption on triethylenediamine (TEDA-) impregnated charcoal cartridges connected in series after the air particulate filters.     Air sample volumes were measured with calibrated dry-gas meters and were corrected to standard temperature and pressure.
RESULTS AND DISCUSSION The analytical results of the 2001 REMP samples are divided into categories based on exposure pathways: atmospheric, direct, terrestrial, and aquatic.
Air Particulates     (Tables C-1, C-2)
The analytical results for the 2001 REMP are summarized in Appendix A.
Air particulate samples were collected weekly, at 6 locations.         Each of the 318 samples collected for the year were analyzed for gross beta. Quarterly composites of the weekly samples from each station were analyzed for specific gamma emitters.       Total data recovery for the 6 sampling stations in 2001 was 99.91 percent.
The data for individual samples are presented in Appendix C.
The data collected demonstrates that the SGS and HCGS REMP was conducted in compliance with the Technical Specifications/ODCM.
The REMP for the SGS/HCGS Site has historically included samples and analyses not specifically required by these Stations' Technical Specifications/ODCM.
MTS continues to collect and analyze some of these samples in order to maintain personnel proficiency in performing these non-routine analyses.
These analyses are referenced throughout the report as Management Audit samples.
The summary tables in this report include these additional samples and analyses.
ATMOSPHERIC Air particulates were collected on Schleicher-Schuell No.
25 glass fiber filters with low-volume air samplers.
Iodine was collected from the air by adsorption on triethylenediamine (TEDA-) impregnated charcoal cartridges connected in series after the air particulate filters.
Air sample volumes were measured with calibrated dry-gas meters and were corrected to standard temperature and pressure.
Air Particulates (Tables C-1, C-2)
Air particulate samples were collected weekly, at 6 locations.
Each of the 318 samples collected for the year were analyzed for gross beta.
Quarterly composites of the weekly samples from each station were analyzed for specific gamma emitters.
Total data recovery for the 6 sampling stations in 2001 was 99.91 percent.
6
6


0     Gross beta activity was detected in 265 of the indicator station samples at concentrations ranging from 8 x 10-3 to 44 x 10-3 pCi/m 3 and in 53 of the control station samples from 11 x I0-3 to 44 x 10-3 pCi/mUh       The averages for the indiqator and control station .samples were 231and 25 x i0o3 PCi/m3, respectively. - Theý maximum preoperational
0 Gross beta activity was detected in 265 of the indicator station samples at concentrations ranging from 8 x 10-3 to 44 x 10-3 pCi/m3 and in 53 of the control station samples from 11 x I0-3 to 44 x 10-3 pCi/mUh The averages for the indiqator and control station.samples were 231and 25 x i0o3 PCi/m3, respectively. - Theý maximum preoperational
:.level detected was 920 x 10v pCi/m3, with an average of 74 x 10-3 pci/m3. Results:from-1980 to current year are plotted on Figure 1 as quarterly-averages.         Included along with this plot, for purposes of comparison, is an inset depicting a continuation of this plot from the current year all the wayback to 1973-.
:.level detected was 920 x 10v pCi/m3, with an average of 74 x 10-3 pci/m3.
* Gamma spectroscopy, performed on each of the 24 quarterly composite samples analyzed, Aindicated the presence of the naturally-occurring radionuclides Be-7 and K-40.         All other gamma emitters searched for were below the LLD.
Results:from-1980 to current year are plotted on Figure 1 as quarterly-averages.
O Beryllium-7,       attributed to cosmic ray activity in the atmosphere, was detected in all 20 indicator station composites that were.analyzed, :at concentrations ranging from 36 x 10-3 to 78 x 10- pCi/mý, with an average of 56 x 10-3 pCi/m',. It was detected in the 4 control station composites ranging from 33 x 10-3 to 66 x 10- 3 pCi/m3, with an average of 53 x 10-3 pCi/M3.. The maximum preoperational level detected was 330 x l:-3 pCi/rn3 , with an average of 109 x 10-3 pCi/m 3 .
Included along with this plot, for purposes of comparison, is an inset depicting a continuation of this plot from the current year all the wayback to 1973-.
o   Potassium-40 activity was detected in 13 of the indicator station samples,:with- concentrations ranging from7 x 10-3 tC 14 x 10-3 pCi/m 3 , with an average of 10 x 10-3 pCi/m 3 . K-40 was also detected in 2 control station samples, with concentrations of 9 x 10; and 11 x i0-1 pCi/m 3 .     No preoperational data is available for comparison.
Gamma spectroscopy, performed on each of the 24 quarterly composite samples analyzed, Aindicated the presence of the naturally-occurring radionuclides Be-7 and K-40.
Air Iodine     (Table C-3)
All other gamma emitters searched for were below the LLD.
O Beryllium-7, attributed to cosmic ray activity in the atmosphere, was detected in all 20 indicator station composites that were.analyzed, :at concentrations ranging from 36 x 10-3 to 78 x 10-pCi/mý, with an average of 56 x 10-3 pCi/m',.
It was detected in the 4 control station composites ranging from 33 x 10-3 to 66 x 10- 3 pCi/m3, with an average of 53 x 10-3 pCi/M3..
The maximum preoperational level detected was 330 x l:-3 pCi/rn3, with an average of 109 x 10-3 pCi/m 3.
o Potassium-40 activity was detected in 13 of the indicator station samples,:with-concentrations ranging from7 x 10-3 tC 14 x 10-3 pCi/m3, with an average of 10 x 10-3 pCi/m 3.
K-40 was also detected in 2 control station samples, with concentrations of 9 x 10; and 11 x i0-1 pCi/m 3.
No preoperational data is available for comparison.
Air Iodine (Table C-3)
Iodine in filtered air samples was collected weekly, at 6 locations.
Iodine in filtered air samples was collected weekly, at 6 locations.
Each of the 318 samples collected for the year was analyzed for I -131.
Each of the 318 samples collected for the year was analyzed for I -131.
Iodine-131 was not detected in any of the weekly samples analyzed.
Iodine-131 was not detected in any of the weekly samples analyzed.
LLD sensitivities for all the stations,- both indicator and control, ranged from *1 x 10-3 to <i0 X 1i0-1 pCi/m3-.       The maximum 3
LLD sensitivities for all the stations,- both indicator and control, ranged from *1 x 10-3 to <i0 X 1i0-1 pCi/m3-.
preoperational level detected-was 42 x 10-3 pCi/m .
The maximum preoperational level detected-was 42 x 10-3 pCi/m3.
DIRECT RADIATION Ambient radiation levels in, the environs: were- measured with energy compensated CaSO4 (TI) thermoluminescent dosimeters (TLDs) supplied and read by DE&SEL.         Packets containing TLD's for quarterly exposure were placed in the owner controlled area and around the Site at various distances.
DIRECT RADIATION Ambient radiation levels in, the environs: were-measured with energy compensated CaSO4 (TI) thermoluminescent dosimeters (TLDs) supplied and read by DE&SEL.
Packets containing TLD's for quarterly exposure were placed in the owner controlled area and around the Site at various distances.
7
7


Direct Radiation     (Table C-4)
Direct Radiation (Table C-4)
A total of 49 locations were monitored for direct radiation during 2001, including 12 on-site locations, -31 off-site locations within the 10 mile zone,, and 6 control locations beyond 10 miles.     Effort was made to locate TLD's at schools and population centers -in the area.
A total of 49 locations were monitored for direct radiation during 2001, including 12 on-site locations, -31 off-site locations within the 10 mile zone,, and 6 control locations beyond 10 miles.
Five readings for each TLD (ie; 5 elements) at each location were taken in order to obtain a more statistically valid result.       For these measurements, the rad is considered equivalent to the rem, in accordance with 10CFR20.1004.
Effort was made to locate TLD's at schools and population centers -in the area.
The average dose rate   for the 31 quarterly off-site indicator TLDs was 4.1 millirads per   standard month, and the average control rate was 4.5 millirads per   standard month. The preoperational average for the quarterly TLD   readings was 4.4 millirads per standard month.
Five readings for each TLD (ie; 5 elements) at each location were taken in order to obtain a more statistically valid result.
For these measurements, the rad is considered equivalent to the rem, in accordance with 10CFR20.1004.
The average dose rate for the 31 quarterly off-site indicator TLDs was 4.1 millirads per standard month, and the average control rate was 4.5 millirads per standard month.
The preoperational average for the quarterly TLD readings was 4.4 millirads per standard month.
In Figure 2, the quarterly average radiation levels of the off-site indicator stations versus the control stations, are plotted for the period 1980 through 2001, with an inset graph depicting the current year back to 1973.
In Figure 2, the quarterly average radiation levels of the off-site indicator stations versus the control stations, are plotted for the period 1980 through 2001, with an inset graph depicting the current year back to 1973.
TERRESTRIAL Milk samples were taken semi-monthly when cows were on pasture and monthly when cows were not grazing on open pasture.       Animals are considered on pasture from April to November of each year.       Samples were collected in new polyethylene containers and transported in ice chests with no preservatives added.
TERRESTRIAL Milk samples were taken semi-monthly when cows were on pasture and monthly when cows were not grazing on open pasture.
A well water sample was collected monthly.     Separate. raw and treated potable water samples were composited daily at the City cf Salem water treatment plant. All samples were collected in new polyethylene containers.
Animals are considered on pasture from April to November of each year.
Locally grown vegetable and fodder crops were collected at the time of harvest. Such samples were weighed and packed in plastic bags.
Samples were collected in new polyethylene containers and transported in ice chests with no preservatives added.
Game (muskrat) has been collected annually (time of year     dependent on weather conditions, which affect pelt thickness). from     local farms after being trapped, stripped of their pelts and gutted.       The carcasses were packed in plastic bags and kept chilled in     ice chests during transport.
A well water sample was collected monthly.
Separate. raw and treated potable water samples were composited daily at the City cf Salem water treatment plant.
All samples were collected in new polyethylene containers.
Locally grown vegetable and fodder crops were collected at the time of harvest.
Such samples were weighed and packed in plastic bags.
Game (muskrat) has been collected annually (time of year dependent on weather conditions, which affect pelt thickness). from local farms after being trapped, stripped of their pelts and gutted.
The carcasses were packed in plastic bags and kept chilled in ice chests during transport.
Milk (Table C-5)
Milk (Table C-5)
Milk samples were collected at 4 local dairy farms (2 farms in NJ and 2 in Delaware). Each sample was analyzed for 1-131 and gamma emitters.
Milk samples were collected at 4 local dairy farms (2 farms in NJ and 2 in Delaware).
N   Iodine-131 was not detected in any of the 80 samples analyzed.
Each sample was analyzed for 1-131 and gamma emitters.
N Iodine-131 was not detected in any of the 80 samples analyzed.
8
8


LLD sensitivities for both the indicator and the control station samples ranged from <0.1 to <0.4 pCi/L.       The maximum preoperational level detected was 65 pCi/L which occurred following a period of atmospheric nuclear weapons tests.
LLD sensitivities for both the indicator and the control station samples ranged from <0.1 to <0.4 pCi/L.
The maximum preoperational level detected was 65 pCi/L which occurred following a period of atmospheric nuclear weapons tests.
Results from 1980 to 2001 are plotted on Figure 3, with an inset graph depicting the current year back to 1973.,
Results from 1980 to 2001 are plotted on Figure 3, with an inset graph depicting the current year back to 1973.,
U Gamma spectroscopy performed on each of the 80 samples indicated the presence of the naturally-occurring radionuclide K-40. All other gamma emitters searched for were below the LLD.
U Gamma spectroscopy performed on each of the 80 samples indicated the presence of the naturally-occurring radionuclide K-40.
0   Potassium-40 was detected in all 80 samples.     Concentrations for the 60 indicator station samples ranged from 1220 to 1460 pCi/L, with an average of 1350 pCi/L.     The 20 control station sample concentrations ranged from 1220 to 1390 pCi/L, with an average of 1310 *pCi/L. The maximum preoperational level detected was 2000 pCi/L, with an average of 1437 pCi/L.
All other gamma emitters searched for were below the LLD.
Well Water (Ground Water)   (Tables C-6,   C-7)
0 Potassium-40 was detected in all 80 samples.
Although wells in the vicinity of SGS/HCGS are not directly affected by plant operations, water samples were collected monthly from one farm's well during January through December of the year.       Each sample was analyzed for gross alpha; gross beta, tritium, and gamma emitters.
Concentrations for the 60 indicator station samples ranged from 1220 to 1460 pCi/L, with an average of 1350 pCi/L.
N   Gross alpha activity was detected in 9 of the well water samples at concentrations ranging. from 1.2 to 2.6 pCi/L and an average of 2.2 pCi/L. The maximum preoperational level detected was 9.6 pCi/L,. There was no preoperational average determined for this   analysis...
The 20 control station sample concentrations ranged from 1220 to 1390 pCi/L, with an average of 1310 *pCi/L.
"*  Gross beta activity was detected in all 12 well water samples.
The maximum preoperational level detected was 2000 pCi/L, with an average of 1437 pCi/L.
Concentrations for the samples ranged from 9.8 to 14 pCi/L, with an average of 12 pCi/L.       The 2001 gross beta results are comparable with the preoperational -results which ranged from
Well Water (Ground Water) (Tables C-6, C-7)
    <2.1 to 38 pCi/L, with an average value of 9 pCi/L.
Although wells in the vicinity of SGS/HCGS are not directly affected by plant operations, water samples were collected monthly from one farm's well during January through December of the year.
"[   Tritium activity was not detected in any of the well water samples. The LLD, sensitivities, ranged from <-150 to <180 pCi/L.
Each sample was analyzed for gross alpha; gross beta, tritium, and gamma emitters.
N Gross alpha activity was detected in 9 of the well water samples at concentrations ranging. from 1.2 to 2.6 pCi/L and an average of 2.2 pCi/L.
The maximum preoperational level detected was 9.6 pCi/L,.
There was no preoperational average determined for this analysis...
Gross beta activity was detected in all 12 well water samples.
Concentrations for the samples ranged from 9.8 to 14 pCi/L, with an average of 12 pCi/L.
The 2001 gross beta results are comparable with the preoperational -results which ranged from  
<2.1 to 38 pCi/L, with an average value of 9 pCi/L.  
"[
Tritium activity was not detected in any of the well water samples.
The LLD, sensitivities, ranged from <-150 to <180 pCi/L.
The maximum preoperational level detected was 380.:pCi/L.
The maximum preoperational level detected was 380.:pCi/L.
"*  Gamma spectroscopy performed on each of the 12 well water samples indicated the presence of the naturally-occurring radionuclides K-40 and Radium.       All other gamma emitters searched for were below the LLD.
Gamma spectroscopy performed on each of the 12 well water samples indicated the presence of the naturally-occurring radionuclides K-40 and Radium.
0   Radium was deteqted in all 12 of the well water samples at concentrations ranging from 90 to 193 pCi/L with an average of 146 pCi/L. The maximum preoperational level detected was 2.0 pCi/L.
All other gamma emitters searched for were below the LLD.
0 Radium was deteqted in all 12 of the well water samples at concentrations ranging from 90 to 193 pCi/L with an average of 146 pCi/L.
The maximum preoperational level detected was 2.0 pCi/L.
9
9


These values are similar to those found in the past 11 years. However, as with-the 1989 through 2000 results, they are higher than those tfound in the preoperational program.
These values are similar to those found in the past 11 years.
The results are most likely due to a procedural change for sample preparation. The change results in less-removal of radon (and its daughter products) from the sample.       It is reasonable to conclude that values currently observed are typical for this region.,
However, as with-the 1989 through 2000 results, they are higher than those tfound in the preoperational program.
o Potassium-40 ,was detected in 4 of the samples at concen trations ranging from 48 to 85 pCi/L and an average of 71 pCi/L. The maximum preoperational level detected was 30 pCi/L.
The results are most likely due to a procedural change for sample preparation.
Potable Water (Drinking Water)     (Tables C-8, C-9)
The change results in less-removal of radon (and its daughter products) from the sample.
Both raw and treated potable water samples were collected and composited by Salem water treatment plant personnel.       Each sample consisted of daily aliquots composited into a -imonthly sample.     The raw water source forthis   plant is Laurel Lake. and adjacent wells.
It is reasonable to conclude that values currently observed are typical for this region.,
Each of the 24 individual samples.was analyzed for gross alpha, gross beta, tritium, iodine-131 and gamma emitters.
o Potassium-40,was detected in 4 of the samples at concen trations ranging from 48 to 85 pCi/L and an average of 71 pCi/L.
*]   Gross alpha activity was detected in 10 raw water samples at concentrations of 0.6 to 1.4 pCi/L and in 7 treated water samples ranging from 0.8 to 1.6 pCi/L.       The averages for both raw and treated water samples was 0.9 pCi/L.       The maximum pre operational level detected was 2.7 pCi/L.
The maximum preoperational level detected was 30 pCi/L.
M   Gross beta activity was:detected in all 24 samples at concentrations ranging from 2.7 to 4.7 pCi/L for both the raw and treated water. The average concentration for both raw and treated was 3.4 pCi/L. The maximum preoperational level detected was 9-.0 pCi/L, with an average of 4.2 pCi/L.
Potable Water (Drinking Water) (Tables C-8, C-9)
"*  Tritium activity was not detected in any of the raw and treated water samples. LLD sensitivities ranged from <150 to <180 pCi/L. The maximum preoperational level detected was 350 pCi/L, with an average of 179 pCi/L.
Both raw and treated potable water samples were collected and composited by Salem water treatment plant personnel.
"*  Iodine-131 measurements to:a sensitivity of 1.0 pCi/L were performed. Since the receiving water body (Delaware River) is brackish, the water is not used for human consumption.
Each sample consisted of daily aliquots composited into a -imonthly sample.
Drinking water supplies are not affected by discharges from the site. Iodine-131 measurements for all 24 samples were below the LLD sensitivities. The LLD sensitivities ranged from <0.1 to <0.4 pCi/L.               *
The raw water source forthis plant is Laurel Lake. and adjacent wells.
* Gamma spectroscopy performed on each of the 24 monthly water samples indicated the presence of the naturally-occurring radionuclides K-40 and Radium.     All other gamma emitters searched for were below the LLD.
Each of the 24 individual samples.was analyzed for gross alpha, gross beta, tritium, iodine-131 and gamma emitters.  
*]
Gross alpha activity was detected in 10 raw water samples at concentrations of 0.6 to 1.4 pCi/L and in 7 treated water samples ranging from 0.8 to 1.6 pCi/L.
The averages for both raw and treated water samples was 0.9 pCi/L.
The maximum pre operational level detected was 2.7 pCi/L.
M Gross beta activity was:detected in all 24 samples at concentrations ranging from 2.7 to 4.7 pCi/L for both the raw and treated water.
The average concentration for both raw and treated was 3.4 pCi/L.
The maximum preoperational level detected was 9-.0 pCi/L, with an average of 4.2 pCi/L.
Tritium activity was not detected in any of the raw and treated water samples.
LLD sensitivities ranged from <150 to <180 pCi/L.
The maximum preoperational level detected was 350 pCi/L, with an average of 179 pCi/L.
Iodine-131 measurements to:a sensitivity of 1.0 pCi/L were performed.
Since the receiving water body (Delaware River) is brackish, the water is not used for human consumption.
Drinking water supplies are not affected by discharges from the site.
Iodine-131 measurements for all 24 samples were below the LLD sensitivities.
The LLD sensitivities ranged from <0.1 to <0.4 pCi/L.
Gamma spectroscopy performed on each of the 24 monthly water samples indicated the presence of the naturally-occurring radionuclides K-40 and Radium.
All other gamma emitters searched for were below the LLD.
10
10


o   The radionuclide K-40 was detected in 11 of the raw and treated potable waters at concentrations ranging from 26 to 70 pCi/L. The combined average &#xfd;for both raw-and treated
o The radionuclide K-40 was detected in 11 of the raw and treated potable waters at concentrations ranging from 26 to 70 pCi/L.
      -    positive results was 44 pCi/L. There was no preoperational Sdata available for comparison.
The combined average &#xfd;for both raw-and treated positive results was 44 pCi/L.
o   Radium was detected iAn-one potable raw samples and in four of the treated samples at concentrations of 4 to 6.5 pCi/L.
There was no preoperational Sdata available for comparison.
o Radium was detected iAn-one potable raw samples and in four of the treated samples at concentrations of 4 to 6.5 pCi/L.
LLD sensitivities for the remaining raw and treated waters
LLD sensitivities for the remaining raw and treated waters
* ranged from <1.6 to <3.5 pCi/L. The maximum preoperational level detected was 1.4 pCi/L. The higher results in the two measurable samples are most likely due to the procedural change for sample preparation, as discussed in the Well Water section.
* ranged from <1.6 to <3.5 pCi/L. The maximum preoperational level detected was 1.4 pCi/L.
Vegetables       (Table C-10)
The higher results in the two measurable samples are most likely due to the procedural change for sample preparation, as discussed in the Well Water section.
Although vegetables- in the region are not irrigated with water into which liquid plant- effluents have been discharged, a- variety of food products grown in-the area for human consumption were sampled at 5 indicator stations (14 samples) and 5 control'stations (15 samples).
Vegetables (Table C-10)
Although vegetables-in the region are not irrigated with water into which liquid plant-effluents have been discharged, a-variety of food products grown in-the area for human consumption were sampled at 5 indicator stations (14 samples) and 5 control'stations (15 samples).
The vegetables collected as management audit samples were analyzed for gamma emitters and included asparagus, cabbage, sweet corn, peppers and tomatoes.
The vegetables collected as management audit samples were analyzed for gamma emitters and included asparagus, cabbage, sweet corn, peppers and tomatoes.
Gamma spectroscopy performed on each of the 29 samples indicated the presence of the naturally occurring radionuclides K-40 and Radium.
Gamma spectroscopy performed on each of the 29 samples indicated the presence of the naturally occurring radionuclides K-40 and Radium.
All other gamma emitters searched for were below the LLD.
All other gamma emitters searched for were below the LLD.
Potassium-40 was detected in all 29 samples.         Concentrations for the 14 indicator station samples ranged from.1420 to 2570 pCi/kg wet and averaged 2090 pCi/kg-wet. ::Concentrations for the 15 control station samples ranged from 1230 to 2710 pCi/kg-wet, and averaged 2060 pCi/kg-wet.       The average concentration detected for all   samples, both indicator and control, was 2070 pCi/kg-wet.
Potassium-40 was detected in all 29 samples.
Concentrations for the 14 indicator station samples ranged from.1420 to 2570 pCi/kg wet and averaged 2090 pCi/kg-wet. :: Concentrations for the 15 control station samples ranged from 1230 to 2710 pCi/kg-wet, and averaged 2060 pCi/kg-wet.
The average concentration detected for all samples, both indicator and control, was 2070 pCi/kg-wet.
The maximum preoperational level detected was 4800 pCi/kg-wet, with an average of 2140 pCi/kg-wet.
The maximum preoperational level detected was 4800 pCi/kg-wet, with an average of 2140 pCi/kg-wet.
Radium was detected in 1 indicator sample (tomato) at a concentration of 16 pCi/kg-wet.       It was not detected in any of the control station samples.       No preoperational data is available for comparison.
Radium was detected in 1 indicator sample (tomato) at a concentration of 16 pCi/kg-wet.
Game   (Table. C-II)
It was not detected in any of the control station samples.
Although not required by the SGS or HCGS Technical Specifications/ODCM, samples of muskrats, inhabiting the marshlands surrounding the site, are collected.         This game is consumed-by local residents.       The samples, when available, are collected from 2 locations once a year as management audit samples and analyzed for gamma emitters.
No preoperational data is available for comparison.
Game (Table. C-II)
Although not required by the SGS or HCGS Technical Specifications/ODCM, samples of muskrats, inhabiting the marshlands surrounding the site, are collected.
This game is consumed-by local residents.
The samples, when available, are collected from 2 locations once a year as management audit samples and analyzed for gamma emitters.
11
11


Gamma spectroscopy performed on the flesh indicated the presence of the naturally-occurring radionuclide K-40.         All other gamma emitters searched for were below the LLD.
Gamma spectroscopy performed on the flesh indicated the presence of the naturally-occurring radionuclide K-40.
Potassium-40 was detected. in the. indicator station sample at a concentration of 2600 pCi/kgwKet.-:and the control station sample at 2840 pCi/kg-wet. The average. forboth muskrat samples was 2720 pCi/kg-wet. The maximum preoperational level detected was 27000 pCi/kg-wet, with an average*Qof-4400 pCi/kg-wet.        .
All other gamma emitters searched for were below the LLD.
Fodder Crops     (Table C--12)
Potassium-40 was detected. in the. indicator station sample at a concentration of 2600 pCi/kgwKet.-:and the control station sample at 2840 pCi/kg-wet.
Although not required by the SGS or HCGS Technical Specifications/ODCM, six samples of crops normally used as cattle feed (silage and soybeans) were collected from three indicator stations (5 samples) and one control station. (1 sample).       It was determined that these products may be a significant element in the food-chain pathway. Fodder crops are collected as management audit samples and analyzed for gamma emitters.       All of the locations from which samples were collected this year are milk sampling stations.
The average. forboth muskrat samples was 2720 pCi/kg-wet.
Gamma spectroscopy performed on each of the 6 samples indicated the presence of the naturally-occurring radionuclides Be-7, K-40 and Radium. All other gamma emitters searched for were below the LLD.
The maximum preoperational level detected was 27000 pCi/kg-wet, with an average*Qof-4400 pCi/kg-wet.
Beryllium-7, attributed to cosmic ray activity in the atmosphere, was detected in the 3 indicator silage samples at concentrations of 210 to 670 pCi/kg-wet. It was detected in the control station silage sample at 350 pCi/kg-wet.       The average for all the silage samples was 400 pCi/kg-wet.     The maximum preoperational level detected for silage was 4700 pCi/kg-wet, with an average of 2000 pCi/kg-wet. Be-7 was not detected in either of the two indicator soybean samples. LLD sensitivities for the soybean samples were
Fodder Crops (Table C--12)
    <30 and <40 pCi/kg-wet.     The maximum preoperational level detected for soybean samples was 9300 pCi/kg-dry.
Although not required by the SGS or HCGS Technical Specifications/ODCM, six samples of crops normally used as cattle feed (silage and soybeans) were collected from three indicator stations (5 samples) and one control station. (1 sample).
-Potassium-40 was detected in all       6 samples. Concentrations for the 5 indicator station samples ranged from 2560 to 16800 pCi/kg wet and for the 1 control station sample at 4380 pCi/kg-wet.         The average concentration detected for the silage samples (both indicator and control) was 3710 pCi/kg-wet.         Preoperational results averaged 7000 pci/kg-wet.       Results for the soybean samples (both indicator and control) averaged 15900 pCi/kg-wet which is comparable to preoperational studies when the average wet/dry factor of 1.2 is used.       Preoperational soybean results averaged 22000 pCi/kg-dry.
It was determined that these products may be a significant element in the food-chain pathway.
Soil   (Table C-13)
Fodder crops are collected as management audit samples and analyzed for gamma emitters.
Soil is sampled every three years at nine stations, including one control, and analyzed for gamma emitters.       Samples are collected at each station, in areas that have been relatively undisturbed since 12
All of the locations from which samples were collected this year are milk sampling stations.
Gamma spectroscopy performed on each of the 6 samples indicated the presence of the naturally-occurring radionuclides Be-7, K-40 and Radium.
All other gamma emitters searched for were below the LLD.
Beryllium-7, attributed to cosmic ray activity in the atmosphere, was detected in the 3 indicator silage samples at concentrations of 210 to 670 pCi/kg-wet.
It was detected in the control station silage sample at 350 pCi/kg-wet.
The average for all the silage samples was 400 pCi/kg-wet.
The maximum preoperational level detected for silage was 4700 pCi/kg-wet, with an average of 2000 pCi/kg-wet.
Be-7 was not detected in either of the two indicator soybean samples.
LLD sensitivities for the soybean samples were  
<30 and <40 pCi/kg-wet.
The maximum preoperational level detected for soybean samples was 9300 pCi/kg-dry.  
-Potassium-40 was detected in all 6 samples.
Concentrations for the 5 indicator station samples ranged from 2560 to 16800 pCi/kg wet and for the 1 control station sample at 4380 pCi/kg-wet.
The average concentration detected for the silage samples (both indicator and control) was 3710 pCi/kg-wet.
Preoperational results averaged 7000 pci/kg-wet.
Results for the soybean samples (both indicator and control) averaged 15900 pCi/kg-wet which is comparable to preoperational studies when the average wet/dry factor of 1.2 is used.
Preoperational soybean results averaged 22000 pCi/kg-dry.
Soil (Table C-13)
Soil is sampled every three years at nine stations, including one control, and analyzed for gamma emitters.
Samples are collected at each station, in areas that have been relatively undisturbed since 12


the last collection, in order to determine any change in the radionuclide inventory of the area.
the last collection, in order to determine any change in the radionuclide inventory of the area.
Line 200: Line 397:
All other gamma emitters searched 'for were below the LLD' Beryllium-7, attributed to cosmic ray activity in the atmosphere, was detected in 3 of the indicator station samples at concentrations of 120 to 360 pCi/kg-dry and an average of 210 pCi/kg-dry. It was not detected in the control station sample.
All other gamma emitters searched 'for were below the LLD' Beryllium-7, attributed to cosmic ray activity in the atmosphere, was detected in 3 of the indicator station samples at concentrations of 120 to 360 pCi/kg-dry and an average of 210 pCi/kg-dry. It was not detected in the control station sample.
The maximum preoperational level detected for soil samples was 21000 pCi/kg-dry.
The maximum preoperational level detected for soil samples was 21000 pCi/kg-dry.
Potassium-40 was detected in all 8 samples of the indicator station samples at. concentrations ranging from 4610 to 12900 pCi/kg-dry with an average of 885.0 pCi/kg-dry. The control station sample was.8190 pCi/kg-dry. The maximum preoperational level detected was.24000 pCi/kg-dry with an average of 10000 pCi/kg-dry.
Potassium-40 was detected in all 8 samples of the indicator station samples at. concentrations ranging from 4610 to 12900 pCi/kg-dry with an average of 885.0 pCi/kg-dry.
Cesium-137 was detected in 7 of the indicator station samples ranging from 26 to 350 pCi/kg-dry:,-with an average of 210 pCi/kg dry. The control station sample showed a concentration of 160 pCi/kg-dry. The maximum preoperational level detected was 2800 pCi/kg-dry with an average of 800 pCi/kg-dry.     Results from 1974 to the current year are plotted on. FigUre 7.
The control station sample was.8190 pCi/kg-dry.
Radium was detected in all 8 of the indicator stationt samples in concentrations of 260 to 970 pCi/kg-dry, with an average of 660 pCi/kg-dry. :The control station. samp-le showed a concentration of 700 pCi/kg-dry. The maximum preoperational level detected was 1500 pCi/kg-dry with. an average-of 870 pCi/kg-dry.
The maximum preoperational level detected was.24000 pCi/kg-dry with an average of 10000 pCi/kg-dry.
Thorium-232 was detected in all 8 indicator station samples in ranges of 350 to 1200 pCi/kg-dry, and had an average of 790 pCi/kg-dry. The- control station' sample&#xfd; showed a concentration of 850 pCi/kg-dry. 'The.maximum preoperatiofial level detected was 1400 pCi/kg-dry with an average of 740 pCi/kg-dry.
Cesium-137 was detected in 7 of the indicator station samples ranging from 26 to 350 pCi/kg-dry:,-with an average of 210 pCi/kg dry.
AQUATIC All aquatic samples were. collected by Environmental Consulting Services, Inc. Surface water samples were collected in new polyethylene containers that were rinsed twice with the sample medium prior to collection.
The control station sample showed a concentration of 160 pCi/kg-dry.
Edible fish and crabs are taken by net and then processed.       In processing, the flesh is separated from the bone and shell and placed in sealed polyethylene containers and frozen before being transported in- ice-chests.
The maximum preoperational level detected was 2800 pCi/kg-dry with an average of 800 pCi/kg-dry.
Results from 1974 to the current year are plotted on. FigUre 7.
Radium was detected in all 8 of the indicator stationt samples in concentrations of 260 to 970 pCi/kg-dry, with an average of 660 pCi/kg-dry.
:The control station. samp-le showed a concentration of 700 pCi/kg-dry.
The maximum preoperational level detected was 1500 pCi/kg-dry with. an average-of 870 pCi/kg-dry.
Thorium-232 was detected in all 8 indicator station samples in ranges of 350 to 1200 pCi/kg-dry, and had an average of 790 pCi/kg-dry.
The-control station' sample&#xfd; showed a concentration of 850 pCi/kg-dry.  
'The.
maximum preoperatiofial level detected was 1400 pCi/kg-dry with an average of 740 pCi/kg-dry.
AQUATIC All aquatic samples were. collected by Environmental Consulting Services, Inc.
Surface water samples were collected in new polyethylene containers that were rinsed twice with the sample medium prior to collection.
Edible fish and crabs are taken by net and then processed.
In processing, the flesh is separated from the bone and shell and placed in sealed polyethylene containers and frozen before being transported in-ice-chests.
13
13


Sediment samples were taken with a bottom grab sampler and frozen in sealed polyethylene containers before being transported in ice chests.
Sediment samples were taken with a bottom grab sampler and frozen in sealed polyethylene containers before being transported in ice chests.
Surface Water     (Tables C-14,-C-15,   C-16)
Surface Water (Tables C-14,-C-15, C-16)
Surface water samples were collected monthly at 4 indicator stations and 1 control station in the-Delaware estuary.
Surface water samples were collected monthly at 4 indicator stations and 1 control station in the-Delaware estuary.
One location is at the outfall area (which is the area where liquid radioactive effluents from the Salem Station are allowed to be discharged into the Delaware River), another is downstream from the outfall area, and another is directly west of the outfall area at the mouth of the Appoquinimink River.         Two upstream locations are in the Delaware River and at the mouth of the Chesapeake and Delaware Canal, the latter     being sampled&#xfd; when thel flow is from the Canal into the river. Station 12C1, at the mouth of the Appoquinimink River, serves as the operational control.         All surface water samples were analyzed monthly for gross beta and gamma emitters.         Quarterly composites were analyzed for tritium.
One location is at the outfall area (which is the area where liquid radioactive effluents from the Salem Station are allowed to be discharged into the Delaware River),
0     Gross beta activity was detected in all     48 of the indicator station samples ranging from 4.7 to 224 pCi/L, with an average of 82 pCi/L. Beta activity was detected in all   12 of the control station samples with concentrations ranging from 6.4 to 129 pCi/L, with an average of 71 pCi/L.       The maximum preoperational level detected was 110 pCi/L, with an average of 32 pCi/L. Quarterly results for all locations are plotted on Figure 4, for the years 1980 to 2001, with&#xfd; an inset graph depicting the current year back to 1973.
another is downstream from the outfall area, and another is directly west of the outfall area at the mouth of the Appoquinimink River.
H     Tritium activity was not detected in any of the indicator or Scontrol       station composites. LLD sensitivities for the station composites, both indicator and control, ranged from <150 to
Two upstream locations are in the Delaware River and at the mouth of the Chesapeake and Delaware Canal, the latter being sampled&#xfd; when thel flow is from the Canal into the river.
      <190 pCi/L. The maximum preoperational level detected was 600 pCi/L, with an average of 210 pCi/L.       Positive results from 1980 to 2001 are plotted on Figure 5, with an inset graph depicting the current year back to 1973.
Station 12C1, at the mouth of the Appoquinimink River, serves as the operational control.
E       Gamma spectroscopy performed on each of the 48 indicator station and 12 control station surface water samples indicated the presence of the naturally-occurring radionuclide K-40.
All surface water samples were analyzed monthly for gross beta and gamma emitters.
Quarterly composites were analyzed for tritium.
0 Gross beta activity was detected in all 48 of the indicator station samples ranging from 4.7 to 224 pCi/L, with an average of 82 pCi/L.
Beta activity was detected in all 12 of the control station samples with concentrations ranging from 6.4 to 129 pCi/L, with an average of 71 pCi/L.
The maximum preoperational level detected was 110 pCi/L, with an average of 32 pCi/L.
Quarterly results for all locations are plotted on Figure 4, for the years 1980 to 2001, with&#xfd; an inset graph depicting the current year back to 1973.
H Tritium activity was not detected in any of the indicator or Scontrol station composites.
LLD sensitivities for the station composites, both indicator and control, ranged from <150 to  
<190 pCi/L.
The maximum preoperational level detected was 600 pCi/L, with an average of 210 pCi/L.
Positive results from 1980 to 2001 are plotted on Figure 5, with an inset graph depicting the current year back to 1973.
E Gamma spectroscopy performed on each of the 48 indicator station and 12 control station surface water samples indicated the presence of the naturally-occurring radionuclide K-40.
All other gamma emitters searched for were below the LLD.
All other gamma emitters searched for were below the LLD.
Potassium-40 was detected in 45 samples from the indicator stations at concentrations ranging from 42 to 178 pCi/L and in 11 of the control station samples ranging from 38 to 165 pCi/L.
Potassium-40 was detected in 45 samples from the indicator stations at concentrations ranging from 42 to 178 pCi/L and in 11 of the control station samples ranging from 38 to 165 pCi/L.
The average for the indicator station locations was 95 pCi/L, while the average for the control station locations was 99 pCi/L. The maximum preoperational level detected was 200 pCi/L, with an average of 48 pCi/L.
The average for the indicator station locations was 95 pCi/L, while the average for the control station locations was 99 pCi/L.
The maximum preoperational level detected was 200 pCi/L, with an average of 48 pCi/L.
14
14


Fish   (Table C-17)
Fish (Table C-17)
Edible species of fish were collected semi-annually at 3 locations and analyzed for gamma emitters (flesh), and for Sr-89 and Sr-90 (bones) in one location (1AI) . This location was chosen since it is the outfall area for the Salem Station.       Samples included catfish, weakfish, white perch and striped bass.
Edible species of fish were collected semi-annually at 3 locations and analyzed for gamma emitters (flesh), and for Sr-89 and Sr-90 (bones) in one location (1AI).
* Gamma spectroscopy performed an each of the 4 indicator station samples and 2 control station samples indicated the presence of the naturally-occurring radionuclide K-40. All other gamma emitters searched for were below the LLD.
This location was chosen since it is the outfall area for the Salem Station.
o   Potassium-40 was detected in all 4 samples from the indicator stations at concentrations ranging from 3240 to 3910 pCi/kg-wet for an average of 3500 pCi/kg-wet.     K-40 was detected in, both samples from the control location at 3650 and 3700 pCi/kg-wet. The average for the. control samples, was 3675 pCi/kg-wet. The maximum preoperational level detected was 13000 pCi/kg-wet, with an average of 2900 pCi/kg-wet.
Samples included catfish, weakfish, white perch and striped bass.
* Strontium-89 and strontium-90 analyses were performed by DE&SLL oz one sample of the first   semi-annual sample collection (location IIAl), and reported as MDC. These are management audit analyses which are performed in recognition of the high bioaccumulation factor of strontium in bone.
Gamma spectroscopy performed an each of the 4 indicator station samples and 2 control station samples indicated the presence of the naturally-occurring radionuclide K-40. All other gamma emitters searched for were below the LLD.
o   Strontium-89 was not detected.in the bone sample. The MDC value for the-sample was <600 pCi/kg-dry. The maximum preoperational level detected was 100 pCi/kg-dry.
o Potassium-40 was detected in all 4 samples from the indicator stations at concentrations ranging from 3240 to 3910 pCi/kg-wet for an average of 3500 pCi/kg-wet.
o   Strontium-90 was not detected in- the bone sample. The MDC value for the sample was <130 :pCi/kg-dry. The maximum preoperational level detected was 940.pCi/kg-dry, with an average of 335 pCi/kg-dry..
K-40 was detected in, both samples from the control location at 3650 and 3700 pCi/kg-wet.
Blue Crab     (Table C-18)
The average for the. control samples, was 3675 pCi/kg-wet.
The maximum preoperational level detected was 13000 pCi/kg-wet, with an average of 2900 pCi/kg-wet.
Strontium-89 and strontium-90 analyses were performed by DE&SLL oz one sample of the first semi-annual sample collection (location IIAl),
and reported as MDC.
These are management audit analyses which are performed in recognition of the high bioaccumulation factor of strontium in bone.
o Strontium-89 was not detected.in the bone sample.
The MDC value for the-sample was <600 pCi/kg-dry. The maximum preoperational level detected was 100 pCi/kg-dry.
o Strontium-90 was not detected in-the bone sample.
The MDC value for the sample was <130 :pCi/kg-dry. The maximum preoperational level detected was 940.pCi/kg-dry, with an average of 335 pCi/kg-dry..
Blue Crab (Table C-18)
Blue crab samples were collected semi-annually at 2 locations, 1 indicator and 1 control, arid the edible portions were analyzed for gamma emitters.
Blue crab samples were collected semi-annually at 2 locations, 1 indicator and 1 control, arid the edible portions were analyzed for gamma emitters.
Gamma spectroscopy performed on the flesh of each of the 2 indicator station samples and 2 control station samples indicated the presence of the naturally-occurring radionuclide K-40.       All other gamma emitters searched for were below the LLD.
Gamma spectroscopy performed on the flesh of each of the 2 indicator station samples and 2 control station samples indicated the presence of the naturally-occurring radionuclide K-40.
Potassium-40 was detected in both indicator station samples at concentrations of 2510 and 2910 pCi/kg-wet and in both of&#xfd; the control station samples at 2660 and 3080 pCi/kg-wet.       The average for both the indicator and control station samples was 2790 pCi/kg-wet. The maximum preoperational level detected was 12000 pCi/kg-wet, with an average of 2835 pCi/kg-wet.
All other gamma emitters searched for were below the LLD.
Potassium-40 was detected in both indicator station samples at concentrations of 2510 and 2910 pCi/kg-wet and in both of&#xfd; the control station samples at 2660 and 3080 pCi/kg-wet.
The average for both the indicator and control station samples was 2790 pCi/kg-wet.
The maximum preoperational level detected was 12000 pCi/kg-wet, with an average of 2835 pCi/kg-wet.
15
15


Sediment   (Table C-19)
Sediment (Table C-19)
Sediment samples were collected semi-annually from 7 locations, 6 indicator stations and 1 control.station.     Each of the 14 samples was analyzed for gamma emitters.. Although trace levels of man-made nuclides were detected in some sediment.samples, these levels were expected and well within the-acceptable levels specified-in section 3/4.12.1 of the Technical Specifications/ODCM.
Sediment samples were collected semi-annually from 7 locations, 6 indicator stations and 1 control.station.
Gamma spectroscopy was performed on each of the 12 indicator station samples and 2 control station samples.     In addition to the detection of the naturally-occurring radionuclides Radium, K-40, Be-7 and Th-232, low levels 'fCs-134 and Cs-137 were also detected.         All other gamma emitters searched for were below the LLD.
Each of the 14 samples was analyzed for gamma emitters.. Although trace levels of man-made nuclides were detected in some sediment.samples, these levels were expected and well within the-acceptable levels specified-in section 3/4.12.1 of the Technical Specifications/ODCM.
Cesium-134 was detected in 2 of the 12 indicator station samples at concentrations of 19 and 27 pCi/kg-dry.     It was not detected in either control station samples. LLD sensitivities for the remaining station samples, both indicator and control ranged from
Gamma spectroscopy was performed on each of the 12 indicator station samples and 2 control station samples.
  <2.2 to <7.2 pCi/kg-dry. No pre-operational data is available for comparison.
In addition to the detection of the naturally-occurring radionuclides Radium, K-40, Be-7 and Th-232, low levels  
Cesium-137 was detected in 9 indicator station samples at concentrations ranging from 19 to 120 pCi/kg-dry and an average of 59 pCi/kg-dry. It was detected in 1 control station sample at a concentration~of 58 pCi/kg-dry.     The maximum preoperational level detected was 400 .1Ci/kg-dry with an average of 150 pCi/kg dry. Results from 1980 to 2000 are plotted on Figure 6A, with an inset graph depicting the current year back to 1973.
'f Cs-134 and Cs-137 were also detected.
Cobalt-60 was not detected in any of the sediment samples for the second year in a row. LLD sensitivities for these 14 samples, indicator and control, ranged from <2 to <22 pCi/kg-dry.       Results of all the positive values from 1980 to 2001 are plotted on Figure 6B, with an inset graph depicting the current year back to 1973.
All other gamma emitters searched for were below the LLD.
Potassium-40 was detected in all 12 indicator station samples at concentrations ranging from 1020 to 15900 pCi/kg-dry, with an average of 11550 pCi/kg-dry. Concentrations detected in both of the control station samples were at 15600 pCi/kg-dry.       The average for both the indicator and control station samples was 12100 pCi/kg-dry. The maximum preoperational level detected was 21000 pCi/kg-dry, with an average of 15000 pCi/kg-dry.
Cesium-134 was detected in 2 of the 12 indicator station samples at concentrations of 19 and 27 pCi/kg-dry.
Radium was detected in all 12 indicator station samples at con centrations ranging from 96 to 760 pCi/kg-dry, with an average of 530 pCi/kg-dry. Concentrations detected in both of the control station samples were at 550 and 820 pCi/kg-dry, with an average of 690 pCi/kg-dry. The grand average for both the indicator and control station samples was 560 pCi/kg-dry.       The maximum pre operational level detected was 1200 pCi/kg-dry, with an average of 760 pCi/kg-dry.
It was not detected in either control station samples.
LLD sensitivities for the remaining station samples, both indicator and control ranged from  
<2.2 to <7.2 pCi/kg-dry.
No pre-operational data is available for comparison.
Cesium-137 was detected in 9 indicator station samples at concentrations ranging from 19 to 120 pCi/kg-dry and an average of 59 pCi/kg-dry.
It was detected in 1 control station sample at a concentration~of 58 pCi/kg-dry.
The maximum preoperational level detected was 400.1Ci/kg-dry with an average of 150 pCi/kg dry.
Results from 1980 to 2000 are plotted on Figure 6A, with an inset graph depicting the current year back to 1973.
Cobalt-60 was not detected in any of the sediment samples for the second year in a row.
LLD sensitivities for these 14 samples, indicator and control, ranged from <2 to <22 pCi/kg-dry.
Results of all the positive values from 1980 to 2001 are plotted on Figure 6B, with an inset graph depicting the current year back to 1973.
Potassium-40 was detected in all 12 indicator station samples at concentrations ranging from 1020 to 15900 pCi/kg-dry, with an average of 11550 pCi/kg-dry.
Concentrations detected in both of the control station samples were at 15600 pCi/kg-dry.
The average for both the indicator and control station samples was 12100 pCi/kg-dry. The maximum preoperational level detected was 21000 pCi/kg-dry, with an average of 15000 pCi/kg-dry.
Radium was detected in all 12 indicator station samples at con centrations ranging from 96 to 760 pCi/kg-dry, with an average of 530 pCi/kg-dry.
Concentrations detected in both of the control station samples were at 550 and 820 pCi/kg-dry, with an average of 690 pCi/kg-dry.
The grand average for both the indicator and control station samples was 560 pCi/kg-dry.
The maximum pre operational level detected was 1200 pCi/kg-dry, with an average of 760 pCi/kg-dry.
16
16


Thorium-232 was detected in all 12 indicator station samples at concentrations ranging from 82 to 1130 pCi/kg-dry, with an average of 710 pCi/kg-dry.       Concentrations detected in both Of the. control station samples were at 480 and II00 pCi/kg-dry, with an average of; 790 pCi/kg-dry ... The grand average for both the indicator and control station samples was 830 pCi/kg-dry.
Thorium-232 was detected in all 12 indicator station samples at concentrations ranging from 82 to 1130 pCi/kg-dry, with an average of 710 pCi/kg-dry.
Concentrations detected in both Of the. control station samples were at 480 and II00 pCi/kg-dry, with an average of; 790 pCi/kg-dry... The grand average for both the indicator and control station samples was 830 pCi/kg-dry.
The maximum pre-operational level detected was 1300 pCi/kg-dry, with an average of 840 pCi/kg-dry..
The maximum pre-operational level detected was 1300 pCi/kg-dry, with an average of 840 pCi/kg-dry..
Beryllium-7 was detected in 5 of the 12 indicator station samples at concentrations of 220 to 870 pCi/kg-dry, with an average of 550 pCi/kg-dry. It was detected in 1 of the control station samples at a concentration of 350 pCi/kg-dry.       The LLD sensitivities for the remaining samples, both indicator and control, ranged from <40 to <250 pCi/kg-dry.       The maximum preoperational level detected was 2300 pCi/kg-dry.
Beryllium-7 was detected in 5 of the 12 indicator station samples at concentrations of 220 to 870 pCi/kg-dry, with an average of 550 pCi/kg-dry.
CONCLUSIONS The Radiological Environmental Monitoring Program for Salem and Hope Creek Generating Stations was conducted- during 2001 in accordance with the SGS and HCGS- Technical Specifications/ODCM.       The LLD values required by the Technical Specifications/ODCM were achieved for this reporting period., The, objectives of the program were also met during this period.     The. data collected-.assists in demonstrating that SGS and--HCGS .were operated in coifpliance with Technical Specifications/ODCM.
It was detected in 1 of the control station samples at a concentration of 350 pCi/kg-dry.
From the results obtained, it can be.concluded that the levels and fluctuations of radioactivity in environmental samples were as expected for an estuarine environment-.: No unusual radiological characteristics, were observed in the environs of SGS/HCGS-during this reporting period.       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, we can.'conclude that the operation of the Salem and Hope Creek Stations had no-significant impact on the radiological characteristics of. the environs of that area.
The LLD sensitivities for the remaining samples, both indicator and control, ranged from <40 to <250 pCi/kg-dry.
The maximum preoperational level detected was 2300 pCi/kg-dry.
CONCLUSIONS The Radiological Environmental Monitoring Program for Salem and Hope Creek Generating Stations was conducted-during 2001 in accordance with the SGS and HCGS-Technical Specifications/ODCM.
The LLD values required by the Technical Specifications/ODCM were achieved for this reporting period.,
The, objectives of the program were also met during this period.
The. data collected-.assists in demonstrating that SGS and--HCGS.were operated in coifpliance with Technical Specifications/ODCM.
From the results obtained, it can be.concluded that the levels and fluctuations of radioactivity in environmental samples were as expected for an estuarine environment-.:
No unusual radiological characteristics, were observed in the environs of SGS/HCGS-during this reporting period.
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, we can.'conclude that the operation of the Salem and Hope Creek Stations had no-significant impact on the radiological characteristics of. the environs of that area.
17
17


TABLE 1 SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (PROGRAM OVERVIEW)
TABLE 1 SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (PROGRAM OVERVIEW)
STATION CODE             COLLECTION MEDIUM             INDICATOR             CONTROL   FREQUENCY           TYPE/FREQUENCY* OF ANALYSIS I. ATMOSPHERIC ENVIRONMENT
STATION CODE COLLECTION MEDIUM INDICATOR CONTROL FREQUENCY TYPE/FREQUENCY* OF ANALYSIS I.
: a. Air Particulate               5SI SDI 16El         14G1     Weekly               Gross beta/weekly IF1 2F6                                            Gamma scan/quarterly
ATMOSPHERIC ENVIRONMENT
: b. Air Iodine                    5S1  5DI 16EI        14G1    Weekly              Iodine-131/weekly FI! 2F6 P"
: a. Air Particulate
II. DIRECT RADIATION
: b.
: a. Thermoluminescent             I11   2S4 3SI   4S1   3G1    Quarterly            Gamma dose/  quarterly Dosimeters                  2S2    5DI  2E1  IF1   IG3 5S1    ODI 3El    2F2   1OGI 6S2 14D1 13E1    2F6   16G1 7S1 15SI 16SI    4F2   14GI 1051 16E1    5FI  6FI   3H1 7F2 11F1 13F4 4D2    9E1  2F5  3F2 lIE2 15D1 12EI      3F3 16F2 10F2 12FI 13F2 I1F3 14F2 15F3 III. Terrestrial Environment Monthly              Iodine-131/monthly
Air Iodine 5SI SDI 16El IF1 2F6 5S1 5DI 16EI FI!
: a. Milk                          2F9 1IF3 14F4         3GI     (when animals are on Gamma scan/monthly pasture)
2F6 14G1 14G1 Weekly Weekly Gross beta/weekly Gamma scan/quarterly Iodine-131/weekly II.
Semi-monthly         Iodine-13 1/semi -monthly (when animals are on Gamma scan/semi-monthly pasture)
DIRECT RADIATION
: a.
Thermoluminescent Dosimeters I11 2S2 5S1 6S2 7S1 1051 4D2 lIE2 16F2 I1F3 2S4 5DI ODI 14D1 15SI 16E1 7F2 9E1 15D1 10F2 14F2 3SI 2E1 3El 13E1 16SI 5FI 11F1 2F5 12EI 12FI 15F3 4S1 IF1 2F2 2F6 4F2 6FI 13F4 3F2 3F3 13F2 3G1 IG3 1OGI 16G1 14GI 3H1 Quarterly Gamma dose/ quarterly III.
Terrestrial Environment 2F9 1IF3 14F4 3GI Monthly (when animals are on pasture)
Semi-monthly (when animals are on pasture)
Iodine-131/monthly Gamma scan/monthly Iodine-13 1/semi -monthly Gamma scan/semi-monthly P"
: a.
Milk


TABLE 1 (cont'd)
TABLE 1 (cont'd)
SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (PROGRAM OVERVIEW)
SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (PROGRAM OVERVIEW)
STATION CODE               COLLECTION MEDIUM    INDICATOR             CONTROL   FREQUENCY     TYPE/FREQUENCY* OF ANALYSIS
STATION CODE INDICATOR CONTROL COLLECTION FREQUENCY TYPE/FREQUENCY* OF ANALYSIS
: b. Well Water           3E1                           Monthly       Gross alpha/monthly Gross beta/monthly Tritium/monthly Gamma scan/monthly
: b. Well Water
: c. Potable Water        2F3                            Monthly      Gross alpha/monthly (Raw & Treated)                                    (composited  Gross beta/monthly daily)        Tritium/monthly Gamma scan/monthly Iodine-131/monthly
: c. Potable Water (Raw & Treated) 3E1 2F3 3E1 3F5 6F2
: d. Vegetables          3E1  2F4  2F9          iG1    Annually      Gamma scan/on collection 3F5  3F6  3F8          2G2    (at harvest) 6F2      14F3          3H5 9G1 14G2 e, Game               I!DI  3E1                      Annually      Gamma scan/on collectiOn (Muskrat)
: d. Vegetables Monthly Monthly (composited daily) 2F4 2F9 3F6 3F8 14F3 iG1 2G2 3H5 9G1 14G2 Annually (at harvest)
: f. Fodder Crops_       2F9 11F3   14F4       3GI     Annually     Gamma scan/on collection
Gross alpha/monthly Gross beta/monthly Tritium/monthly Gamma scan/monthly Gross alpha/monthly Gross beta/monthly Tritium/monthly Gamma scan/monthly Iodine-131/monthly Gamma scan/on collection e, Game (Muskrat)
: g. Soil                6S2  2F7  11F3      3GI    Every 3 years Gamma scan/on collection 10DI   2F9   14F4 16E1    5F1
: f.
Fodder Crops_
I!DI 3E1 2F9 11F3 14F4 3GI Annually Annually Gamma scan/on collectiOn Gamma scan/on collection Every 3 years Gamma scan/on collection MEDIUM
: g.
Soil 6S2 10DI 16E1 2F7 2F9 5F1 11F3 14F4 3GI


TABLE 1 (cont'd)
TABLE 1 (cont'd)
SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (PROGRAM OVERVIEW)
SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (PROGRAM OVERVIEW)
STATION CODE                   COLLECTION MEDIUM       INDICATOR             CONTROL       FREQUENCY   TYPE/FREQUENCY* OF ANALYSIS IV. AQUATIC ENVIRONMENT
STATION CODE COLLECTION MEDIUM INDICATOR CONTROL FREQUENCY TYPE/FREQUENCY* OF ANALYSIS IV. AQUATIC ENVIRONMENT
: a. Surface Water         IIAl   7E1   IF2 12CI   16F1         Monthly     Gross beta/monthly Gamma scan/monthly Tritium/quarterly
: a. Surface Water
: b. Edible Fish            IIAl      7El            12C1        Semi annually  Sr-89 & Sr-90 (bones)/on 1 loc.**
: b. Edible Fish
0O                                                                              Sr-89 & Sr-90 (flesh/on 1 loc.**
: c. Blue Crabs
Gamma scan (flesh)/on collection
: d. Sediment IIAl 7E1 IF2 12CI 16F1 IIAl 7El IIAl 11AI 1hAl 15A1 16AI 12C1 12C1 6S2 16FI 7E1 12C1 Monthly Semi annually Semi annually Semi annually.
: c. Blue Crabs            IIAl                    12C1          Semi        Gamma scan (flesh)/on collection annually
Gross beta/monthly Gamma scan/monthly Tritium/quarterly Sr-89 & Sr-90 (bones)/on 1 loc.**
: d. Sediment                11AI      6S2    7E1    12C1          Semi      Gamma scan/on collection 1hAl 15A1    16FI                          annually.
Sr-89 & Sr-90 (flesh/on 1 loc.**
16AI
Gamma scan (flesh)/on collection Gamma scan (flesh)/on collection Gamma scan/on collection
* Except for TLDs, the quarterly analysis is performed on a composite of individual samples collected during the quarter.
* Except for TLDs, the quarterly analysis is performed on a composite of individual samples collected during the quarter.  
    ** Management audit analyses, not required by Technical Specifications or by specific commitments to local officials.
** Management audit analyses, not required by Technical Specifications or by specific commitments to local officials.
0O


FIGURE 1 GROSS BETA IN AIR PARTICULATE 1980 TH4ROUGH 2001 1000 I GROSS RTA INAIR PARTICULATE 1973 THROUGH2001 Weapons Test 10-15-80               Chernobyl 04-26-86 O0                                                                                                        "1M 1~i 97979                              l5,                                            l997 100 C,
FIGURE 1 GROSS BETA IN AIR PARTICULATE 1980 TH4ROUGH 2001 Weapons Test 10-15-80 Chernobyl 04-26-86 Salem - 2 Criticality I
0 10-Salem - 2 Criticality                           I 08-02-80                                     Hope Creek Criticality 06-28-86 1 i. lI  lI I I . . . I I   . I I I I I I I I I   I I I I I I I I Il I I I 1 1 1 1 1 1 1 . I . . I I I I   I   I I I a I I I   I I I I I I . .      ..                              ...  ...
08-02-80 Hope Creek Criticality 06-28-86 1983 1985 1987 1989 "1991 1993 1995 1997 1999 2001 QUARTERLY AVERAGE 1000 100 C,
1981              1983          1985          1987            1989            "1991          1993          1995                1997            1999                                  2001 QUARTERLY AVERAGE
0 GROSS RTA IN AIR PARTICULATE 1973 THROUGH 2001 1~i 97979 l5, l997 O0 "1M 10-1 1981 i.
l I l I I I.
I I I I I I I I I I I
I I I I I I I I Il I I I 1 1 1 1 1 1
1.
I.
I I I I
I I I I a I I I I
I I I I I.
I


z 0 0 lz w
22 z
0 0
lz w
0 M
0 M
z LL 0 0
z LL 0
0 0
0 0
z 0,
0 z
N  UJ w t:
0, N
U) 0 00 LL z
UJ w
0 m P
t:
qjuow   PIS/wom 22
U) 0 00 LL z
0 m
P qjuow PIS/wom


FIGURE 3 IODINE - 131 ACTIVITY IN MILK 1980 THROUGH 2001 20 ACTVrrYINMILK ODINE0.13i 1973THROUGH2001 Chernobyl                     - 5.
FIGURE 3 IODINE - 131 ACTIVITY IN MILK 1980 THROUGH 2001 20 ODINE0.13i ACTVrrY IN MILK 1973 THROUGH 2001 Chernobyl  
04/26/86                         0.00
- 5.
                                                                      -.00 10 909     1905                     199             1997 001o Weapons Test                     "                    1           I 10-15-80 I                   *Hope                         Creek Criticality 06-28-86 0
04/26/86 0.00 10
Salem-2 Criticality 08-02-80
-.00 001o 909 1905 199 1997 Weapons Test 1
-10 OII   I I I IS   ,I II I   I   ,I   0 IIIII     I                             1 11   1       1I       I I     I I III   I   IIIIIII     II I 1985           1987       1989           1991 1993   1995                 1997             1999           2001 1981        1983 IQUARTERLY AVERAGE
I 10-15-80 I  
*Hope Creek Criticality 06-28-86 0
Salem-2 Criticality 08-02-80  
-10 OII I I I
IS  
,I II I
I  
,I 0
IIIII I
1 11 1
1I I
I I I III I
IIIIIII II I
1981 1983 1985 1987 1989 1991 1993 1995 1997 1999 2001 IQUARTERLY AVERAGE


FIGURE 4 GROSS BETA ACTIVITY IN SURFACE WATER 1980 THROUGH 2001 1000.0 GROSSBETAACTIVITYINSURFACEWATER 1971 THROUGH2091 1000 ]. . . .  . . .  . .. ..  . . . . .
FIGURE 4 GROSS BETA ACTIVITY IN SURFACE WATER 1980 THROUGH 2001 Weapons Test 10-15-80 Chernobyl 04-26-86 Salem - 2 Criticality 08-02-80 GROSS BETA ACTIVITY IN SURFACE WATER 1971 THROUGH 2091 100 1973 1979 1986 1991 1997 Hope Creek Criticality 06-28-86
Weapons Test 10-15-80 100 Chernobyl 04-26-86                     1973                   1979                     1986                 1991               1997 100.0 r11:
: 1987, 1989.
    ,J C.)
.1991, 1993 1995 1997 1999 I QUARTERLY AVERAGE I 1000.0 100.0 r11:
10.0 - Salem - 2 Criticality 08-02-80                                    Hope Creek Criticality 06-28-86 1.0             . . . . . . . . .      f l l . l l l ."il 1 1 1 1   1   1   1 1 1 1   1 1 1 1 1 1 1 1   1   1   1   1   1 1 1 . I I I I I I I a   I l I l I I 1 I 1981              1983    1985        1987,          1989.         .1991,              1993                1995              1997            1999            2001 I QUARTERLY AVERAGE I
,J C.)
10.0 -
1.0 1981 1983 1985 2001 "il f
l l
l l
l 1 1 1
1 1
1 1 1 1 1 1 1 1 1 1 1 1 1 1
1 1
1 1 1 1.
I I I I I I I a I l I l I
I 1 I 1000 ]....


FIGURE 5 TRITIUM ACTIVITY IN SURFACEWATER-,.
FIGURE 5 TRITIUM ACTIVITY IN SURFACEWATER-,.
1980 THROUGH 2001 10,000                                                                                                   TRITIL "10000 1000 tOO 10 1973       1979 Chernobyl 04-26-86 1,000 Weapons Test 10-15-80
1980 THROUGH 2001 10,000 TRITIL "10000 1000 tOO 10 1973 1979 Chernobyl 04-26-86 1,000 Weapons Test 10-15-80  
-J 100 Hope Creek Criticality
-J 100 Hope Creek Criticality  
          .Salem-2 Criticality                       06-28-86 08-02-80 10   1 8   I   I I II  I II I i   I I I I I I I I I I I I . I I I I       i, 1991 I  1 9&#xfd;I
.Salem-2 Criticality 06-28-86 08-02-80 10 1
                                                                                                .199,3 1981         1983           1985           *1987*:         1989,                                 1995 1997   1999     2001 QUARTERLY AVERAGEj
8 I
I I
I I
I I
I I
i I
I I I
I I I
I I
I I I.
I I
I I
1 9&#xfd;I i,
I 1981 1983 1985  
*1987*:
: 1989, 1991
.199,3 1995 1997 1999 2001 QUARTERLY AVERAGEj


FIGURE 6A CESIUM-137 ACTIVITY IN AQUATIC SEDIMENT 1980 THROUGH 2001 10000 CESIUM-137 ACTIVITYINAQUATIC  SEDIMENT 1977THROUGH  2001 0
FIGURE 6A CESIUM-137 ACTIVITY IN AQUATIC SEDIMENT 1980 THROUGH 2001 Weapons Test 10-15-80 CESIUM-137 ACTIVITY IN AQUATIC SEDIMENT 1977 THROUGH 2001 I=00 0
I=00   -- ----.-
1985 19B9 290 1997 2001 IChernobyl 04-26-86 I
1000 Weapons Test                                                t973            1977      19"1        1985             19B9           290       1997   2001 10-15-80 0" CL                            IChernobyl     04-26-86 0.
Salem - 2 Criticality 08-02-80 Hope Creek Criticality 06-26-86 1983 1985 1987 1989 1991 I
100 I
I I
Salem - 2 Criticality 08-02-80 Hope Creek Criticality 06-26-86 10          .
I I
                    .1 .  . .  .    .    .  .  .  .  ...I         I         I     I     ,  I I   I I I   I   I   I   I    I    I  I  I I I I    I I I I I 1981        1983            1985        1987      1989              1991        1993       1995               1997             1999       2001 I SEMI-ANNUAL AVERAGEI
I I
I I
I I
I I
I I
I I
I 1993 1995 1997 1999 2001 I SEMI-ANNUAL AVERAGEI 10000 1000 CL 0"
0.
100 10 1981 I
I I
.1
...I I
I I
t973 1977 19"1


FIGURE 6B COBALT- 60 ACTIVITY IN AQUATIC SEDIMENT 1980 THROUGH 2001 10000 COBALT-60 ACTIVITY IN AQUATIC SEDIMENT 1977 THROUGH 2001 10000                                                          -   -- *-   --       -- * -   .
FIGURE 6B COBALT-60 ACTIVITY IN AQUATIC SEDIMENT 1980 THROUGH 2001 10000 1000 C)
10 m1000 lO.                                 *        .o.
Chernobyl 04-26-86 Solem - 2 Criticality 08-02-80 Hope Creek Criticality 06-26-86 1981 1983 1985 1987 1989 1991 1993 1996 1997 1999 2001 SEMI-ANNUAL AVERAGE Weapons Test 10-15-80.
10 1973     1977         1981         1985           1989     1993           1997       2001 1000 Weapons Test 10-15-80.  ..
100 COBALT-60 ACTIVITY IN AQUATIC SEDIMENT 1977 THROUGH 2001 10000 m 1000 10 lO.  
C)
.o.
Chernobyl 04-26-86 100 Solem - 2 Criticality              Hope Creek Criticality 06-26-86 08-02-80 10  1981 1993 I   I     I I 1996 I   I   .    .  . I            l   lI             Il I I .
10 1973 1977 1981 1985 1989 1993 1997 2001 10 I
1983    1985        1987        1989            1991                                          1997        1999              2001 SEMI-ANNUAL AVERAGE
I I
I I
I I
l lI Il I
I  


FIGURE 7 CESIUM -137 ACTIVITY IN SOIL 1974 THROUGH 2001 10000.0 Salem - 2 Criticality 08-02-80 Hope Creek Criticality 06-28-86 1000.0 -
FIGURE 7 CESIUM -137 ACTIVITY IN SOIL 1974 THROUGH 2001 10000.0 Salem - 2 Criticality 08-02-80 Hope Creek Criticality 06-28-86 4
4 C,
I IF Salem - 1 Crticality 12-11-76 Weapons Test Chernobyl 10-15-80 04-26-86 1974 1977 1980 1983 1986 1000.0 -
Salem - 1 Crticality I                        IF 12-11-76 100.0                          Weapons Test                 Chernobyl 10-15-80                 04-26-86 10.0  i 1974       1977           1980         1983       1986           1989 1992 1995   1998     2001 YEARLY AVERAGE
C, 100.0 10.0 1989 1992 1995 1998 2001 YEARLY AVERAGE i


REFERENCES
REFERENCES
[1]: Public Service Enterprise Group     "Environmental Report, Operating License Stage - Salem Nuclear Generating Station Units 1 and 2".     1971.
[1]: Public Service Enterprise Group "Environmental Report, Operating License Stage - Salem Nuclear Generating Station Units 1 and 2".
[2] _ Public Service Enterprise Group     "Environmental Report, Operating License Stage - Hope Creek Generating Station". 1983.
1971.
[3]   United States Atomic Energy Commission.   "Final Environmental Statement Salem Nuclear Generating Station, Units 1 and 2". Docket No. 50-272 and 50-311. 1973.
[2] _ Public Service Enterprise Group "Environmental Report, Operating License Stage -
[4]   United States Atomic Energy Commission.   "Final Environmental Statement Hope Creek Generating Station,   Docket No. 50-354. 1983.
Hope Creek Generating Station".
[5]   Public Service Enterprise Group .    "Updated Final Safety Analysis Report - Salem Nuclear Generating Station, Units 1 and 2". 1982.
1983.
[6]   Public Service Enterprise Group     "Updated Final Safety Analysis Report - Hope Creek Generating Station.
[3]
[71   Radiation Management Corporation.   "Artificial Island Radiological Environmental Monitoring Program - Annual Reports 1973 through 198.2".
United States Atomic Energy Commission.  
[8]   Radiation Management Corporation.   "Artificial Island Radiological Environmental Monitoring Program - Preoperation Summary - 1973 through 1976". RMC-TR-77-03, 1978.
"Final Environmental Statement Salem Nuclear Generating Station, Units 1 and 2".
[9]   Radiation Management Corporation.   "Artificial Island Radiological Environmental Monitoring Program - December 11 to December 31, 1976"..
Docket No. 50-272 and 50-311.
1973.
[4]
United States Atomic Energy Commission.  
"Final Environmental Statement Hope Creek Generating Station, Docket No.
50-354. 1983.
[5]
Public Service Enterprise Group "Updated Final Safety Analysis Report - Salem Nuclear Generating Station, Units 1 and 2".
1982.
[6]
Public Service Enterprise Group "Updated Final Safety Analysis Report - Hope Creek Generating Station.
[71 Radiation Management Corporation.  
"Artificial Island Radiological Environmental Monitoring Program - Annual Reports 1973 through 198.2".
[8]
Radiation Management Corporation.  
"Artificial Island Radiological Environmental Monitoring Program - Preoperation Summary -
1973 through 1976".
RMC-TR-77-03, 1978.
[9]
Radiation Management Corporation.  
"Artificial Island Radiological Environmental Monitoring Program  
- December 11 to December 31, 1976"..
RMC-TR-77-02, 1977.
RMC-TR-77-02, 1977.
[10]   PSEG Power LLC Maplewood Testing Services.     "Salem'and Hope Creek Generating Stations' Radiological Environmental Monitoring Program - Annual Reports 1983 through 2000".
[10]
[11]   PSEG Power LLCMaplewood Testing Services.   "Quality Assurance Plan."
PSEG Power LLC Maplewood Testing Services.  
"Salem'and Hope Creek Generating Stations' Radiological Environmental Monitoring Program - Annual Reports 1983 through 2000".
[11]
PSEG Power LLCMaplewood Testing Services. "Quality Assurance Plan."
June, 2001
June, 2001
[12]   Public Service Enterprise Group .    "Salem Nuclear Generating Station Technical Specifications",. Appendix A to Operating License No. DPR-70, 1976, Sections 6.8.4.h - 1,2,3 and 6.9.1.7.
[12]
[13)   Public Service Enterprise Group     "Hope Creek Generating Station Technical Specifications", Appendix A to Facility Operating License No. NPF-57, 1986, Sections 6.8.4.h - 1,2,3 and 6.9.1.6.
Public Service Enterprise Group "Salem Nuclear Generating Station Technical Specifications",. Appendix A to Operating License No.
[14]   Public Service Enterprise Group     "Offsite Dose Calculation Manual"
DPR-70, 1976, Sections 6.8.4.h -
        -  Salem Generating Station.
1,2,3 and 6.9.1.7.
[13)
Public Service Enterprise Group "Hope Creek Generating Station Technical Specifications", Appendix A to Facility Operating License No. NPF-57, 1986, Sections 6.8.4.h - 1,2,3 and 6.9.1.6.
[14]
Public Service Enterprise Group "Offsite Dose Calculation Manual" Salem Generating Station.
29
29


REFERENCES         (cont' d)
REFERENCES (cont' d)
[15] Public Service Enterprise Group     "Offsite Dose Calculation Manual"
[15]
    - Hope Creek Generating Station.
Public Service Enterprise Group  
[16] U.S. Environmental Protection Agency.   "Prescribed Procedures for Measurement of Radioactivity in Drinking Water.*I" ;E-PA-600/4-80-032, August, 1980.
- Hope Creek Generating Station.
"Offsite Dose Calculation Manual"
[16]
U.S. Environmental Protection Agency.  
"Prescribed Procedures for Measurement of Radioactivity in Drinking Water.*I" ;E-PA-600/4-80-032,
: August, 1980.
30
30


Line 361: Line 735:


==SUMMARY==
==SUMMARY==
31
31


RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION                           DOCKET 50-272/-311 HOPE CREEK GENERATING STATION                    DOCKET NO. 50-354 SALEM COUNTY, NEW JERSEY            JANL JARY 1, 2001 to DECEMBER 31, 2001 MEDIUM OR PATHWAY         Analysis And       Lower   All Indicator Locations   Location with Highest Mean               Control Location Number of SAMPLE                   Total Number       Limit of           Mean                       Name                   Mean         Mean       Nonroutine (UNIT OF MEASUREMENT)     of Analyses       Detection           (Range)             Distance and Direction       (Range)       (Range)       Reported Performed         (LLD)
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY JANL DOCKET 50-272/-311 DOCKET NO. 50-354 JARY 1, 2001 to DECEMBER 31, 2001 MEDIUM OR PATHWAY Analysis And Lower All Indicator Locations Location with Highest Mean Control Location Number of SAMPLE Total Number Limit of Mean Name Mean Mean Nonroutine (UNIT OF MEASUREMENT) of Analyses Detection (Range)
* Measurements I. AIRBORNE Air Particulates      Beta     318       6.0         23 (265 /265             14G1 11.8 mi WNW          25 (53/53)   25 (53/53)           0 (10.3 pCi/m3)                                                 (8-44)                                           (11-44)       (11-44)
Distance and Direction (Range)
Gamma Be7        24        7.2          56 (20/20)                2F6 7.3 mi NNE           62 (4/4)     53 (4/4)           0 (36-78)                                          (49-78)       (33-66)
(Range)
K-40        24        7.0          11 (13/20)              16E1 4.1 mi NNW          13 (2/4)     10 (2/4)           0 (7-14)                                          (12-14)       (9-11)
Reported Performed (LLD)
Air Iodine          1-131      318        10                < LLD                                           < LLD         < LLD          0 (10o- pCi/m 3 )
* Measurements Beta 318 6.0 23 (265 /265 (8-44)
II DIRECT Direct Radiation  Quarterly     196                   4.1   (172/172)             2S2 0.4 mi NNE           5.6 (4/4)   4.5 (24/24)         0 (mrad/std. month)  Badges                                (2.6-6.1)                                        (4.7-6.1)     (3.4-5.3)
Gamma Be7 24 7.2 K-40 24 7.0 1-131 318 10 Air Iodine (10o-pCi/m 3) 56 (20/20)
III TERRESTRIAL Milk              1-131      80        0.4                < LLD                                           < LLD        <LLD            0 (pCi/L)
(36-78) 11 (13/20)
Gamma K-40      80        50        1350 (60 /60)                2F9 7.5 mi NNE       1370 (20/20) 1310 (20/20)         0 (1220-1460)                                      (1250-1450) (1220-1390)
(7-14)
< LLD 14G1 11.8 mi WNW 2F6 7.3 mi NNE 16E1 4.1 mi NNW 25 (53/53)
(11-44) 25 (53/53)
(11-44) 62 (4/4) 53 (4/4)
(49-78)
(33-66) 13 (2/4) 10 (2/4)
(12-14)
(9-11)
< LLD
< LLD II DIRECT Direct Radiation (mrad/std. month)
III TERRESTRIAL Milk (pCi/L)
Quarterly Badges 196 1-131 80 0.4 Gamma K-40 80 50 4.1 (172/172)
(2.6-6.1) 2S2 0.4 mi NNE
< LLD 1350 (60 /60)
(1220-1460) 5.6 (4/4) 4.5 (24/24)
(4.7-6.1)
(3.4-5.3)
< LLD 2F9 7.5 mi NNE
<LLD 1370 (20/20) 1310 (20/20)
(1250-1450)
(1220-1390)
I. AIRBORNE Air Particulates (10.3 pCi/m3) 0 0
0 0
0 0
0


RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION                           DOCKET 50-272/-311 HOPE CREEK GENERATING STATION                    DOCKET NO. 50-354 SALEM COUNTY, NEW JERSEY            JANU ARY 1, 2001 to DECEMBER 31, 2001 MEDIUM OR PATHWAY       Analysis And       Lower   All Indicator Locations   Location with Highest Mean                 Control Location Number of SAMPLE                 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 III TERRESTRIAL Well Water          Alpha       12       1.7         2.2 &#xfd;9/12)               3E1 4.1 mi NE          2.2'  (9/12)  No Control
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY JANU DOCKET 50-272/-311 DOCKET NO. 50-354 ARY 1, 2001 to DECEMBER 31, 2001 MEDIUM OR PATHWAY Analysis And Lower All Indicator Locations Location with Highest Mean Control Location Number of SAMPLE Total Number Limit of Mean Name  
                                                                                                              - (1.2-2.6)                        0 (pCi/L)                                                  (1.2-2.6)                                                         Location Beta        12    1.0***          12 (12/12)               3E1 4.1 mi NE          12 (12/12)      No Control          0 (9.8-14)                                         (9.8-14)      Location H-3        12        180              < LLD                                              < LLD     No Control          0 Location Gamma K-40         12       30           71 (4/12)                 3E1 4.1mi NE          71 (4/12)      No Control          0 (48-85)                                           (48-85)      Location RA-NAT         12       2.9         146 (12/12)                 3E1 4.1mi NE        146 (12/12)      No Control          0 (90-193)                                         (90-193)      Location Potable Water        Alpha         24       1.0         0.9 (17/24)               2F3 8.0 mi NNE        0.9 (17/24)      No Control          0 (pCi/L)                                                      (0.6-1.6)                                         (0.6-1.6)      Location Beta         24     1.0***       3.4 (24/24)               2F3 8.0 mi NNE          3.4 (24124)      No Control          0 (2.7-4.7)                                         (2.7-4.7)    -Location H-3       24       180               < LLD                                             < LLD      No Control          0 Location Gamma K-40       24         30'         44 (11 /24)             2F3 8.0 mi NNE          44 (11 /24)    No Control          0 (26-70)                                          (26-70)       Location.
'Mean Mean Nonroutine (UNIT OF MEASUREMENT) of Analyses Detection (Range)
1-131        24       0.3               <LLD                                              < LLD     No Control          0 Location RA-NAT       24'       2.9         5.4 (5/24)               2F3 8.0 mi NNE           5.4 (5 /24)     No Control           0 (4-6.5)                                           (4-6.5)       Location
Distance and Direction (Range)
(Range)
Reported Performed (LLD)*
Measurements Alpha 12 1.7 Beta 12 1.0***
H-3 Potable Water (pCi/L) 12 180 2.2 &#xfd;9/12)
(1.2-2.6) 12 (12/12)
(9.8-14)  
< LLD Gamma K-40 12 30 71 (4/12)
(48-85)
RA-NAT 12 2.9 146 (12/12)
(90-193)
Alpha 24 1.0 0.9 (17/24)
(0.6-1.6)
Beta 24 1.0***
3.4 (24/24)
(2.7-4.7)
H-3 24 180  
< LLD Gamma K-40 1-131 24 30' 44 (11 /24)
(26-70) 24 0.3  
<LLD RA-NAT 24' 2.9 5.4 (5/24)
(4-6.5) 3E1 4.1 mi NE 3E1 4.1 mi NE 3E1 4.1mi NE 3E1 4.1mi NE 2F3 8.0 mi NNE 2F3 8.0 mi NNE 2F3 8.0 mi NNE 2F3 8.0 mi NNE 2.2' (9/12)
-(1.2-2.6) 12 (12/12)
(9.8-14)
< LLD 71 (4/12)
(48-85) 146 (12/12)
(90-193) 0.9 (17/24)
(0.6-1.6) 3.4 (24124)
(2.7-4.7)
< LLD No Control Location No Control Location No Control Location No Control Location No Control Location No Control Location No Control
-Location No Control Location 44 (11 /24)
No Control (26-70)
Location.
< LLD No Control Location 5.4 (5 /24)
No Control (4-6.5)
Location III TERRESTRIAL Well Water (pCi/L) 0 0
0 0
0 0
0 0
0 0
0


RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION                         DOCKET 50-272/-311 HOPE CREEK GENERATING STATION                  DOCKET NO. 50-354 SALEM COUNTY, NEW JERSEY          JANLJARY 1, 2001 to DECEMBER 31, 2001 MEDIUM OR PATHWAY       Analysis And       Lower   All Indicator Locations   Location with Highest Mean               Control Location Number of SAMPLE                 Total Number       Limit of           Mean                     Name                   Mean           Mean       Nonroutine (UNIT OF MEASUREMENT)   of Analyses     Detection         (Range)           Distance and Direction       (Range)       (Range)       Reported Performed       (LLD)
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY JANL DOCKET 50-272/-311 DOCKET NO. 50-354 JARY 1, 2001 to DECEMBER 31, 2001 MEDIUM OR PATHWAY Analysis And Lower All Indicator Locations Location with Highest Mean Control Location Number of SAMPLE Total Number Limit of Mean Name Mean Mean Nonroutine (UNIT OF MEASUREMENT) of Analyses Detection (Range)
* Measurements III TERRESTRIAL       Gamma K-40       29       70       2090 (14/14)             14G2 12.1 mi WNW          2460 (2/2)  2060 (15 /15)        0 Fruit &
Distance and Direction (Range)
(1420-2570)                                     (2290-2620)  (1230-2710)
(Range)
Vegetables 15           16 (1 /1)               6F2 8.2 mi ESE          16 (1 /1)       < LLD            0 (pCi/Kg-wet)      RA-NAT       29 (16)                                              (16)
Reported Performed (LLD)
Game              Gamma 11D1 3.5miSW            2840 (1 /1)  2840 '(1/1)          0 (pCi/Kg-wet)        K-40         2        70         2600 (1/1)
* Measurements III TERRESTRIAL Fruit &
(2600)                                           (2840)       (2840)
Vegetables (pCi/Kg-wet)
Fodder Crops      Gamma (pCi/Kg-wet)       Be-7        6        35          420 (3/5)               2F9 7.5 mi NNE          670 (1/1)     350 (1 /i          0 (210-670)                                           (670)         (350) 6        70          8430 (5/5)               11F3 5.3 mi SW        9950 (2/2)   4380 (1 /1 )         0 K-40 (2560-16800)                                     (4990-14900)   (4380-4380) 20 (1 /5)            14F4 7.6 mi. WNW           20 (1/1)     10 (1/1)           0 RA-NAT        6        14 (20)                                             (20)         (10)
Game (pCi/Kg-wet)
Soil            Gamma Be-7        9        80          210 (3/8)               11F3 5.3 mi. SW          360 (1 /1)       < LLD          0 (pCi/kg (dry)
Fodder Crops (pCi/Kg-wet)
(120-360)                                           (360) 9        70          8850 (8/8)             14F4 7.6 mi. WNW        12900 (1 /1)   8190 (1./1)         0 K-40 (4610-12900)                                         (12900)        (8190)
Gamma K-40 RA-NAT Gamma K-40 Gamma Be-7 K-40 29 70 2090 (14/14)
Cs-137        9        33          210 (7/8)             S1ODI -3.9 mi. SSW        350 (1 /1)   160 (1 /1)         0 (26-350)                                           (350)         (160) 9        45          660 (8/8)               11F3 5.3 mi. SW        970 (1 /1)   700 (1 /1)           0 Ra-NAT (260-970)                                           (970)        (700)
(1420-2570) 29 15 16 (1 /1)
Th-232        9        50          790 (8/8)               11F3 5.3 mi. SW        1200 (1 /1)   850 (1/1)           0 (350-1200)                                         (1200)         (850)
(16) 2 70 6
35 6
70 RA-NAT 6
14 Soil (pCi/kg (dry)
Gamma Be-7 K-40 9
80 9
70 Cs-137 9
33 Ra-NAT 9
45 Th-232 9
50 2600 (1/1)
(2600) 420 (3/5)
(210-670) 8430 (5/5)
(2560-16800) 20 (1 /5)
(20) 210 (3/8)
(120-360) 8850 (8/8)
(4610-12900) 210 (7/8)
(26-350) 660 (8/8)
(260-970) 790 (8/8)
(350-1200) 14G2 12.1 mi WNW 6F2 8.2 mi ESE 11D1 3.5miSW 2F9 7.5 mi NNE 11F3 5.3 mi SW 14F4 7.6 mi. WNW 11F3 5.3 mi. SW 14F4 7.6 mi. WNW S1ODI -3.9 mi. SSW 11F3 5.3 mi. SW 11F3 5.3 mi. SW 2460 (2/2)
(2290-2620) 16 (1 /1)
(16) 2060 (15 /15)
(1230-2710)  
< LLD 2840 (1 /1) 2840 '(1/1)
(2840)
(2840) 670 (1/1)
(670) 9950 (2/2)
(4990-14900) 20 (1/1)
(20) 360 (1 /1)
(360) 12900 (1 /1)
(12900) 350 (1 /1)
(350) 970 (1 /1)
(970) 1200 (1 /1)
(1200) 350 (1 /i (350) 4380 (1 /1 )
(4380-4380) 10 (1/1)
(10)  
< LLD 8190 (1./1)
(8190) 160 (1 /1)
(160) 700 (1 /1)
(700) 850 (1/1)
(850) 0 0
0 0
0 0
0 0
0 0
0


RADIOLOGICAL ENVIRONMENTAL MONITORING           PROGRAM SALEM GENERATING STATION                           DOCKET 50-272/-311 HOPE CREEK GENERATING STATION                    DOCKET NO. 50-354 SALEM COUNTY, NEW JERSEY            JANUJARY 1, 2001 to DECEMBER 31, 2001 MEDIUM OR PATHWAY       Analysis And         Lower     All Indicator Locations   Location with Highest Mean               Control Location Number of SAMPLE                 Total Number       Limit of             Mean                     Name                   Mean         Mean       Nonroutine (UNIT OF MEASUREMENT)   of Analyses       Detection           (Range)           Distance and Direction         (Range)     (Range)       Reported Performed         ILLD)
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY JANU DOCKET 50-272/-311 DOCKET NO. 50-354 JARY 1, 2001 to DECEMBER 31, 2001 MEDIUM OR PATHWAY Analysis And Lower All Indicator Locations Location with Highest Mean Control Location Number of SAMPLE Total Number Limit of Mean Name Mean Mean Nonroutine (UNIT OF MEASUREMENT) of Analyses Detection (Range)
* Measurements IV AQUATIC Surface Water        Beta       60       3.8           82 (48/48)               7E1 4.5 mi SE        118 (12/12)   71 (12/12)           0 (pCi/L)                                                     (4.7-224)                                         (34-224)     (6.4-129)
Distance and Direction (Range)
H-3        20        180                < LLD                                                           < LLD           0 Gamma K-40         60        30            95 (45/48)               11A1 0.2 miSW         111 (12/12)   99 (11 /12)
(Range)
(42-178)                                         (54-178)     (38-165)         0 Blue Crabs          Gamma (pCi/kg-wet)         K-40          4        70            2710 (2 /2)           12CI 2.5 mi WSW          2870 (2/2)     2870 (2/2)
Reported Performed ILLD)
(2510-2910)                                      (2660-3080)   (2660-3080)        0 Edible Fish          Sr-89        1      600                <LLD (pCi/kg-dry)
* Measurements Beta 60 3.8 H-3 Gamma K-40 Gamma K-40 Sr-89 (bones)
                                                                                                                  "<LLD         "<LLD (bones)                                                                                                                  0 Sr-90        1      130                < LLD                                            "<LLD (bones)
Sr-90 (bones)
                                                                                                                                "<LLD 0
Gamma K-40 Blue Crabs (pCi/kg-wet)
(pCi/kg-wet)      Gamma K-40        6        70            3530 -(4 /4)            12C1 2.5 mi WSW          3675 (2/2)   3675 (2/2)
Edible Fish (pCi/kg-dry)
(3240-3910)                                      (3650-3700)   (3650-3700)         0 Sediment (pCi/kg-dry)       Gamma Be-7        14        80            550 (5/12)               11A1 0.2 mi SW          870 (1 /2)   350 (1 /2)
(pCi/kg-wet)
(220-870)                                          (870)        (350)           0 K-40        14        70        11550 (12/12)              12C1 2.5 mi WbW          15600 (2/2)   15600 (2/2)
Sediment (pCi/kg-dry) 20 180 60 30 4
(1020-15900)                                                                        0 (15600)      (15600)
70 1
Co-60        14        22                <LLD                                              < LLD        < LLD 0
600 1
130 6
70 82 (48/48)
(4.7-224)  
< LLD 95 (45/48)
(42-178) 2710 (2 /2)
(2510-2910)  
<LLD  
< LLD 3530 -(4 /4)
(3240-3910)
Gamma Be-7 14 80 550 (5/12)
(220-870)
K-40 14 70 11550 (12/12)
(1020-15900)
Co-60 14 22
<LLD 7E1 4.5 mi SE 11A1 0.2 miSW 12CI 2.5 mi WSW 118 (12/12)
(34-224) 111 (12/12)
(54-178) 71 (12/12)
(6.4-129)  
< LLD 99 (11 /12)
(38-165) 2870 (2/2) 2870 (2/2)
(2660-3080)
(2660-3080)
LLD LLD 12C1 2.5 mi WSW 11A1 0.2 mi SW 12C1 2.5 mi WbW
"<LLD LLD 3675 (2/2) 3675 (2/2)
(3650-3700)
(3650-3700) 870 (1 /2)
(870) 15600 (2/2)
(15600)
< LLD 350 (1 /2)
(350) 15600 (2/2)
(15600)
< LLD IV AQUATIC Surface Water (pCi/L) 0 0
0 0
0 0
0 0
0 0


RADIOLOGICAL ENVIRONMENTAL MONITORING             PROGRAM SALEM GENERATING STATION                           DOCKET 50-272/-311 HOPE CREEK GENERATING STATION                    DOCKET NO. 50-354 SALEM COUNTY, NEW JERSEY          JANL IARY 1, 2001 to DECEMBER 31, 2001 MEDIUM OR PATHWAY                   Analysis And         Lower   All Indicator Locations   Location with Highest Mean                     Control Location Number of SAMPLE                             Total Number         Limit of           Mean                       Name                     Mean           Mean         Nonroutine (UNIT OF MEASUREMENT)               oft Analyses,     Detection         (Range)             Distance and Direction           (Range)         (Range)       Reported Performed         (LLD)
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY JANL DOCKET 50-272/-311 DOCKET NO. 50-354 IARY 1, 2001 to DECEMBER 31, 2001 MEDIUM OR PATHWAY Analysis And Lower All Indicator Locations Location with Highest Mean Control Location Number of SAMPLE Total Number Limit of Mean Name Mean Mean Nonroutine (UNIT OF MEASUREMENT) oft Analyses, Detection (Range)
* Measurements IV AQUATIC Sediment                       Cs-134       14       27           23 (2/12)                   7E1 4.5 mi SE            27 (1 /2)          < LLD            0 (19-27)                                                (27)
Distance and Direction (Range)
(pCi/kg-dry)
(Range)
Cs-137       14       33           59 (9/12)               16A1 0.7 mi NNW              98 (2/2)        58 (1 /2)          0 (19-120)                                            (76-120)          (58)
Reported Performed (LLD)
RA-NAT         14       45         530 (12/12)               12C1 2.5 mi WSW            690 (2/2)        690 (2/2)          0 (96-760)                                            (550-820)        (550-820)
* Measurements IV AQUATIC Sediment (pCi/kg-dry)
Th-232       14       50         710 (12/12)               16F1 6.9 mi NNW             995 (2/2)        790 (2/2)          0 (82-1130)                                          (860-1130)      (480-1100)
Cs-134 14 27 23 (2/12)
* LLD listed is the lower limit of detection which we endeavored to achieve during this reporting period. In some instances nuclides were detected at concentrations above the LLD values shown. All strontium results are reported by DESEL as MDC..
(19-27)
  **   Mean calculated using values above LLD only. Fraction of measurements above LLD are in parentheses.
Cs-137 14 33 59 (9/12)
(19-120)
RA-NAT 14 45 530 (12/12)
(96-760)
Th-232 14 50 710 (12/12)
(82-1130) 7E1 4.5 mi SE 16A1 0.7 mi NNW 12C1 2.5 mi WSW 16F1 6.9 mi NNW
* LLD listed is the lower limit of detection which we endeavored to achieve during this reporting period. In some instances nuclides were detected at concentrations above the LLD values shown. All strontium results are reported by DESEL as MDC..  
** Mean calculated using values above LLD only. Fraction of measurements above LLD are in parentheses.
Typical LLD values.
Typical LLD values.
27 (1 /2)
(27) 98 (2/2)
(76-120) 690 (2/2)
(550-820) 995 (2/2)
(860-1130)
< LLD 58 (1 /2)
(58) 690 (2/2)
(550-820) 790 (2/2)
(480-1100) 0 0
0 0


APPENDIX B SAMPLE DESIGNATION AND LOCATIONS 39
APPENDIX SAMPLE DESIGNATION AND LOCATIONS 39 B


APPENDIX B SAMPLE DESIGNATION The PSEG's Maplewood Testing Services 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.
APPENDIX B SAMPLE DESIGNATION The PSEG's Maplewood Testing Services identifies samples by a three part code.
AIO  = Air Iodine               IDM    Immersion Dose (TLD)
The first two letters are the program identification code.
APT  = Air Particulate           MLK    Milk ECH = Hard Shell Blue Crab     PWR    Potable Water (Raw)
Because of the proximity of the Salem and Hope Creek Stations a common environmental surveillance program is being conducted.
ESF = Edible Fish               PWT    Potable Water (Treated)
The identification code, "SA",
ESS = Sediment                 SOL    Soil FPL = Green Leafy Vegetables   SWA    Surface Water FPV = Vegetables (Various)     VGT     Fodder Crops (Various)
has been applied to Salem and Hope Creek stations.
GAM = Game (Muskrat)            WWA    Well Water The last four symbols are a location code based on direction and distance from a standard reference point.       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; e.g., 2=NNE, 3=NE, 4=ENE, etc. The next digit is a letter which represents the radial distance from the reference point:
The next three letters are for the media sampled.
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,...       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 450 (north east) with respect to the reactor site 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.
= Air Iodine  
41
= Air Particulate  
= Hard Shell Blue Crab  
= Edible Fish  
= Sediment  
= Green Leafy Vegetables  
= Vegetables (Various)  
= Game (Muskrat)
IDM MLK PWR PWT SOL SWA VGT WWA Immersion Dose (TLD)
Milk Potable Water (Raw)
Potable Water (Treated)
Soil Surface Water Fodder Crops (Various)
Well Water The last four symbols are a location code based on direction and distance from a standard reference point.
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; e.g.,
2=NNE, 3=NE, 4=ENE, etc.
The next digit is a
letter which represents the radial distance from the reference point:
S = On-site location A = 0-1 miles off-site B = 1-2 miles off-site C = 2-3 miles off-site D = 3-4 miles off-site E =
4-5 miles off-site F =
5-10 miles off-site G =
10-20 miles off-site H =  
>20 miles off-site The last number is the station numerical designation within each sector and zone; e.g., 1,2,3,...
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 450 (north east) with respect to the reactor site 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.
41 AIO APT ECH ESF ESS FPL FPV GAM


TABLE B- 1 SAMPLING LOCATIONS Specific information about the individual sampling locations are given in Table B-I.
TABLE B-1 SAMPLING LOCATIONS Specific information about the individual sampling locations are given in Table B-I.
Maps B-I 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.
Maps B-I 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.
The Datem used was WGS 84.
The Datem used was WGS 84.
STATION CODE                         STATION LOCATION                       LATITUDINAL          LONGITUDINAL                  SAMPLE TYPE DEG. MIN. SEC        DEG. MIN. SEC -
STATION CODE ISi 2S2 2S4 3S1 4S1 5S1 4-6S2 7S1 15SI 16SI 11A1 15AI 16A1 12Cl 4D2 5DI 10DI lID1 14D1 15D1 2El 3E1 STATION LOCATION 0.55mi.
ISi      0.55mi. N of vent                                       39 16        75 15              IDM 2S2      0.4 mi. NNE of vent                                     39 - 28        07
N of vent 0.4 mi.
                                                                                    -      75    -  31 -    57      IDM 2S4      0.59 mi. NNE of vent                                   39    -  28    16
NNE of vent 0.59 mi.
                                                                                    -      75    -  31 -    55      IDM 3S1      0.58 mi. NE of vent                                     39 - 28        08
NNE of vent 0.58 mi.
                                                                                    -      75    -  31 - 41          IDM 4S1      0.60 mi. ENE of vent                                   39    -  28    02
NE of vent 0.60 mi.
                                                                                    -      75    -  31  -  33      IDM 5S1      1.0 mi. E of vent;   site     access road             39--    27    38  75
ENE of vent 1.0 mi.
                                                                                    -            -  31  -  08      AIO,APT, IDM 4-  6S2      0.2 mi. ESE of vent;       observation building           39 - 27        43  75    -  31 -    55      IDM, SOL., ESS',
E of vent; site access road 0.2 mi. ESE of vent; observation building 0.12 mi.
7S1      0.12 mi. SE of vent;       station   personnel gate     39 - 27        44  75      32 -    03      IDM 0.14 mi. SSW of vent;     inlet   cooling water bldg. 39 - 27        39, 75        32 -    10      IDM 0.09 mi. SW of vent;     service water inlet   bldg. 39 - 27    -  43  75    -32    -  12      IDM 15SI      0.57 mi. NW of vent                                     39 - 28    -  10  75    -  32  - 32      IDM 16SI      0.54 mi. NNW of vent                                   39 - 28        13
SE of vent; station personnel gate 0.14 mi.
                                                                                    -      75    -  32  - 26      IDM 11A1      0.2 mi. SW of vent; outfall         area                 39 - 27        59
SSW of vent; inlet cooling water bldg.
                                                                                    -      75    -  32  -  25      ECH, ESF, ESS, SWA 15AI      0.3 mi. NW of vent; cooling tower blowdown               39 - 27    -  67  75    -  32  -  19      ESS discharge line outfall 16A1      0.7 mi. NNW of vent; south storm drain discharge         39      28
0.09 mi.
                                                                            -      -  24  75 - 32      -  58      ESS line 12Cl      2.5 mi. WSW of vent; west bank of Delaware River       39  -  27    22  75  -  34      08      ECH, ESF, ESS, SWA 4D2      3.7  mi. ENE of vent; Alloway Creek Neck Road           39      29
SW of vent; service water inlet bldg.
                                                                            -          18  75  -  32              IDM 5DI      3.5  mi. E of vent;   local farm                         39      28    24
0.57 mi.
                                                                            -              75  -  28  -  22      AIO,APT, IDM 10DI      3.9  mi. SSW of vent; Taylor's Bridge Spur               39      24
NW of vent 0.54 mi.
                                                                            -          37  75  -  33  -  44      IDM, SOL''
NNW of vent 0.2 mi.
lID1      3.5  mi. SW of vent                                     39  -    24    49  75  -  34  -  26      GAM 14D1      3.4  mi. WNW of vent;     Bay View,     Delaware         39  -  29    02  75  -  35  -31        IDM 15D1      3.8  mi. NW of vent; Rt.       9, Augustine Beach       39  -  30    08  75  -  35  -  02      IDM 2El      4.4  mi. NNE of vent;     local farm                     39   -   31 L 23     75   -   30  -   26     IDM 3E1      4.1 mi. NE of vent;    local farm                      39 -     30 -   07   75  -  28 -   41     GAM, IDM,VGT,WWA,FPV
SW of vent; outfall area 0.3 mi.
NW of vent; cooling tower blowdown discharge line outfall 0.7 mi.
NNW of vent; south storm drain discharge line 2.5 3.7 3.5 3.9 3.5 3.4 3.8 4.4 mi.
mi.
mi.
mi.
mi.
mi.
mi.
mi.
WSW of vent; west bank of Delaware River ENE of vent; Alloway Creek Neck Road E of vent; local farm SSW of vent; Taylor's Bridge Spur SW of vent WNW of vent; Bay View, Delaware NW of vent; Rt.
9, Augustine Beach NNE of vent; local farm 4.1 mi.
NE of vent; local farm LATITUDINAL DEG.
MIN.
SEC 39 -
28 16 39 -
28 -
07 39 -
28 16 39 -
28 08 39 -
28 02 39--
27 -
38 39 -
27 43 39 - 27 44 39 -
27 39, 39 -
27 -
43 39 -
28 -
10 39 -
28 -
13 39 - 27 59 39 -
27 67 39 28 24 39 39 39 39 39 39 39 39 27 29 28 24 24 29 30 31 L 22 18 24 37 49 02 08 23 LONGITUDINAL DEG.
MIN.
SEC -
75 75 75 75 75 75 75 75 75 75 75 75 75 75 32 -
15 31 -
57 31 -
55 31 -
41 31 33 31 08 31 -
55 32 -
03 32 -
10
-32 12 32 32 32 26 32 -
25 32 19 75 -
32 58 75 75 75 75 75 75 75 75 75 39 -
30 -
07 34 32 28 33 34 35 35 30 28 08 22 44 26
-31 02 26 41 SAMPLE TYPE IDM IDM IDM IDM IDM AIO,APT, IDM IDM, SOL., ESS',
IDM IDM IDM IDM IDM ECH, ESF, ESS, SWA ESS ESS ECH, ESF, ESS, SWA IDM AIO,APT, IDM IDM, SOL''
GAM IDM IDM IDM GAM, IDM,VGT,WWA,FPV


TABLE B-1   (cont' d)
TABLE B-1 (cont' d)
STATION CODE                     STATION LOCATION                       LATITUDINAL        LONGITUDINAL      SAMPLE TYPE DEG. MIN. SEC      DEG. MIN.     SEC 1 mi. W of Mad Horse Creek      39      25  - 08  75    28 - 64      ESF,ESS,SWA 7E1    4.5 mi. SE of vent; S of vent                                      39      24  - 10  75    32  -  42    IDM 9E1    4.2 mi.
STATION CODE 7E1 9E1 11E2 12E1 13E1 16El IF1 1F2 2F2 2F3 2F4 2F5 2F6 2F7 t
39      24  - 20  75    35  - 33    IDM 11E2    5.0 mi. SW of vent; Rt. 9 39      26  - 52  75    36  - 59    IDM 12E1    4.4 mi. WSW of vent; Thomas Landing 39    *27  -  59 75    36  - 44    IDM 13E1    4.2 mi. W of vent; Diehl House Lab NNW of vent; Port Penn                         39      30  - 47  75    34  -  34    AIO,APT, IDM,SOL 16El    4.1 mi.
2F8 2F9 3F2 3F3 3F5 3F6 3F8 4F2 5F1 6F1 6F2 7F2 10F2 1IF!
39      32  - 45  75    31  -  06    AIO,APT, IDM IF1    5.8 mi.  "Nof vent; Fort Elfsborg 39      33  -  08 75    32  -  54    SWA 1F2    7.1 mi.  "Nof vent; midpoint of Delaware River 2F2    8.7 mi. NNE of vent; Corner of 5t     &Howell,       39      34  -  38 75    28  -  04    IDM Salem 39      33  -  40 75    27  -  18    PWR, PWT 2F3    8.0 mi. NNE of vent; Salem Water Company 39      33  -  21 75    30  -  33    FPV, FPL 2F4    6.3 mi. NNE of vent; local farm 39      33  -  27 75    28  -  31    IDM 2F5    7.4 mi. NNE of vent; Salem High School 39      33  -  43 75    28  -  48    AIO,APT, IDM 2F6    7.3 mi. NNE of vent; Southern Training Center 39      32  -  40 75    30  -  53    SOL 2F7    5.7 mi. NNE of vent; local farm 39      31  -  54 75    29  -  18    FPV t 2F8    5.3 mi. NNE OF vent; local farm 45 S.        39      33  -  55 75    29  -  30    MLK,FPV,VGT,SOL 2F9    7.5 mi. NNE of vent; Tilbury Farms       ,
11F3 12F1 STATION LOCATION 4.5 mi.
Tilbury Rd, Salem                                                                             IDM Eridge Municipal Bld     39      30      25 75    27  -  36 3F2    5.1 mi. NE of vent;Hancocks                                        -
4.2 mi.
Quinton Township School           39      32  -  38 75    24  -  45    IDM 3F3    8-.6 mi. NE of vent; 39    33  -  29 75    24  -  54    FPV 3F5    9.4 mi. NE of vent; Harris's Farm Market 39  -  32      03 75  - 28  -  00    FPV 3F6    *6.5 mi. NE of vent; #324 Salem/Hancocks     Bridge Road                                                                                          FPV,FPL 5.1 mi. NE of vent; 33 Maple Ave.,     Hancocks       39 -  30  -25  75 -  27 -  37 3F8 Bridge Harmersville        39    29  -  58 75  - 26  - 03    IDM 4F2    6.0 mi. ENE of vent; Mays Lane, E of vent; Canton                               39    28  - 22  75  - 24  - 59    IDM,SOL 5F1    6.5 mi.
5.0 mi.
Stow Neck Road                  39    26  -  24 75  - 25  - 09    IDM 6F1    6.4 mi. ESE of vent; NJ    39    26  -  04 75  - 23  - 09    FPV, FPL 6F2    8.2 mi. ESE of vent; RD#3 Box 160 Bridgeton, 39    22  -  56 75    24  -  17  IDM 7F2    9.1 mi. SE of vent; Bayside, New Jersey 39      23  -  01 75    34  -  09  IDM 10F2    5.8  mi. SSW of vent; Rt. 9 39      24  -  44 75    37  -  37  IDM 1IF!    6.2  mi. SW of vent; Taylor's Bridge Delaware Townsend,   Delaware               39     24 - 06 75     36 - 20   MLK,VGT, SOL 11F3    5.3  mi. SW of vent; 39      23  - 47 75    41  -  18  IDM 12F1    9.4  mi. WSW of vent; Townsend Elementary School 13F2   6.5 mi. W of vent; Odessa,   Delaware21               &#xfd;39, - 27     7 18 75 21       IDM
4.4 mi.
4.2 mi.
4.1 mi.
5.8 mi.
7.1 mi.
8.7 mi.
Salem 8.0 mi.
6.3 mi.
7.4 mi.
7.3 mi.
5.7 mi.
5.3 mi.
7.5 mi.
Tilbury 5.1 mi.
8-.6 mi.
9.4 mi.
*6.5 mi.
Road 5.1 mi.
Bridge 6.0 mi.
6.5 mi.
6.4 mi.
8.2 mi.
9.1 mi.
5.8 mi.
6.2 mi.
5.3 mi.
9.4 mi.
SE of vent; 1 mi.
W of Mad Horse Creek S of vent SW of vent; Rt.
9 WSW of vent; Thomas Landing W of vent; Diehl House Lab NNW of vent; Port Penn "N of vent; Fort Elfsborg "N of vent; midpoint of Delaware River NNE of vent; Corner of 5t  
&Howell, NNE of vent; Salem Water Company NNE of vent; local farm NNE of vent; Salem High School NNE of vent; Southern Training Center NNE of vent; local farm NNE OF vent; local farm NNE of vent; Tilbury Farms  
, 45 S.
Rd, Salem NE of vent;Hancocks Eridge Municipal Bld NE of vent; Quinton Township School NE of vent; Harris's Farm Market NE of vent; #324 Salem/Hancocks Bridge NE of vent; 33 Maple Ave.,
Hancocks ENE of vent; Mays Lane, Harmersville E of vent; Canton ESE of vent; Stow Neck Road ESE of vent; RD#3 Box 160 Bridgeton, NJ SE of vent; Bayside, New Jersey SSW of vent; Rt.
9 SW of vent; Taylor's Bridge Delaware SW of vent; Townsend, Delaware WSW of vent; Townsend Elementary School LATITUDINAL DEG.
MIN.
SEC 39 39 39 39 39 39 39 39 39 39 39 39 39 39 39 39 39 39 39 39 -
25 24 24 26
*27 30 32 33 34 33 33 33 33 32 31 33 08 10 20 52 59 47 45 08 38 40 21 27 43 40 54 55 LONGITUDINAL DEG.
MIN.
SEC 75 75 75 75 75 75 75 75 75 75 75 75 75 75 75 75 75 75 75 75 30 25 32 -
38 33 29 32 03 39 -
30 -25 39 39 39 39 39 39 39 39 39 29 28 26 26 22 23 24 24 23 58 22 24 04 56 01 44 06 47 28 32 35 36 36 34 31 32 28 27 30 28 28 30 29 29 27 24 24 28 64 42 33 59 44 34 06 54 04 18 33 31 48 53 18 30 36 45 54 00 75 -
27 -
37 75 75 75 75 75 75 75 75 75 26 24 25 23 24 34 37 36 41 03 59 09 09 17 09 37 20 18 SAMPLE TYPE ESF,ESS,SWA IDM IDM IDM IDM AIO,APT, IDM,SOL AIO,APT, IDM SWA IDM PWR, PWT FPV, FPL IDM AIO,APT, IDM SOL FPV MLK,FPV,VGT,SOL IDM IDM FPV FPV FPV,FPL IDM IDM,SOL IDM FPV, FPL IDM IDM IDM MLK, VGT, SOL IDM 13F2 6.5 mi.
W of vent; Odessa, Delaware21
&#xfd;39, - 27 7 18 75 21 IDM


TABLE B-I     (cont'd)
TABLE B-I (cont'd)
STATION CODE                         STATION LOCATION                       LATITUDINAL              LONGITUDINAL                SAMPLE TYPE DEG. MIN. SEC            "DEG. MIN.          SEC 13F3      9.3 mi. W ofvent; Redding Middle School,               39    -  27 -    14    75    -  42    -  32      IDM Middletown, Delaware 13F4      9.8 mi. W of vent; Middletown, Delaware                 39        26    -  51    75      43    - 07        IDM 14F2      6.6 mi. WNW of vent; Boyds Corner                      39        30    -  00    75      38    - 59      IDM 14F3      5.4 mi. WNW of vent; local farm                        39        29    -  33    75      37    - 55      FPV, FPL 14F4      7.6 mi. WNW of vent; local farm                        39        30    - 44    75      40  -  52      MLK,VGT,SOL.
STATION CODE 13F3 13F4 14F2 14F3 14F4 15F3 16F1 16F2 IGI 1G3 IG4 2G2 3G1
15F3      5.4 mi. NW of vent                                      39        30        58    75      36
&#xfd;4-9G1 10GI 14GI 14G2 16G1 3H1 3H5 3H3 STATION LOCATION 9.3 mi.
                                                                                          -                      -  36      IDM 16F1      6.9 mi. NNW of vent; C&D Canal                         39        33    - 55    75      34  -  25      ESS,SWA 16F2        8.1 mi. NNW of vent; Delaware City Public School       39        34        18    75      35      25
W ofvent; Redding Middle School, Middletown, Delaware 9.8 mi.
                                                                                          -                      -          IDM IGI        10.3 mi. N of vent; local farm                           39        36        31    75      29
W of vent; Middletown, Delaware 6.6 mi.
                                                                                        -                      -  59      FPV, FPL 1G3        19 mi. N of vent; N. Church St. Wilmington, Del ,*      39      44        16  -75      32
5.4 mi.
                                                                                        -                          31      IDM IG4        10.8 mi. N of vent; (Dads Produce);Rte. 49, South       39        37    -  55  75        30      44 Broadway, Pennsville
7.6 mi.
                                                                                                        -                    FPV 2G2        13.5 mi. NNE of vent; Moore's Market; 324 Pointers       39    -  38        19  75    -
5.4 mi.
Auburn Road (Rt.. 540), Salem, NJ 08079
6.9 mi.
                                                                                          -                26  -    10      FPV 3G1        17 mi. NE of vent; Mr. Lee Williams Farm                 39        35        56  75
8.1 mi.
                                                                              -          -                16  -  47      IDM,MLK,VGT,SOL
10.3 mi.
&#xfd;4-  9G1        10.3 mi. S of Vent; Mr. Goldsburrough-, 1784             39        18 -      47  75 Woodland Beach Rd., Smyrnas, Delaware
WNW of vent; Boyds Corner WNW of vent; local farm WNW of vent; local farm NW of vent NNW of vent; C&D Canal NNW of vent; Delaware City Public School N of vent; local farm 19 mi.
                                                                              -                        -  33  -  50      FPV 10GI      12 mi. SSW of vent; Smyrna, Delaware                     39        18        13  75
N of vent; N.
                                                                              -        -                36  -  05      IDM 14GI      11.8 mi. WNW of vent; Rte. 286; Bethel Church Road;     39      31        18  75
Church St. Wilmington, Del 10.8 mi.
                                                                              -        -              -  46  -    30      AIO,APT, IDM Delaware 14G2      12.1 mi. WNW of vent; Locust Grove Farm & Garden       39' -    31        21    75 57 Center; 1084 Bethel Church Road; Middletown, DE
N of vent; (Dads Produce);Rte.
                                                                                        -                                  FPV 19709 16G1      15 mi. NNW of vent; Greater Wilmington Airport         39        40        32
49, South Broadway, Pennsville 13.5 mi.
                                                                            -                    75  -  35              IDM 3H1        32 mi. NE of vent; National Park, New Jersey           39        51        36    75  -    11
NNE of vent; Moore's Market; 324 Pointers Auburn Road (Rt.. 540),
                                                                            -                                - 06        IDM 3H5        25 mi. NE of vent; Sorbello Girl's:Market               39        41        02    75      12
Salem, NJ 08079 17 mi.
                                                                            -                        -        -    23      FPL, FPV 3H3        110 mi. NE of vent; Maplewood Testirng Services         40       43       25   74
NE of vent; Mr. Lee Williams Farm 10.3 mi.
                                                                            -         -             -   15 -    09     IDM NOTE:   All station locations are referenced to the midpoint of the two Salem Units' Vents.          The coordinates of this location are:   Latitude N 390 - 27' - 45.3" and Longitude W 750 - 32'     -    09.7".
S of Vent; Mr.
All Game (GAM), 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 Station's ODCM.               Vegetable samples are not always collected in consecutive years from the same farmer since they rotate the type of crop they grow.
Goldsburrough-, 1784 Woodland Beach Rd.,
: Smyrnas, Delaware 12 mi.
SSW of vent; Smyrna, Delaware 11.8 mi.
WNW of vent; Rte. 286; Bethel Church Road; Delaware 12.1 mi.
WNW of vent; Locust Grove Farm & Garden Center; 1084 Bethel Church Road; Middletown, DE 19709 15 mi.
NNW of vent; Greater Wilmington Airport 32 mi.
NE of vent; National Park, New Jersey 25 mi.
NE of vent; Sorbello Girl's:Market 110 mi.
NE of vent; Maplewood Testirng Services LATITUDINAL DEG. MIN.
SEC 39 -
27 -
14 39 39 39 39 39 39 39 39 39 39 26 30 29 30 30 33 34 36 44 37 51 00 33 44 58 55 18 31 16 55 LONGITUDINAL SAMPLE TYPE "DEG. MIN.
SEC 75 42 32 75 75 75 75 75 75 75 75
-75 75 43 38 37 40 36 34 35 29 32 30 07 59 55 52 36 25 25 59 31 44 39 -
38 19 75 -
26 10 39 -
35 56 39 -
18 -
47 39 18 13 39 31 18 39' -
31 21 39 39 39 40 40 51 41 43 32 36 02 25 75 75 75 75 16 -
47 33 50 36 -
05 46 -
30 IDM IDM IDM FPV, FPL MLK,VGT,SOL.
IDM ESS,SWA IDM FPV, FPL IDM FPV FPV IDM,MLK,VGT,SOL FPV IDM AIO,APT, IDM 75 -
44 - 57 FPV 75 75 75 74 35 11 12 15 06 23 09 IDM IDM FPL, FPV IDM NOTE:
All station locations are referenced to the midpoint of location are:
Latitude N 390 -
27'  
- 45.3" and Longitude W 750 the two Salem Units' 32' 09.7".
Vents.
The coordinates of this All Game (GAM),
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 Station's ODCM.
Vegetable samples are not always collected in consecutive years from the same farmer since they rotate the type of crop they grow.
L


MAP B-1 ON-SITE SAMPLING     LOCATIONS 1
MAP B-1 ON-SITE SAMPLING LOCATIONS 1
5 9
5 9
45 pIn&#xf7;l&#xfd;++ nn
45 D~~~nttav4~jq an.
          - 1 Ic
R0kA ff) 1
              ,&#xfd; 1")0(')
.flfS ()
                      *"  D~~~nttav4~jq 1    .flfS R0kA () R an.
nom R
rina nom ff)
rina pIn&#xf7;l&#xfd;++
nn 1  
, Ic &#xfd; 1")0(')  


MAP B-2 SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM OFF-SITE SAMPLING   LOCATION 15   NW             16         NN&#xfd;           I AML1   N           2 NNE           A PE 8R                                   VTW HU2NDR**D i
MAP B-2 SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM OFF-SITE SAMPLING LOCATION 15 NW 16 NN&#xfd; I
HdUNDRED 14G           E R ES                                       3F2 2702 HUNDRED                                                         Fl H E L w               to 2/.           br       E~46
AML1 N
2 NNE A
HdUNDRED PE 8R VTW HU2NDR**D i
14G E R ES 3F2 2702 HUNDRED Fl H E
L w
to 2/.
br E~46
(-00--
(-00--


APPENDIX C DATA TABLES 47
APPENDIX C DATA TABLES 47


APPENDIX C DATA TABLES Appendix C presents the analytical                               results of the 2001 Radio logical   Environmental Monitoring Program for                                     the period of January 1 to December 31, 2001.
APPENDIX C DATA TABLES Appendix C presents the analytical results of the 2001 Radio logical Environmental Monitoring Program for the period of January 1 to December 31, 2001.
TABLE OF CONTENTS TABLE TABLE DESCRIPTION                                                             PAGE NO.
TABLE OF CONTENTS TABLE NO.
ATMOSPHERIC ENVIRONMENT AIR PARTICULATES C-I   2001 Concentrations of Gamma Emitters in                               Quarterly Composites of Air Particulates ............................................                                           53 2001 Concentrations of Gross Beta Emitters in                               Air Particulates.               54 C-2 AIR IODINE in     Filtered Air .................           56 C-3  2001 Concentrations of Iodine-131 DIRECT RADIATION THERMOLUMINESCENT DOSIMETERS 2001 Direct Radiation Measurements                               - Quarterly TLD Results .....               58 C-4 TERRESTRIAL ENVIRONMENT MILK 2001 Concentrations of Iodine-131 and Gamma Emitters in                                         Milk... 59 C-5 WELL WATER C-6   2001 Concentrations of Gross Alpha and Gross Beta Emitters, and Tritium in Well Water ......................................                                           61 49
TABLE DESCRIPTION PAGE ATMOSPHERIC ENVIRONMENT AIR PARTICULATES C-I 2001 Concentrations of Gamma Emitters in Quarterly Composites of Air Particulates............................................
53 C-2 2001 Concentrations of Gross Beta Emitters in Air Particulates.
54 AIR IODINE C-3 2001 Concentrations of Iodine-131 in Filtered Air.................
56 DIRECT RADIATION THERMOLUMINESCENT DOSIMETERS C-4 2001 Direct Radiation Measurements  
- Quarterly TLD Results.....
58 TERRESTRIAL ENVIRONMENT MILK C-5 2001 Concentrations of Iodine-131 and Gamma Emitters in Milk...
59 WELL WATER C-6 2001 Concentrations of Gross Alpha and Gross Beta Emitters, and Tritium in Well Water......................................
61 49


IU -- III DATA TABLES                 (cont'd.)
IU III DATA TABLES (cont'd.)
TABLE NO                                   TABLE.DESCRIPTION                                                           PAGE TERRESTRIAL ENVIRONMENT                     (cont, d)
TABLE NO TABLE.DESCRIPTION PAGE TERRESTRIAL ENVIRONMENT (cont, d)
C-7   2001 Concentrations of Gamma Emitters in                           Well Water ...............             62 POTABLE WATER C-8   2001 Concentrations of Gross Alpha and Gross Beta Emitters, and Tritium in Raw and Treated Potable Waters ......................
C-7 2001 Concentrations of Gamma Emitters in Well Water...............
63 C-9   2001 Concentrations of Iodine 131 and Gamma Emitters in Raw and Treated Potable Water ..........................................
62 POTABLE WATER C-8 2001 Concentrations of Gross Alpha and Gross Beta Emitters, and Tritium in Raw and Treated Potable Waters......................
64 FOOD PRODUCTS C-10   2001 Concentrations of Gamma Emitters in                           Vegetables ...............             65 C-11   2001 Concentrations of Gamma Emitters in                           Game ......................             66 FODDER CROPS C-12   2001 Concentrations of Gamma Emitters in                           Fodder Crops .............             67 SOIL C-13   2001 Concentrations of Gamma Emitters in Soil                                     .................      68 AQUATIC ENVIRONMENT SURFACE WATER C-14   2001 Concentrations of Gross Beta Emitters in                             Surface Water ....               69 C-15   2001 Concentrations       of Gamma Emitters in                     Surface Water ............             70 C-16   2001 Concentrations of Tritiuri in                     Quarterly Composites of Surface Water.................       ......        ....          ...............................                  72 EDIBLE FISH C-17   2001 Concentrations of Strontium-89, Strontium-90                                   and Gamma Emitters in Edible Fish ........................................
63 C-9 2001 Concentrations of Iodine 131 and Gamma Emitters in Raw and Treated Potable Water..........................................
64 FOOD PRODUCTS C-10 2001 Concentrations of Gamma Emitters in Vegetables...............
65 C-11 2001 Concentrations of Gamma Emitters in Game......................
66 FODDER CROPS C-12 2001 Concentrations of Gamma Emitters in Fodder Crops.............
67 SOIL C-13 2001 Concentrations of Gamma Emitters in Soil 68 AQUATIC ENVIRONMENT SURFACE WATER C-14 2001 Concentrations of Gross Beta Emitters in Surface Water....
69 C-15 2001 Concentrations of Gamma Emitters in Surface Water............
70 C-16 2001 Concentrations of Tritiuri in Quarterly Composites of Surface Water.................
72 EDIBLE FISH C-17 2001 Concentrations of Strontium-89, Strontium-90 and Gamma Emitters in Edible Fish........................................
73 50
73 50


DATA TABLES                   (cont'd'.d)
DATA TABLES (cont'd'.d)
TABLE NO                                         TABLE DESCRIPTION                                                   PAGE BLUE CRABS C-18 2001 Concentrations of Gamma Emitters in                                       Crabs ..................... 74 SEDIMENT C-19 2001 Concentrations of Gamma Emitters in                                       Sediment .................. 75 SPECIAL TABLES LLDs C-20 2001 PSE&G Maplewood Testing Services'                                     LLDs for Gamma Spectrometry ...................................................                                             76 51
TABLE NO TABLE DESCRIPTION PAGE BLUE CRABS C-18 2001 Concentrations of Gamma Emitters in Crabs.....................
74 SEDIMENT C-19 2001 Concentrations of Gamma Emitters in Sediment..................
75 SPECIAL TABLES LLDs C-20 2001 PSE&G Maplewood Testing Services' LLDs for Gamma Spectrometry...................................................
76 51


Table C-1 2001 CONCENTRATIONS OF GAMMA EMITTERS*
Table C-1 2001 CONCENTRATIONS OF GAMMA EMITTERS*
IN QUARTERLY COMPOSITES OF AIR PARTICULATES Results in Units of 10-3 pCi/rn 3 +/- 2 sigma STATION                 Sampling Period                 <--- Gamma Emitters --- >
IN QUARTERLY COMPOSITES OF AIR PARTICULATES Results in Units of 10-3 pCi/rn 3 +/- 2 sigma STATION Sampling Period  
ID               Start             Stop               Be-7             K-40 SA-APT-5S 1             12/26/2000    to    3/27/2001            38+/-4              11 _4 SA-APT-1 F1             12/26/2000    to    3/27/2001            36+/-3              10+/-3 SA-APT-2F6             12/26/2000    to    3/27/2001            51_+/-4            12+/-3 SA-APT-5D 1             12/26/2000    to    3/27/2001            37+/-3              10+/-2 SA-APT-1 6E1           12/27/2000    to    3/28/2001            37+/-4              14+/-5 SA-APT- 1 4G 1 (C)     12/27/2000    to    3/28/2001            33+/-3              11+/-2 SA-APT-5S 1             3/27/2001    to    6/25/2001            64+/-6                <4 SA-APT-1 F1             3/27/2001    to    6/25/2001            69_+/-5              <4 SA-APT-2F6               3/27/2001    to    6/25/2001            69_+/-4              <4 SA-APT-5D 1             3/27/2001    to    6/25/2001            61 +/-4            12+/-3 SA-APT-16E1             3/28/2001    to    6/26/2001            68+/-4                <4 SA-APT-14G1 (C)         3/28/2001    to    6/26/2001            66-+/-4              <4 SA-APT-5S 1             6/25/2001    to    9/24/2001            70+/-5              10+/-2 SA-APT-1 F1              6/25/2001    to    9/24/2001            67_+/-4              9_+/-2 SA-APT-2F6              6/25/2001    to    9/24/2001            78_+/-5              <6 SA-APT-5D 1             6/25/2001    to    9/24/2001            60+/-4                <3 SA-APT-16E1              6/26/2001    to    9/25/2001            58+/-4              <4 SA-APT-14G1 (C)         6/26/2001    to    9/25/2001            58+/-6              <6 SA-APT-5S 1              9/24/2001    to    1/2/2002            48+/-4              12+/-3 SA-APT-1 F1              9/24/2001   to    1/2/2002            47+/-4              9_+/-2 SA-APT-2F6              9/24/2001   to    1/2/2002            49+/-4              11_+/-2 SA-APT-5D1              9/24/2001   to    1/2/2002            51 +/-4            7-+/-3 SA-APT-1 6E1            9/25/2001     to    1/3/2002            51-+/-4            12+/-3 SA-APT-14G1 (C)          9/25/2001     to    1/3/2002            53+/-4              9+/-3 AVERAGE                                                          55+/-_25            8_+/-7
<--- Gamma Emitters --- >
ID Start Stop Be-7 K-40 SA-APT-5S 1 SA-APT-1 F1 SA-APT-2F6 SA-APT-5D 1 SA-APT-1 6E1 SA-APT-1 4G 1 (C)
SA-APT-5S 1 SA-APT-1 F1 SA-APT-2F6 SA-APT-5D 1 SA-APT-16E1 SA-APT-14G1 (C)
SA-APT-5S 1 SA-APT-1 F1 SA-APT-2F6 SA-APT-5D 1 SA-APT-16E1 SA-APT-14G1 (C)
SA-APT-5S 1 SA-APT-1 F1 SA-APT-2F6 SA-APT-5D1 SA-APT-1 6E1 SA-APT-14G1 (C) 12/26/2000 12/26/2000 12/26/2000 12/26/2000 12/27/2000 12/27/2000 3/27/2001 3/27/2001 3/27/2001 3/27/2001 3/28/2001 3/28/2001 6/25/2001 6/25/2001 6/25/2001 6/25/2001 6/26/2001 6/26/2001 9/24/2001 9/24/2001 9/24/2001 9/24/2001 9/25/2001 9/25/2001 AVERAGE
* All other gamma emitters searched for were <LLD; typical LLDs are given in Table 20.
* All other gamma emitters searched for were <LLD; typical LLDs are given in Table 20.
(C) Control Station 53
(C) Control Station 53 to to to to to to to to to to to to to to to to to to to to to to to to 3/27/2001 3/27/2001 3/27/2001 3/27/2001 3/28/2001 3/28/2001 6/25/2001 6/25/2001 6/25/2001 6/25/2001 6/26/2001 6/26/2001 9/24/2001 9/24/2001 9/24/2001 9/24/2001 9/25/2001 9/25/2001 1/2/2002 1/2/2002 1/2/2002 1/2/2002 1/3/2002 1/3/2002 38+/-4 36+/-3 51_+/-4 37+/-3 37+/-4 33+/-3 64+/-6 69_+/-5 69_+/-4 61 +/-4 68+/-4 66-+/-4 70+/-5 67_+/-4 78_+/-5 60+/-4 58+/-4 58+/-6 48+/-4 47+/-4 49+/-4 51 +/-4 51-+/-4 53+/-4 55+/-_25 11 _4 10+/-3 12+/-3 10+/-2 14+/-5 11+/-2
<4
<4
<4 12+/-3
<4
<4 10+/-2 9_+/-2
<6
<3
<4
<6 12+/-3 9_+/-2 11_+/-2 7-+/-3 12+/-3 9+/-3 8_+/-7


TABLE C-2 2001 CONCENTRATIONS OF GROSS BETA EMITTERS IN AIR PARTICULATES Results in Units of 10.3 pCi/M 3 +/- 2 sigma
TABLE C-2 2001 CONCENTRATIONS OF GROSS BETA EMITTERS IN AIR PARTICULATES Results in Units of 10.3 pCi/M 3 +/- 2 sigma STATION ID..............................
                                      < -----------------                            STATION ID ..............................
Control MONTH SA-APT-14G1 SA-APT-16E1 SA-APT-1F1 SA-7APT-2F6 SA-APT-5D1 SA-APT-5S1 AVERAGE January February March April May June 23+/-2 18+/-3 17+/-2 19+/-2 34+/-3 17+/-2 21 +/-3 28+/-2 20+/-2 14+/-2 12+/-2 18+/-2 13+/-2 13+/-2 22+/-3 18+/-2 35+/-4 29+/-3 35+/-3 28+/-3 11+/-2 13+/-2 15 +/-2 24+/-3 25+/-2 39+/-3 24+/-2 22+/-3 21 +/-2 19+/-2 33+/-3 17+/-2 23+/-3 25+/-2 21 +/-2 18_+/-2 11+/-2 15+/-2 11+/-2 12+/-2 18+/-3 19+/-2 32+/-3 27+/-2 29+/-2 29+/-3 9+/-2 11+/-2 16+/-2 24+/-3 25+/-2 42+/- 3 21+/-2 17+/-2 17+/-2 18+/-2 32+/-3 15+/-2 16+/-2 25+/-2 20+/-2 19+/-2 15+/-2 16+/-2 1.7+/-2 11,+/-2 20+/-2 19+/-2 34+/-3 27+/-3 32+/-3 23+/-2 10+/-2 9+/-2 18+/-2 22+/-2 22+/-2 24+/- 2 21 +/-2 18+/-2 22+/-2 19+/-2 32+/-3 21+/-2 20+/-2 27+/-2 23+/-2 24+/-2 15+/-2 17+/-2 1.8+/-2 10+/-2 20+/-2 18+/-2 33+/-3 29+/-3 35+/-3 24+/- 2 11+/-2 8+/-2 15+/-2 23+/-2 21_+/-2 24+/-2 21+/-2 21 +/-3 20+/-2 15+/-2 30+/-3  
Control MONTH SA-APT-14G1       SA-APT-16E1             SA-APT-1F1           SA-7APT-2F6     SA-APT-5D1             SA-APT-5S1       AVERAGE January     23+/-2             24+/-2                    21+/-2                 21 +/-2           21+/-2                    21 +/-2             22+/-3 18+/-3              22+/-3                    17+/-2                   18+/-2           21 +/-3                  19_+/-3            19+/-4 17+/-2             21 +/-2                   17+/-2                  22+/-2             20+/-2                    16_+/-2            19+/-5 19+/-2              19+/-2                   18+/-2                   19+/-2             15+/-2                  18+/-2 34+/-3 18+/-3 33+/-3                   32+/-3                  32+/-3            30+/-3                   32+/-3              32+/-3 February    17+/-2             17+/-2                   15+/-2                 21+/-2             .15+/-2                   17+/-2             17+/-4 21 +/-3             23+/-3                   16+/-2                   20+/-2             13+/-2                    15+/-2             18+/-8 28+/-2             25+/-2                    25+/-2                   27+/-2            24+/-2                   28+/-2             26+/-33 20+/-2             21 +/-2                   20+/-2                  23+/-2             20+/-2                   18+/-2 L~n 20+/-3 March      14+/-2             18_+/-2                   19+/-2                   24+/-2             21 +/-3                  20+/-2 12+/-2             11+/-2                    15+/-2                  15+/-2            18+/-2                   16+/-2             14+/-5 18+/-2             15+/-2                   16+/-2                   17+/-2             17+/-2                   14+/-2             16+/-3 13+/-2             11+/-2                    1.7+/-2                 1.8+/-2           17+/-2                   18+/-2             16+/-6 April      13+/-2             12+/-2                   11,+/-2                 10+/-2           9+/-2                     11+/-2             11+/-3 22+/-3             18+/-3                   20+/-2                   20+/-2           19+/-2                     19+/-3            20+/-3 18+/-2             19+/-2                   19+/-2                   18+/-2            19+/-2                     15+/-2             18+/-3 35+/-4              32+/-3                    34+/-3                  33+/-3           29+/-3                    29+/-3              32+/-5 29+/-3              27+/-2                   27+/-3                  29+/-3           27'+/- 2                 27+/-3             27+/-2 May        35+/-3              29+/-2                   32+/-3                  35+/-3            32+/-3                    28+/-3              32+/-6 28+/-3             29+/-3                    23+/-2                 24+/- 2           26+/-2                   25+/-3              26 +/-4 11+/-2             9+/-2                     10+/-2                   11+/-2           8+/-2                     9+/-2 13+/-2 9+/-3 11+/-2                    9+/-2                  8+/-2              11+/-2                   9+/-2               10+/-3 June        15 +/-2             16+/-2                   18+/-2                 15+/-2            13+/-2                    16+/-2              15+/-3 24+/-3             24+/-3                    22+/-2                  23+/-2            21+/-2                    21+/-2              22+/-3 25+/-2              25+/-2                    22+/-2                  21_+/-2            21+/-2                    24+/-2             2,3:+/-t4 39+/-3              42+/- 3                   24+/- 2                24+/-2            20+/- 2                   20+/-2              28+/- 20
.15+/-2 13+/-2 24+/-2 20+/-2 21 +/-3 18+/-2 17+/-2 17+/-2 9+/-2 19+/-2 19+/-2 29+/-3 27'+/- 2 32+/-3 26+/-2 8+/-2 11+/-2 13+/-2 21+/-2 21+/-2 20+/- 2 21 +/-2 19_+/-3 16_+/-2 18+/-2 32+/-3 17+/-2 15+/-2 28+/-2 18+/-2 20+/-2 16+/-2 14+/-2 18+/-2 11+/-2 19+/-3 15+/-2 29+/-3 27+/-3 28+/-3 25+/-3 9+/-2 9+/-2 16+/-2 21+/-2 24+/-2 20+/-2 22+/-3 19+/-4 19+/-5 18+/-3 32+/-3 17+/-4 18+/-8 26+/-33 20+/-3 14+/-5 16+/-3 16+/-6 11+/-3 20+/-3 18+/-3 32+/-5 27+/-2 32+/-6 26 +/-4 9+/-3 10+/-3 15+/-3 22+/-3 2,3:+/-t4 28+/- 20 L~n


TABLE C-2 2001 CONCENTRATIONS OF GROSS BETA EMITTERS IN AIR PARTICULATES Results in Units of 10,3 pCi/m 3 +/- 2 sigma
TABLE C-2 2001 CONCENTRATIONS OF GROSS BETA EMITTERS IN AIR PARTICULATES Results in Units of 10,3 pCi/m 3 +/- 2 sigma STATION ID ------------------------------------
                                        < ----------------------------------------------- STATION ID ------------------------------------
Control MONTH SA-APT-14G1 SA-APT-16E1 SA-APT-1F1 SA-APT-2F6 SA-APT-5D1 SA-APT-5S1 AVERAGE September 27+/- 2 25 +/-+3 25+/-2 29+/-3 July 22_+/-2 17+/-2 19+/-2 23-+/-3 18+/-2 22+/-3 24_+/-2 26_+/-2 29+/-3 28+/-3 20+/--2 20+/-2 24+/-3 19+/-2 29 3
Control MONTH SA-APT-14G1       SA-APT-16E1         SA-APT-1F1               SA-APT-2F6     SA-APT-5D1           SA-APT-5S1         AVERAGE July      28+/-3               28+/-3                 22_+/-2                     26+/-2           28+/-2                 27_+/-3               26_+/-5 20+/--2             16+/-2                 17+/-2                      23+/-2            16+/- 2               20+/-2               19+/-5 20+/-2               20+/-2                 19+/-2                     22+/- 2            15-+/-2               19_+/-2               19+/-4 24+/-3               23+/-3                 23-+/-3                    22_+/-3           17-+/-2               20+/-3               21+/-5 19+/-2               17+/-2                 18+/-2                      19+/-2             15+/-2                 13+/-2               17+/-5 August    29 3               27+/-3                22+/-3                     26++/-3           24+/-3                 20+/-3                24+/--7 23+/-2               29+/-3                24_+/-2                     23+/-2           19_+/-2                 26+/-3               24_+/-
23+/-2 33+/-2 28+/-3 28+/-3 16+/-2 20+/-2 23+/-3 17+/-2 27+/-3 29+/-3 26+/-2 27+/-3 25+/-2 23+/-3 23_+/-2 25+/-2 13+/-2 38+/-3 18+/-2 24+/- 2 23+/-2 28+/-3 31 +/-2 39+/-3 19+/-2 28+/-3 34+/--3 28-+/-2 25_+/-2 33+/-2 23 +/-15 26+/-2 23+/-2 22+/- 2 22_+/-3 19+/-2 26++/-3 23+/-2 29+/-2 29-+/-3 28+/-2 22+/--3 26_+/-2 28-+/-3 14+/-2 41 +/-3 22_+/-2 27-+/-3 24+/-2 26+/-3 31+/-2 39_+/-3 20+/- 2 338.+/-3 36-+/-3 26+/- 2 26+/-2 33+/-3 24+/-14 27_+/-2 24+/-3 23+/-2 32+/-3 16_+/-2 41+/-3 20+/-2 25_+/-3 21 +/-2 29+/-3 38_+/-3 40+/- 3 19_+/-2 32+/-3 34+/-3 26+/-2 28+/-2 37 +/- 3 August 23+/-15 U,n Ln 22+/-15 22+/-14 GRAND AVERAGE October November December AVERAGE 28+/-2 16+/- 2 15-+/-2 17-+/-2 15+/-2 24+/-3 19_+/-2 21 +/-2 26-+/-3 26-+/-2 18+/-+2 22+/-_2 32_+/-3 15+/-2 43-+/-3 18+/-2 28+/-3 24+/-2 29 +/-3 30+/-2 37 +/-3 20+/-2 34+/-3 35-+/-3 28+/-_2 28+/-2 35 +/-3 14+/-2 44+/-3 21 +/-_2 26+/-3 28+/-2 29+/-3 33+/-2 43+/-3 21 +/-2 34+/-3 41 +/-3 31+/-3  
33+/-2              26+/-2                 26_+/-2                     29+/-2            21 +/-2                 22_+/-2              26+/-9 28+/-3               27+/-3                29+/-3                     29-+/-3          26-+/-3                 28+/-3                28+/-3 September  27+/- 2             25+/-2                27_+/-2                     28+/-2            26-+/-2                21 +/-2               26+/--5 U,n Ln            25 +/-+3             23+/-3                24+/-3                      22+/--3           18+/-+2               25+/-3                 23+/-5 25+/-2              23_+/-2               23+/-2                      26_+/-2           22+/-_2                20+/-2                23+/--5 29+/-3               25+/-2                 32+/-3                     28-+/-3          32_+/-3                30+/-3                 29+/-6 October    14+/-2              13+/-2                16_+/-2                     14+/-2           15+/-2                 16++/-2               15+/-2 44+/-3               38+/-3                41+/-3                    41 +/-3           43-+/-3                44+/- 3                42+/-5 21 +/-_2             18+/-2                20+/-2                     22_+/-2          18+/-2                 18-+/-2              20+/-4 26+/-3               24+/- 2               25_+/-3                     27-+/-3          28+/-3                 24+/-3                 26+/-3 28+/-2               23+/-2                21 +/-2                     24+/-2            24+/-2                23-+/-2               24+/-5 November  29+/-3              28+/-3                 29+/-3                      26+/-3           29 +/-3               29_+/-3               28+/-2 33+/-2             31 +/-2                38_+/-3                     31+/-2           30+/-2                 28_+/-2                32+/-7 43+/-3             39+/-3                 40+/- 3                    39_+/-3           37 +/-3                39-+/-3               40+/-4 21 +/-2              19+/-2                 19_+/-2                    20+/- 2           20+/-2                15+/-2                 19+/-4 December  34+/-3             28+/-3                  32+/-3                    338.+/-3           34+/-3                30+/-_3               32+/-4 41 +/-3             34+/--3                34+/-3                    36-+/-3           35-+/-3                31 +/-3                35+/-7 31+/-3              28-+/-2                26+/-2                    26+/- 2            28+/-_2                29+/-2                28+/-4
.26+/-2 36+/-2 25+/-16 27_+/-3 20+/-2 19_+/-2 20+/-3 13+/-2 20+/-3 26+/-3 22_+/-2 28+/-3 21 +/-2 25+/-3 20+/-2 30+/-3 16++/-2 44+/- 3 18-+/-2 24+/-3 23-+/-2 29_+/-3 28_+/-2 39-+/-3 15+/-2 30+/-_3 31 +/-3 29+/-2 29_+/-2 33+/-3 26_+/-5 19+/-5 19+/-4 21+/-5 17+/-5 24+/--7 24_+/-
              .26+/-2              25_+/-2                28+/-2                    26+/-2            28+/-2                29_+/-2                27+/-2 36+/-2              33+/-2                  37 +/- 3                   33+/-3            35 +/-3                33+/-3                34+/-4 AVERAGE    25+/-16            23 +/-15                23+/-15                    24+/-14            22+/-15                22+/-14 GRAND AVERAGE                            23+/- 15
26+/-9 28+/-3 26+/--5 23+/-5 23+/--5 29+/-6 15+/-2 42+/-5 20+/-4 26+/-3 24+/-5 28+/-2 32+/-7 40+/-4 19+/-4 32+/-4 35+/-7 28+/-4 27+/-2 34+/-4 23+/- 15


TABLE C-3 2001 CONCENTRATIONS OF IODINE-131* IN FILTERED AIR 3    3 Results in Units of 10. pCi/m
TABLE C-3 2001 CONCENTRATIONS OF IODINE-131* IN FILTERED AIR Results in Units of 10.3 pCi/m 3 STATION ID ----------------------------------------------
                          <-----------------------------------------------    STATION ID ----------------------------------------------     >
Control MONTH SA-AIO-14G1 SA-AIO-16E1 SA-AIO-1F1 SA-AIO-2F6 SA-AIO-5D1 SA-AIO-5S1 January February March April May June
Control MONTH   SA-AIO-14G1       SA-AIO-16E1                 SA-AIO-1F1           SA-AIO-2F6             SA-AIO-5D1                   SA-AIO-5S1 January   <2.2             <3.5                          <6.7               <2                     <5.1                         <3.3
<2.2  
              <2.3             <5.3                          <2.2               <2.4                    <2.6                          <4.9
<2.3  
              <1.7             <1.7                         <3.1                <6.5                    <2                           <2.5
<1.7  
              <2.3            <3.4                          <1.3                <1.2                   <1.5                          <1.7
<2.3
              <4.9              <4.4                         <2.5                <4.4                    <2.3                         <1.9 February < 1.4             <1.8                          <1.8               <1.9                   <2.1                          <1.6
<4.9
              <3.4              <2.9                          <2.4                <2.8                    <2                            <2.2
< 1.4
              <2.3              <2.7                          <3.8                <*1.3                  <3.2                          <5.7
<3.4
              <2.5              <1.5                          <2.5               <2.2                    <1.9                          <2.5 LnJ March    <2.2             <2                          <1.6                <4.6                    <2.6                          <4 OPN
<2.3  
              <2.9              <3.5                        <2                  <3                      <2.2                          <2.1
<2.5  
              <2.4              <2.7                        <4.4                 <3.2                    <4.8                         <2.6
<2.2  
              <1.7              <1.7                        <1.8                 <3                      <*4*.. 3                     <4.3 April    <5.7              <3.5                         <2.6                <2.8                    <4.8                          <2.1
<2.9
              <2.9              <6.7                        <3.5                <2.9                   <2.8                         <5.3
<2.4  
              <3.3              <2.7                        <3.6                 <2
<1.7  
                                                                                                          < 1.7                        <3
<5.7  
              <6.1              <2.6                        <2.8                <3.1                   <5
<2.9
                                                                                                                                        <2.1
<3.3
              <2.2             <3.7                         <2.3                <3.7                    <3.1                         <4 May      <3.7             <4.6                        <4.1                 <2                     <4                            <4.2
<6.1
              <5.5             <5.7                        <2.8                <2.5                    <2.7                          <1.6
<2.2  
              <2               <1.6                         <1.5                <2.7                    <3.6                          <1.6
<3.7
              <1.7             <4                          <2                  <2                      <2.7                         <1.9 June      <2.8              <4.3                        <2.1                <2.1                  <3                             <5.1
<5.5
              <3.5              <2.5                         <1.4                <1.9                   <1.8                          <3.2
<2  
              <2.4             <2.9                          <1.7                <3..5                  <2.4                           <2.6
<1.7
              <"1.7            <3.2                          <3.1                 < 1.7&#xfd;                <2.7                          <3.2
<2.8
<3.5
<2.4  
<"1.7
<3.5
<5.3  
<1.7
<3.4  
<4.4
<1.8  
<2.9  
<2.7
<1.5
<2
<3.5
<2.7
<1.7
<3.5
<6.7
<2.7
<2.6
<3.7
<4.6
<5.7  
<1.6
<4
<4.3
<2.5  
<2.9
<3.2
<6.7
<2.2  
<3.1
<1.3
<2.5
<1.8
<2.4
<3.8
<2.5
<1.6
<2  
<4.4  
<1.8  
<2.6  
<3.5
<3.6
<2.8  
<2.3  
<4.1
<2.8
<1.5  
<2  
<2.1
<1.4  
<1.7
<3.1
<2
<2.4
<6.5
<1.2
<4.4
<1.9  
<2.8  
<*1.3  
<2.2  
<4.6  
<3
<3.2
<3  
<2.8
<2.9
< 2  
<3.1  
<3.7
<2  
<2.5
<2.7  
<2
<2.1
<1.9
<3..5
< 1.7&#xfd;
<5.1  
<2.6
<2  
<1.5  
<2.3
<2.1
<2  
<3.2  
<1.9
<2.6  
<2.2
<4.8
<*4*.. 3  
<4.8
<2.8
< 1.7  
< 5
<3.1
<4
<2.7  
<3.6
<2.7
<3
<1.8
<2.4
<2.7
<3.3
<4.9
<2.5  
<1.7
<1.9  
<1.6
<2.2  
<5.7
<2.5
<4  
<2.1
<2.6
<4.3  
<2.1
<5.3
<3
<2.1
<4  
<4.2  
<1.6  
<1.6
<1.9
<5.1  
<3.2
<2.6
<3.2 LnJ OPN


TABLE C-3 2001 CONCENTRATIONS OF IODINE-131* IN FILTERED AIR 3        3 De,.Ia + -"-nI e nf In. n ;*rlm
TABLE C-3 2001 CONCENTRATIONS OF IODINE-131* IN De,.Ia +  
                                <  -      S    T   A       T       STATION ID ----------------.. ----------------------------- >
-"-nI e nf In.
IO---------------------------------
3 n  
Control MONTH             SA-AIO-14G1       SA-AIO-16E1     SA-AIO-1F1         SA-AIO-2F6           SA-AIO-5D1                 SA-AIO-5S1 July               <2.4             <2               <1.9               <5.9                <3.5                        <1.5
;*rlm3 FILTERED AIR S
                    <1.7             <4.5            <1.3                <2                  <1.8                         < 2.6
T A
                    <2.4              <2.6            <5.9               <3.7                 <4.2                         <2.5
T IO---------------------------------
                    <3.7              < 1.9           <4                  <5.8                <3.4                        <1.4
STATION ID ----------------.. ----------------------------- >
                    <1.8              <2.6            <1.9                <1.4                 <1.5                        <3.7 August              <.1.6            <2.1             <3.3                <3.6                 <1.1                       <2.3
Control MONTH SA-AIO-14G1 SA-AIO-16E1 SA-AIO-1F1 SA-AIO-2F6 SA-AIO-5D1 SA-AIO-5S1 July August September October November
                    <2.3              <2.3            <3.4                <1.7                 <3                         <2
<2.4  
                                      <3.1             <2.8                <3$.9                <2.5                        <1.9
<1.7
                    <4.9
<2.4
                    <2.4              <2.2            <2.6                <2.2                  <2.8                        <3.1 September          <2,.3            <2.1            <5.4               <1.2                  <3.4                        <3.5
<3.7
                    <4.1              <1.7            <3.6                <2.3                  <3.2                        <2.6
<1.8
                    <1.3              <3              <3.5               <1.2                  <4.2                        <2.7
<.1.6
                    <1.7              <4.2            <3.9                <3                   <4.9                       <1.7 October            <4.9             <3.4            <1.8               <1..7                <1.8                        <3.6
<2.3
                    <1.4              <3.1            <2.4                <1                   <3                         <1.5
<4.9  
                    <1.8                              <2.1               < 1.4                 <1.3                        <1.8
<2.4
                                      <2.8            <1.5                <6.4                  <4.7                        <4.
<2,.3  
                    <3.2
<4.1
                    <2                 <1.6            <2.4                <2.8                 <1                          <1.6 November            <2.3              <3.6            <9.5               <2.5                  <2.1                        <1.2
<1.3
                    <2.9               <1.1            <2.7                <1.3                 <2.1                        <4.1
<1.7  
                    <1.7              <2.5            <6.6                <4.5                <3.6                       <3.3
<4.9
                    <4                 <2.2            <2.6                <2.9                <3.1                        <1.7
<1.4
                                                        <3.3"              <3.9                <4.5                        <4.3 December              2.9             < 3.3
<1.8  
                    <3.7              <3              <3.6               <2.2                <5.1                        <1.4
<3.2  
                    <1.7               <3.1            <1.9                <2.3                <2.1                        <2.4
<2  
                    <1.6               <2.1            "< 2                                     <2                          <1.8
<2.3
                                                        <3.7                <1.3                <1.7                        <1.1
<2.9  
                    <2.3              <1.5
<1.7  
* 1-131 results are corrected for decay to sample stop date.
<4
<2  
<4.5  
<2.6
< 1.9  
<2.6
<2.1
<2.3
<3.1  
<2.2
<2.1
<1.7
<3
<4.2
<3.4
<3.1  
<2.8
<1.6
<3.6  
<1.1  
<2.5
<2.2 December 2.9
< 3.3
<3.7  
<3  
<1.7
<3.1  
<1.6
<2.1
<2.3
<1.5
* 1-131 results are corrected for decay to sample
<1.9  
<1.3
<5.9
<4
<1.9
<3.3
<3.4
<2.8
<2.6
<5.4  
<3.6
<3.5  
<3.9
<1.8
<2.4
<2.1
<1.5  
<2.4
<9.5
<2.7  
<6.6
<2.6
< 3.3"
<3.6
<1.9  
"< 2
<3.7 stop date.
<5.9  
<2
<3.7
<5.8  
<1.4
<3.6  
<1.7
<3$.9
<2.2
<1.2
<2.3  
<1.2
<3
<1..7
<1  
< 1.4  
<6.4
<2.8  
<2.5
<1.3
<4.5
<2.9
<3.9
<2.2  
<2.3
<1.3
<3.5
<1.8  
<4.2
<3.4
<1.5
<1.1
<3  
<2.5  
<2.8
<3.4
<3.2  
<4.2  
<4.9  
<1.8
<3
<1.3  
<4.7
<1  
<2.1
<2.1
<3.6  
<3.1
<4.5
<5.1
<2.1
<2  
<1.7
<1.5
< 2.6
<2.5
<1.4  
<3.7
<2.3  
<2  
<1.9  
<3.1
<3.5
<2.6  
<2.7
<1.7  
<3.6
<1.5
<1.8
<4.  
<1.6  
<1.2  
<4.1  
<3.3
<1.7
<4.3
<1.4
<2.4
<1.8
<1.1


ti -t I TA.BLE C-4 2001 DIRECT RADIATION MEASUREMENTS               - QUARTERLY TLD RESULTS Results in mradfstandard month* +       2 sigma
ti  
                              "'JAN                APR              JUL              Oct        Q..-tR STATION                 to                  to                                to    ELEMENTS ID               MAR                  JUN            SEP              DEC        AVG SA-iDM-2S2                 -5.7,+/-0.5          5.7 +/-0.5        6.1 +/-0.5          4.8+/-5 SA-IDM-5S1                3.5 +/-0.3            3.8 +/-0.4        3.8 +/-0.3          3.6 +/-0.3    3.7 +/-0.3 SA-IDM-6S2                4.9+/-0.3            5.2 +/-0.5        5.3 +/-0.4          4.8+/-0.4    5.0 +/-0.5 SA-lDM-7S1                5.4+/-0.3            5.6 +/-0.4        5.3 +/-0.6          5.9+/- 1.4    5.6 +/-0.6 SA-IDM-1 0S1              4.0 +/-0.4            4.3 +/-0.5        3,.9+/-0.3          4.0 +/-0.3    4.0 +/-0.4 SA-IDM1 1Si                3.6 +/-0.5            4.1 +/-0.5        3.4 +/-0.4          3.6 +/-0.4    3.7 +/-0.6 SA-IDM-4D2                4.1 +/-0.4            4.4+/-0.4        4.3 +/-0.3          4.3 +/-0.4    4.3 +/-0.3 SA-IDM-5D 1               3.7 +/-0.5            4.1 +/-0.4        4.0+/-0.7            3.9 +/-0.3  3.9 +/-0.3 SA-IDM-1OD1                4.3 +/-0.4            4.6 +/-0.4        4.9 +/-0.4          4.5 +/-0.4    4.6+/-0.6 SA-IDM-14D13              3.8 +/-0.3            4.1 +/-0.4        4.2 +/-0.5          4.1 +/-0.4    4.0+/-0.4 SA-IDM-1 5DI              4.5 +/-0.4            4.7 +/-0.5        4.7.+/-0D.4         4.4+/-0.4    4.6 +/-0.3 SA-lDM-2E1                4.1 +/-0.4            4.4+/-0.4        4.3 +/-0.3         4.2 +/-0.4    4.3 +/-0.3 SA-IDM-3E1                3.4 +/-0.4           3.8 +/-0.4       3.7 +/-0.6          .3.5 +/-0.4   3.6+/-0.4 SA.IDM-9E 1                4.0 +/-0.3            4.3 +/-0.3       4.6 +/-0.3          4.4+/-0.4    4.3 +/-0.4 SA-IOM-11 1E2              5.8 +/-4. 1          4.7 +/-0.5        4.7+/-0.4          4.5 +/-0.6    4.9 +/-1.1 SA-lDM- 12E1              4.5 +/-0.5           4.6 +/-0.5        4.9,+/-0.3         4.6+/-0.4     4.7 +/-0.4 SA-lDM-13E1.               3.7 +/-0.7            3.9 +/-0.3       &#xfd;3.8 +/-:0.4       3.6:t+/-0.4   3.8 +/-0.2 SA-IDM-1 6E1              4.2 +/-0.4           4.4+/-0.4        4.4+/-0.4          4.2 +/-0.5   4.3 +/-0.2 SA-IDM.1 Fl                4.0 +/-0.4            4.3 +/-0.3       4.31+/-0.4          4.3 +/-0.4   4.2 +/-0.3 SA-IDM-2F2                3.5 +/-0.3          3.7 +/-0.4         3.6 +/-0.3         3.6 +/-0.3   3.6+/-0.2 SA-IDM-2F5                4.1 +/-0.3          4.4 +/-0.3        4.4+/-0.4          4.1 +/-0.4   4.2 +/-0.*3 SA-lDM-2F6                  3.7 +/-0.3          4.1 +/-0.3        3.9+/-0.5           3.9 +/-0.5    3.9 +/-0.4 SA-IDM-3F2                  3.5 +/-0.3          3.7 +/-0.4         3.7 +/- 0.5         3.6 +/-0.3    3.6 +/-0.2 SA-IDM-3F3                3.5 +/-0.4           3.8 +/-0.5         3.6 +/-0.4          3.5 +/-0.3    3.6 +/-0.3 SA-IDM-4F2                3.4 +/-0.4           3.8 +/-0.4        3.7 +/-0.4         .3.5+/-0.3     3.6 +/-0.3 SA-IDM-5F1                3.6+/-0.4             4.0+/-0.4         4.0+/-0.3          3.7 +/-0.5    3.8 +/-0.4 SA-IDM-6F1                3.0+/-0.3             3.4+/-0.4         3.2 +/-0.4         3.2 +/-0.3   3.2 +/-0.4.
-t I TA.BLE C-4 2001 DIRECT RADIATION MEASUREMENTS - QUARTERLY TLD RESULTS Results in mradfstandard month* +
SA-IDM-7F2.                2.6+/-0.3            3.0 +/-0.4        2.9 +/-0.2          2.8 +/-0.2    2.8 +/- 0.3 SA-IDM-10F2                4.3 +/-0.9            4.6 +/-0.3         4.6 +/-0.3          4.3 +/-0.4    4.5 +/-0.3 SA-IDM-1 1Fl              4.5 +/-0.3            .4.9 +/-0.3       4.8 +/-0.4         4.5 +/-0.3    4.7 +/-0.5 SA-IDM-1 2FI              4.1 +/-0.4            4.4+/-0.4          4.3t+/-0.4          4.2 +/-0.3   4.2 +/-0.2 SA-IDM-1 3F2                                  4.4+/-0.4        4.2 +/-0.6          4.0 +/-0.3    4.2 +/-0.3 SA-IDM-1 3F3              3.9 +/-0.3            4.2 +/-0.3        4.4 +/-0.3          4.2+/-0.5    4.2 +/-0.4 SA-IDM-1 3F4              4.0 +/-0.5            4.2 +/-0.3       4.3 +/-0.4           4.2 +/-0.4   4.2 +/-0.2 SA-IDM-14F2                4.4+/-0.4             4.8 +/-0.4        4.8'+/-0.4          4.6+/-0.4     4.7 +/-0.4 SA-IOM-1 SF3              4.5 +/-0.5            5.0 +/-0.5        5.1 +/-0.6          4.9+/-0.4     4.9 +/-0.5 SA-IDM- 16F2              3.6 +/-0.3            3.'9 +/-0.4      4.2 +/-0.3          3.9+/-0O.4     3.9 +/-0.5 SA-IDM-1G3 (C)            5.0 +/-0.5            5.0 +/-0.4       5.0+/-0.4          4.9 +/-0.3    5.0 +/-0.2 SA-IDM-3G1 (C)            4.3 +/-0.5           4.6 +/-0.4       4.6 +/-0.3         4.5 +/-0.3   4.5 +/-0.3 SA-IOM-1OGi (C)            4.2 +/-0.5           4.5 +/-0.4        4.5 +/-0.5
2 sigma STATION ID SA-iDM-2S2 SA-IDM-5S1 SA-IDM-6S2 SA-lDM-7S1 SA-IDM-1 0S1 SA-IDM1 1 Si SA-IDM-4D2 SA-IDM-5D 1 SA-IDM-1OD1 SA-IDM-14D13 SA-IDM-1 5DI SA-lDM-2E1 SA-IDM-3E1 SA.IDM-9E 1 SA-IOM-11 1E2 SA-lDM-12E1 SA-lDM-13E1.
* 4.3+/-0.3     4.4 +/-0.3 SA-IDM-1 6G1 (C)          4.5 +/-0.3           4.9 +/-0.4       5.3 +/-0.7          5.1.+/-0.6    5.0 +/-0.7 SA-IDM-3H1 (C)            3.4 +/-0.4           3.7 +/-0.4       3.6 +/-0.4
SA-IDM-1 6E1 SA-IDM.1 Fl SA-IDM-2F2 SA-IDM-2F5 SA-lDM-2F6 SA-IDM-3F2 SA-IDM-3F3 SA-IDM-4F2 SA-IDM-5F1 SA-IDM-6F1 SA-IDM-7F2.
* 3.5 +/-0.4   3.5 +/-0.3 SA-IDM-1 Si                4.2 +/-0.3           4.8 +/-0.5        4.8+/-0.5           4.4 +/-0.3   4.5 +/-0.6 SA-1DM-3S1                3.4+/-0.4             3.6 +/-0.4        3.5 +/-0.4          3.4 +/-0.3   3.5 +/-0.2 SA-IDM-2S4                3.6 +/-0.4            3.9 +/-0.4        3.9 +/-0.4         3.5 +/-0.4   3.7 +/-0.4.
SA-IDM-10F2 SA-IDM-1 1 Fl SA-IDM-1 2FI SA-IDM-1 3F2 SA-IDM-1 3F3 SA-IDM-1 3F4 SA-IDM-14F2 SA-IOM-1 SF3 SA-IDM-16F2 SA-IDM-1G3 (C)
SA-1DM-4S 1                3.7 +/-0.3           4.0 +/-0.3       3.9 +/-0.3          4.0 +/-0.4   3.9 +/-0.3 SA-IDM-1 5S1              3.3 +/-0.3            3.86+/-0.4       3.8+/-t0.3         3.5 +/-0.4   3.6 +/-0.5 SA-IDM-1 6S1              4.2 +/-0.6           4.7 +/-0.4       4.6+/-10.5          4.2 +/-0.4   4.4 +/-0.5 SA-IDM-1 4G1 (C)          4.4+/-0.4             4.6 +/-0.3        4.6 +/-0.5          4.5 +/-0.4   4.5 +/-0.2 AVERAGE                    4+/- 1.2            4.3+/- 1. 1      4.3 +/-1.2          4.1 +/-1.1 GRAND AVG            4.2 +/-1.2 The standard month = 30.4 days.
SA-IDM-3G1 (C)
  'Quarterly    Element TLD results by DESEL.
SA-IOM-1OGi (C)
(C) Control Station 58
SA-IDM-1 6G1 (C)
SA-IDM-3H1 (C)
SA-IDM-1 Si SA-1DM-3S1 SA-IDM-2S4 SA-1DM-4S 1 SA-IDM-1 5S1 SA-IDM-1 6S1 SA-IDM-1 4G1 (C)
AVERAGE The standard month = 30.4 days.  
'Quarterly Element TLD results by DESEL.
(C) Control Station
"'JAN to MAR
-5.7,+/-0.5 3.5 +/-0.3 4.9+/-0.3 5.4+/-0.3 4.0 +/-0.4 3.6 +/-0.5 4.1 +/-0.4 3.7 +/-0.5 4.3 +/-0.4 3.8 +/-0.3 4.5 +/-0.4 4.1 +/-0.4 3.4 +/-0.4 4.0 +/-0.3 5.8 +/-4. 1 4.5 +/-0.5 3.7 +/-0.7 4.2 +/-0.4 4.0 +/-0.4 3.5 +/-0.3 4.1 +/-0.3 3.7 +/-0.3 3.5 +/-0.3 3.5 +/-0.4 3.4 +/-0.4 3.6+/-0.4 3.0+/-0.3 2.6+/-0.3 4.3 +/-0.9 4.5 +/-0.3 4.1 +/-0.4 3.9 +/-0.3 4.0 +/-0.5 4.4+/-0.4 4.5 +/-0.5 3.6 +/-0.3 5.0 +/-0.5 4.3 +/-0.5 4.2 +/-0.5 4.5 +/-0.3 3.4 +/-0.4 4.2 +/-0.3 3.4+/-0.4 3.6 +/-0.4 3.7 +/-0.3 3.3 +/-0.3 4.2 +/-0.6 4.4+/-0.4 4+/- 1.2 GRAND AVG APR to JUN 5.7 +/-0.5 3.8 +/-0.4 5.2 +/-0.5 5.6 +/-0.4 4.3 +/-0.5 4.1 +/-0.5 4.4+/-0.4 4.1 +/-0.4 4.6 +/-0.4 4.1 +/-0.4 4.7 +/-0.5 4.4+/-0.4 3.8 +/-0.4 4.3 +/-0.3 4.7 +/-0.5 4.6 +/-0.5 3.9 +/-0.3 4.4+/-0.4 4.3 +/-0.3 3.7 +/-0.4 4.4 +/-0.3 4.1 +/-0.3 3.7 +/-0.4 3.8 +/-0.5 3.8 +/-0.4 4.0+/-0.4 3.4+/-0.4 3.0 +/-0.4 4.6 +/-0.3  
.4.9 +/-0.3 4.4+/-0.4 4.4+/-0.4 4.2 +/-0.3 4.2 +/-0.3 4.8 +/-0.4 5.0 +/-0.5 3.' 9 +/-0.4 5.0 +/-0.4 4.6 +/-0.4 4.5 +/-0.4 4.9 +/-0.4 3.7 +/-0.4 4.8 +/-0.5 3.6 +/-0.4 3.9 +/-0.4 4.0 +/-0.3 3.86+/-0.4 4.7 +/-0.4 4.6 +/-0.3 4.3+/- 1. 1 4.2 +/-1.2 58 JUL SEP 6.1 +/-0.5 3.8 +/-0.3 5.3 +/-0.4 5.3 +/-0.6 3,.9+/-0.3 3.4 +/-0.4 4.3 +/-0.3 4.0+/-0.7 4.9 +/-0.4 4.2 +/-0.5 4.7.+/-0D.4 4.3 +/-0.3 3.7 +/-0.6 4.6 +/-0.3 4.7+/-0.4 4.9,+/-0.3  
&#xfd;3.8 +/-:0.4 4.4+/-0.4 4.31+/-0.4 3.6 +/-0.3 4.4+/-0.4 3.9+/-0.5 3.7 +/- 0.5 3.6 +/-0.4 3.7 +/-0.4 4.0+/-0.3 3.2 +/-0.4 2.9 +/-0.2 4.6 +/-0.3 4.8 +/-0.4 4.3t
+/-0.4 4.2 +/-0.6 4.4 +/-0.3 4.3 +/-0.4 4.8'+/-0.4 5.1 +/-0.6 4.2 +/-0.3 5.0+/-0.4 4.6 +/-0.3 4.5 +/-0.5 5.3 +/-0.7 3.6 +/-0.4 4.8+/-0.5 3.5 +/-0.4 3.9 +/-0.4 3.9 +/-0.3 3.8+/-t0.3 4.6+/-10.5 4.6 +/-0.5 4.3 +/-1.2 Oct to DEC 4.8+/-5 3.6 +/-0.3 4.8+/-0.4 5.9+/- 1.4 4.0 +/-0.3 3.6 +/-0.4 4.3 +/-0.4 3.9 +/-0.3 4.5 +/-0.4 4.1 +/-0.4 4.4+/-0.4 4.2 +/-0.4  
.3.5 +/-0.4 4.4+/-0.4 4.5 +/-0.6 4.6+/-0.4 3.6:t+/-0.4 4.2 +/- 0.5 4.3 +/-0.4 3.6 +/-0.3 4.1 +/-0.4 3.9 +/-0.5 3.6 +/-0.3 3.5 +/-0.3  
.3.5+/-0.3 3.7 +/-0.5 3.2 +/-0.3 2.8 +/-0.2 4.3 +/-0.4 4.5 +/-0.3 4.2 +/-0.3 4.0 +/-0.3 4.2+/-0.5 4.2 +/-0.4 4.6+/-0.4 4.9+/-0.4 3.9+/-0O.4 4.9 +/-0.3 4.5 +/-0.3
* 4.3+/-0.3 5.1.+/-0.6
* 3.5 +/-0.4 4.4 +/-0.3 3.4 +/-0.3 3.5 +/-0.4 4.0 +/-0.4 3.5 +/-0.4 4.2 +/-0.4 4.5 +/-0.4 4.1 +/-1.1 Q..-tR ELEMENTS AVG 3.7 +/-0.3 5.0 +/-0.5 5.6 +/-0.6 4.0 +/-0.4 3.7 +/-0.6 4.3 +/-0.3 3.9 +/-0.3 4.6+/-0.6 4.0+/-0.4 4.6 +/-0.3 4.3 +/-0.3 3.6+/-0.4 4.3 +/-0.4 4.9 +/-1.1 4.7 +/-0.4 3.8 +/-0.2 4.3 +/-0.2 4.2 +/-0.3 3.6+/-0.2 4.2 +/-0.*3 3.9 +/-0.4 3.6 +/-0.2 3.6 +/-0.3 3.6 +/-0.3 3.8 +/-0.4 3.2 +/-0.4.
2.8 +/- 0.3 4.5 +/-0.3 4.7 +/-0.5 4.2 +/-0.2 4.2 +/-0.3 4.2 +/-0.4 4.2 +/-0.2 4.7 +/-0.4 4.9 +/-0.5 3.9 +/-0.5 5.0 +/-0.2 4.5 +/-0.3 4.4 +/-0.3 5.0 +/-0.7 3.5 +/-0.3 4.5 +/-0.6 3.5 +/-0.2 3.7 +/-0.4.
3.9 +/-0.3 3.6 +/-0.5 4.4 +/-0.5 4.5 +/-0.2


TABLE C-5 2001 CONCENTRATIONS OF IODINE-131* AND GAMMA EMITTERS** IN MILK
TABLE C-5 2001 CONCENTRATIONS OF IODINE-131* AND GAMMA EMITTERS** IN MILK  
                              . Resultsin Units ef pCi/. +A 2-sigma .2.      .
..Resultsin Units ef pCi/. +A 2-sigma  
SAMPLING PERIOD                           GAMMA EMITTERS STATION ID         START             STOPQR .   . 1-131   .    .- K..40 SA-MLK-2F9           .01/01/2001        01/02/2001        <0.2        1250 t70 01/02/2001 SA-MLK-11 F3                             01/03/2001      " <0.3          1310 +/-80 SA-MLK-14F4           01/02/2001        01/03/2001        <0.2        1220 +/- 100 SA-MLK-3G1 (C)         0.1/01/2001      01/02/2001        <0.2        1360 +/-70 SA-MLK-2F9             02/05/2001      ,02/06/2001        <0.1       .1340    +/-60 SA-MLK- 11F3         .02/05/2001        02/Q6/2001        <0.2        1320    +/-70 SA-M LK- 14F4         02/05/2001        02/06/2001        <0.2        1390    +/-80 SA-MLK-3G1 (C)         02/04/2001       02/05/2001         <0.2        1340    +/-70 SA-MLK-2F9            03/05/2001       03/06/2001         <0.2        1390    +/-70 SA-MLK- 11F3          03/05/2001       .03/06/2001         <0.2        1410    +/-80 SA-MLK-14F4            03/05/2001       03/06/2001         <0.2        1370    +/-80 SA-MLK-3G1 (C)      '-63/04/2001       03/05/2001        <0.2        1320    +/-60
.2.
                                                            <0.3 SA-MLK-2F9            04/02/2001       04/03/2001                     1350    +/-80 SA-MLK-11F3            04/03/2001       04/04/2001         <0.2        1370    +/-90 SA-M LK- 14F4          04/03/2001       04/04/2001         <0.2        1340    +/-80 SA-MLK-3G1 (C)        04/02/2001       04/03/2001         <0.2        1390    +/-70 SA-MLK-2F9            04/16/2001       04/17/2001         <0.2        1330    +/-80 SA-MLK- 11F3          04/17/2001       04/18/2001         <0.2        1360    +/- 90 SA-MLK-14F4          .04/17/2001       04/18/2001         <0.3        1280    +/- 70 SA-MLK-3G1 (C)        04/17/2001       04/18/2001         <0.2        1330    +/- 70 SA-MLK-2F9            05/06/2001       05/07/2001         <0.2        1360    +/-70 SA-M LK- 11 F3        05/07/2001       05/08/2001         <0.2        1400    +/-70 SA-M LK- 14F4          05/07/2001       05/08/2001         <0.3        1330    +/-90 SA-MLK-3G1 (C)        05/07/2001       05/08/2001         <0.2        1370    +/-60 SA-MLK-2F9            05/22/2001       05/23/2001         <0.2        1360    +/-80 SA-MLK- 11F3          05/221/2001       05/23/2001         <0.2        1320    +/-70 SA-M LK- 14F4          05/22/2001       O5/2 3/2001       <0.2        1390    +/-90 SA-MLK-3G1 (C)        0/201/2002        05/22/2002        <0.2        1220    +/-70 SA-MLK-2F9            06/03/2001       ;06/04/2001       <0.2        1340    +/-60 SA-MLK-1 1 F3          06/04/2001       06/05/2001         <0.2        1310    +/-50 SA-MLK- 14F4          06/05/2001       06/05/2001         <0.2         1310    +/-50 SA-MLK-3G1 (C)        06/04/2001       06/05/2001         <0.2        1370    +/-+60 SA-MLK-2F9            06/25/2001       06/26/2001         <0.1        1390    +/-80 SA-MLK- 11 F3          06/25/2001         06/26/2001       <0.1        1370    +/-60 SA-MLK-14F4            06/2512001        06/26/2001       <0.2        1350    +/-80 SA-MLk-3G1 (C)        06/24/2001         06/25/2001       <0.2        1270    +/-70 SA-MLK-2F9            07/01/2001         07/02/2001       <0.2        1430 +/-80 SA-MLK-1 1 F3          07/01/2001         07/02/2001       <0.2        1370 +/- 70 SA-MLK-14F4            07/011/200 1      07/02/2001       <0.1       1300 +/-100 SA-MLK-3G1 (C)        07/01/200 1        07/02/2001        <0.2        1340 +/-70 SA-MLK-2F9            07/17/2001        07/18/2001        <0.2        1340   +/-70 SA-MLK- 11F3          07/17/2001        07/18/2001        <0.2        1330   +/-70 SA-M LK- 14F4          07/17/2001        07/18/2001        <0.2        1290    +/-70 SA-MLK-3G1 (C)        07/16/2001        07/17/2001        <0.2        1250   +/-70 59
SAMPLING PERIOD GAMMA EMITTERS STATION ID START STOPQR.
1-131 K..
40 SA-MLK-2F9 SA-MLK-11 F3 SA-MLK-14F4 SA-MLK-3G1 (C)
SA-MLK-2F9 SA-MLK-11F3 SA-M LK-14F4 SA-MLK-3G1 (C)
SA-MLK-2F9 SA-MLK-11F3 SA-MLK-14F4 SA-MLK-3G1 (C)
SA-MLK-2F9 SA-MLK-11F3 SA-M LK-14F4 SA-MLK-3G1 (C)
SA-MLK-2F9 SA-MLK-11F3 SA-MLK-14F4 SA-MLK-3G1 (C)
SA-MLK-2F9 SA-M LK-11 F3 SA-M LK-14F4 SA-MLK-3G1 (C)
SA-MLK-2F9 SA-MLK-11F3 SA-M LK-14F4 SA-MLK-3G1 (C)
SA-MLK-2F9 SA-MLK-1 1 F3 SA-MLK-14F4 SA-MLK-3G1 (C)
SA-MLK-2F9 SA-M LK-11 F3 SA-MLK-14F4 SA-MLk-3G1 (C)
SA-MLK-2F9 SA-MLK-1 1 F3 SA-MLK-14F4 SA-MLK-3G1 (C)
SA-MLK-2F9 SA-MLK-11F3 SA-M LK-14F4 SA-MLK-3G1 (C)
.01/01/2001 01/02/2001 01/02/2001 0.1/01/2001 02/05/2001  
.02/05/2001 02/05/2001 02/04/2001 03/05/2001 03/05/2001 03/05/2001  
'-63/04/2001 04/02/2001 04/03/2001 04/03/2001 04/02/2001 04/16/2001 04/17/2001  
.04/17/2001 04/17/2001 05/06/2001 05/07/2001 05/07/2001 05/07/2001 05/22/2001 05/221/2001 05/22/2001 0/201/2002 06/03/2001 06/04/2001 06/05/2001 06/04/2001 06/25/2001 06/25/2001 06/2512001 06/24/2001 07/01/2001 07/01/2001 07/011/200 1 07/01/200 1 07/17/2001 07/17/2001 07/17/2001 07/16/2001 01/02/2001 01/03/2001 01/03/2001 01/02/2001  
,02/06/2001 02/Q6/2001 02/06/2001 02/05/2001 03/06/2001  
.03/06/2001 03/06/2001 03/05/2001 04/03/2001 04/04/2001 04/04/2001 04/03/2001 04/17/2001 04/18/2001 04/18/2001 04/18/2001 05/07/2001 05/08/2001 05/08/2001 05/08/2001 05/23/2001 05/23/2001 O5/2 3/2001 05/22/2002
;06/04/2001 06/05/2001 06/05/2001 06/05/2001 06/26/2001 06/26/2001 06/26/2001 06/25/2001 07/02/2001 07/02/2001 07/02/2001 07/02/2001 07/18/2001 07/18/2001 07/18/2001 07/17/2001
<0.2
" <0.3
<0.2
<0.2
<0.1
<0.2
<0.2
<0.2
<0.2
<0.2
<0.2
<0.2
<0.3
<0.2
<0.2
<0.2
<0.2
<0.2
<0.3
<0.2
<0.2
<0.2
<0.3
<0.2
<0.2
<0.2
<0.2
<0.2
<0.2
<0.2
<0.2
<0.2
<0.1
<0.1  
<0.2
<0.2
<0.2
<0.2
<0.1
<0.2
<0.2
<0.2
<0.2
<0.2 1250 t70 1310 +/-80 1220 +/- 100 1360 +/-70
.1340 +/-60 1320 +/-70 1390 +/-80 1340 +/-70 1390 +/-70 1410 +/-80 1370 +/-80 1320 +/-60 1350 +/-80 1370 +/-90 1340 +/-80 1390 +/-70 1330 +/-80 1360 +/- 90 1280 +/- 70 1330 +/- 70 1360 +/-70 1400 +/-70 1330 +/-90 1370 +/-60 1360 +/-80 1320 +/-70 1390 +/-90 1220 +/-70 1340 +/-60 1310 +/-50 1310 +/-50 1370 +/-+60 1390 +/-80 1370 +/-60 1350 +/-80 1270 +/-70 1430 +/-80 1370 +/- 70 1300 +/-100 1340 +/-70 1340 +/-70 1330 +/-70 1290 +/-70 1250 +/-70 59


TABLE C-5 2001 CONCENTRATIONS OF IODINE-Ibl
TABLE C-5 2001 CONCENTRATIONS OF IODINE-Ibl
* AND GAMMA EMITTERS** IN MILK Results   n-ins bf 4Ci/L4+1- 2 sigma SAMPLING PERIOD                                         GAMMA EMITTERS STATION ID             START           STOP               1-131               K-40 SA-MLK-2F9                 08/06/2001      08/07/2001          <0.2            11420  +/- 70 SA-MLK-1 1 F3             08/06/2001      "08/0712001          <0.2            1420  +/-80 SA-MLK-14F4               08/06/2001      08/07/2001          <0.2            1280  +/-70 SA-MLK-3G1 (C)           08/05/2001      08/061200.J          <0.2            1220  +/-80 SA-MLK-2F9                08/20/2001      08/21/2001          <0.2            1380  +/-60 SA-MLK- 11 F3             08/21/2001      08/22/2001          <0.2            1330  +/-80 SA-MLK-14F4               08/21/2001      08/22/2001          <0.2            1320  +/- 80 SA-MLK-3G1 (C)           08/20/2001       08/21/2001           <0.2            1300  +/-70 SA-MLK-2F9                09/03/2001       09/04/2001           <0.2            130Q  +/-70 SA-MLK-1 1 F3              09/04/2001       09i05/2001           < 6.2            1370  +/--70 SA-MLK-14F4                09/03/2001       09/04/2001           <0.2            1320  +/-60 SA-MLK-3G 1 (C)            09/04/2001       09/05/2001           <0.2'            1280  +/-t 70 SA-MLK-2F9                09/17/2001       09/18/2001           <0.1            1390  +/-80 SA-MLK-1 1=3              09/18/2001       09/19/2001           <0.2            1350  +/-t60 SA-MLK-14F4                09/17/2001       09/18/2001           <0.4            1320  +/-70 SA-MLK-3G1 (C)            09/18/2001       09/19/2001           <0.2            1390  +/-90 SA-MLK-2F9                10/01/2001       10/02/2001           <0.2            1400 -+/-60 SA-MLK- 11 F3              10/01/2001       10/02/2001           < 0.2            1460 +/-90 SA-MLK-14F4                10/01/2001       10/02/2001           <0.2            1230 +/-70 SA-MLK-3G1 (C)            09/30/2001       10/01/2001           <0.2            1350"+/-80 SA-MLK-2F9                10/21/2001       10/22/2001           <0.2            1380  +/-80 SA-MLK-1 1 F3              10/22/2001       10/22/2001           <0.2            1350  +/-80 SA-MLK-14F4                10/21/2001       10/22/2001           <0.2            1240  +/-70 SA-MLK-3G1 (C)            :10/22/2001       10/23/2001           <0.2            1230  +/-80 SA-MLK-2F9                11/12/2001       11/13/2001           <0.2            1450  +/-70 SA-M LK- 11 F3            11/13/2001       11/14/2001           <0:1            1380  +/-70 SA-M LK- 14F4              11/13/2001       11/14/2001           <0.2            1270  + 90 SA-MLK-3G1 (C)            11113/2001       11/1412001          <0.2            1240  +/-60 SA-MLK-2F9                11/26/2001       11/27/2001           <0.2             1410  +/-80 SA-MLK-1 1 F3              11/26/2001      11/27/2001          <0.3             1420 +/-80 SA-MLK-14F4                11/26/2001      11/27/2001          <0.2            1310  +/-70 SA-MLK-3G1 (C)            11/27/2001      11/28/2001          <0.1            1310  +/-90 SA-MLK-2F9                12/09/2001      12110/2001          <0.2            1350 +/-80 SA-MLK-1 1 F3              12/09/2001      12/10/2001          <0.2            1370  +/--80 SA-MLK-14F4                12/10/2001      12/11/2001          <0.3            1380 +/-80 SA-MLK-3G1 (C)            12/09/2001      12/10/2001          <0.3            1380 +/-70 AVERAGE                                                                          1300 +/-100
* AND GAMMA EMITTERS** IN MILK Results n-ins bf 4Ci/L4+1-2 sigma SAMPLING PERIOD GAMMA EMITTERS STATION ID START STOP 1-131 K-40 SA-MLK-2F9 SA-MLK-1 1 F3 SA-MLK-14F4 SA-MLK-3G1 (C)
* Iodine-131 results are corrected for decay to midpoint of collection period & analyzed to a sensitivity of 1.0 pCi/L.
SA-MLK-2F9 SA-MLK-11 F3 SA-MLK-14F4 SA-MLK-3G1 (C)
** All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20.
SA-MLK-2F9 SA-MLK-1 1 F3 SA-MLK-14F4 SA-MLK-3G 1 (C)
SA-MLK-2F9 SA-MLK-1 1 =3 SA-MLK-14F4 SA-MLK-3G1 (C)
SA-MLK-2F9 SA-MLK-11 F3 SA-MLK-14F4 SA-MLK-3G1 (C)
SA-MLK-2F9 SA-MLK-1 1 F3 SA-MLK-14F4 SA-MLK-3G1 (C)
SA-MLK-2F9 SA-M LK-11 F3 SA-M LK-14F4 SA-MLK-3G1 (C)
SA-MLK-2F9 SA-MLK-1 1 F3 SA-MLK-14F4 SA-MLK-3G1 (C)
SA-MLK-2F9 SA-MLK-1 1 F3 SA-MLK-14F4 SA-MLK-3G1 (C) 08/06/2001 08/06/2001 08/06/2001 08/05/2001 08/20/2001 08/21/2001 08/21/2001 08/20/2001 09/03/2001 09/04/2001 09/03/2001 09/04/2001 09/17/2001 09/18/2001 09/17/2001 09/18/2001 10/01/2001 10/01/2001 10/01/2001 09/30/2001 10/21/2001 10/22/2001 10/21/2001
:10/22/2001 11/12/2001 11/13/2001 11/13/2001 11113/2001 11/26/2001 11/26/2001 11/26/2001 11/27/2001 12/09/2001 12/09/2001 12/10/2001 12/09/2001 08/07/2001 "08/0712001 08/07/2001 08/061200.J 08/21/2001 08/22/2001 08/22/2001 08/21/2001 09/04/2001 09i05/2001 09/04/2001 09/05/2001 09/18/2001 09/19/2001 09/18/2001 09/19/2001 10/02/2001 10/02/2001 10/02/2001 10/01/2001 10/22/2001 10/22/2001 10/22/2001 10/23/2001 11/13/2001 11/14/2001 11/14/2001 11/1412001 11/27/2001 11/27/2001 11/27/2001 11/28/2001 12110/2001 12/10/2001 12/11/2001 12/10/2001
<0.2
<0.2
<0.2
<0.2
<0.2
<0.2
<0.2
<0.2
<0.2
< 6.2
<0.2
<0.2'
<0.1
<0.2
<0.4
<0.2
<0.2
< 0.2
<0.2
<0.2
<0.2
<0.2
<0.2
<0.2  
<0.2
<0:1  
<0.2
<0.2
<0.2
<0.3
<0.2
<0.1  
<0.2
<0.2
<0.3
<0.3 AVERAGE 11420 +/- 70 1420 +/-80 1280 +/-70 1220 +/-80 1380 +/-60 1330 +/-80 1320 +/- 80 1300 +/-70 130Q +/-70 1370 +/-- 70 1320 +/-60 1280 +/-t 70 1390 +/-80 1350 +/-t60 1320 +/-70 1390 +/-90 1400 -+/- 60 1460 +/-90 1230 +/-70 1350"+/-80 1380 +/-80 1350 +/-80 1240 +/-70 1230 +/-80 1450 +/-70 1380 +/-70 1270 + 90 1240 +/-60 1410 +/-80 1420 +/-80 1310 +/-70 1310 +/-90 1350 +/-80 1370 +/--80 1380 +/-80 1380 +/-70 1300 +/-100
* Iodine-131 results are corrected for decay to midpoint of collection period & analyzed to a sensitivity of 1.0 pCi/L.  
** All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20.  
*** Monthly sample collected during Jan., Feb., March and Dec., when animals are not on pasture (C) Control Station 60
*** Monthly sample collected during Jan., Feb., March and Dec., when animals are not on pasture (C) Control Station 60


TABLE C-6 2001 CONCENTRATIONS OF GROSS ALPHA AND GROSS BETA EMITTERS, AND TRITIUM IN WELL WATER Results..in Units of pCi/L +/- 2 sigma .
TABLE C-6 2001 CONCENTRATIONS OF GROSS ALPHA AND GROSS BETA EMITTERS, AND TRITIUM IN WELL WATER Results..in Units of pCi/L +/- 2 sigma.
SAMPLING             GROSS           GROSS STATION ID       DATE               ALPHA               BETA TRITIUM SA-WWA-3E1     01/29/2001            1.8+/--1              13+/-1  <150 SA-WWA-3El      02/26/2001              <1.4          11+/-0.8    < 160 SA-WWA-3E1. 03/2712001            -2.4+/-1.1          10+/-0.8    <160 SA-WWA-3E1     04/30/2001           2.6+/-1.2           1-1 +/-0.8  <150 SA-WWA-3E1      05/29/2001            2.5+/-.1.3         1.0+/-0.8  <150 SA-WWA-3E1      06/25/2001            2.5_+/-!1.1           13+/-1   <150 SA-WWA-3E1      07/31/2001              <1.7.              13+/-1   <160 SA-WWA-3E1      08/27/2001            2.1 +/-1.1         13+/- 0.9   <180 SA-WWA-3E 1     09/24/2001            2.2+/-1.2          12+/--0.9  <170 SA-WWA-3E1      10/30/2001            2.1 +/--1.1            14+/-1   <150 SA-WWA-3E1      11/27/2001            1.2+/-0.9             13+/-1  <160 SA-WWA-3E 1     12/26/2001                <1             13+/-1   <180 AVERAGE                              2+/-1.1               12+/-3 61
SAMPLING GROSS GROSS STATION ID DATE ALPHA BETA TRITIUM SA-WWA-3E1 SA-WWA-3El SA-WWA-3E1.
SA-WWA-3E1 SA-WWA-3E1 SA-WWA-3E1 SA-WWA-3E1 SA-WWA-3E1 SA-WWA-3E 1 SA-WWA-3E1 SA-WWA-3E1 SA-WWA-3E 1 01/29/2001 02/26/2001 03/2712001 04/30/2001 05/29/2001 06/25/2001 07/31/2001 08/27/2001 09/24/2001 10/30/2001 11/27/2001 12/26/2001 AVERAGE 1.8+/--1
<1.4
-2.4+/-1.1 2.6+/-1.2 2.5+/-.1.3 2.5_+/-!1.1  
<1.7.
2.1 +/-1.1 2.2+/-1.2 2.1 +/--1.1 1.2+/-0.9  
<1 13+/-1 11+/-0.8 10+/-0.8 1-1 +/-0.8 1.0+/-0.8 13+/-1 13+/-1 13+/- 0.9 12+/--0.9 14+/-1 13+/-1 13+/-1
<150
< 160
<160
<150
<150
<150
<160
<180
<170
<150
<160
<180 2+/-1.1 12+/-3 61


Lii II TABLE C-7 2001 CONCENTRATIONS OF GAMMA EMITTERS* IN WELL WATER Results in Units of pCi/L +1- 2 sigma SAMPLING                 < -----
II Lii TABLE C-7 2001 CONCENTRATIONS OF GAMMA EMITTERS* IN WELL WATER Results in Units of pCi/L +1-2 sigma SAMPLING GAMMA EMITTERS ---- >
GAMMA EMITTERS ---- >
STATION ID DAtE...............
STATION ID               DAtE   ............... K-40                 RA-NAT SA-WWA-3E1             01/29/2001                   <46                 193 +/-7 SA-WWA-3E 1           02/26/2001                 77 +/- 26               178 +/- 5 SA-WWA-3E1             03/27/2001                 74+/-251               193+/-6 SA-WWA-3E 1           04/30/2001                   <45                 144 +/-__
K-40 RA-NAT SA-WWA-3E1 01/29/2001  
5 SA-WWA-3E1             05/29/2001                   <18                 154+/-5 SA-WWA-3E1             06/25/2001                   <41                 98+/-4 SA-WWA-3E1             07/31/2001                   <28                 138 +/-5 SA-WWA-3E1             08/27/2001                   <16                 124+/-4 SA-WWA-3E1             09/24/2001                   <23                 130+/- 5 SA-WWA-3E1             .10/30/2001                 48+/-20                 166 +/- 5 SA-WWA-3E1             11/27/2001                 <16                 90+4 SA-WWA-3E1             12/26/2001                 85+/-35                 139 +/-7 AVERAGE                                                             146 +/-67
<46 193 +/-7 SA-WWA-3E 1 02/26/2001 77 +/- 26 178 +/- 5 SA-WWA-3E1 03/27/2001 74+/-251 193+/-6 SA-WWA-3E 1 04/30/2001  
<45 144 +/-__
5 SA-WWA-3E1 05/29/2001  
<18 154+/-5 SA-WWA-3E1 06/25/2001  
<41 98+/-4 SA-WWA-3E1 07/31/2001  
<28 138 +/-5 SA-WWA-3E1 08/27/2001  
<16 124+/-4 SA-WWA-3E1 09/24/2001  
<23 130+/- 5 SA-WWA-3E1  
.10/30/2001 48+/-20 166 +/- 5 SA-WWA-3E1 11/27/2001  
<16 90+4 SA-WWA-3E1 12/26/2001 85+/-35 139 +/-7 AVERAGE 146 +/-67
* All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20.
* All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20.
62
62


TABLE C-8 2001 CONCENTRATIONS OF GROSS ALPHA ANDGROSS BETAEMITTERS AND TRITIUM IN RAW AND TREATED POTABLE WATER Results in Units of pCi/L +/- 2 sigma SAMPLING          . GROSS               GROSS TYPE        PERIOD            ALPHA               BETA   TRITIUM RAW            1/1-3-1/2001        .. +/-0.5 ..         3.6+/-0.5   < 150 TREATED        1/1-31/2001          1.1 +/-0.6           3.4+/-0.5   <150 RAW            2/1-28/2001        0.8+/-0.5             2.9+/-0.5   <160 TREATED        2/1-28/2001            <1.1             3.3+/-0.5   <160 RAW            3/1-31/2001          1.3+/-0.6             3-+/-0.5   <160 TREATED        3/1-31/2001          1.1 +/-0.6           3.1 +/-0.5   <160 RAW            4/1-30/2001        0.7-+/-0.5           3.4+/-0.5   <150 TREATED        4/1-30/2001        0.9-+/-0.6           2.8-+/-0.5   < 1,50 5/1-31/2001 RAW            5/1-31/2001            <0.7             2.9+/-0.5   <150 TREATED                                <0.8             3+/-0.5     <1 50 6/1-30/2001 RAW            6/1-30/2001          1.4+/-0.6           4.7-+/-0.6   < 150 TREATED                              1.6+/-0.8           4.7_+/-0.6   <150 7/1-31/2001 RAW                                    <0.9             4.6+/-0.6   <150 7/1-31/2001 TREATED                                < 1.1           3.9 +/-0.6   <160 8/1-31/2001 RAW                                0.6+/-0.5             3.5+/-0.5   <180 8/1-31/2001 TREATED                              1 +/-0.7           4.4+/-0.6     <170 9/1-301/2001 RAW                                0.8-+/-0.6             3-+/-0.6   < 170 9/1-30/2001 TREATED                            0.8+/-0.6             3.2+/-0.6   <170 10/1-31/2001 RAW            10/1-31/2001        0.7-+/-0.5           2.7-+/-0.5   <160 TREATED                            0.8+/-0.6             3_+/-0.6   <160 11/1-30/2001 RAW            11/1-30/2001        0.7_+/-0.5           2.8_+/-0.5   <160 TREATED                                <0.8             3.3+/-0.6   <160 121/1-31/2001 RAW                                0.6-+/-0.4           3.5+/-0.6   <170 12/1-31/2001 TREATED                                <0.6             3.7+/-0.6   <170 AVERAGE RAW                                0.8+/- 0.4           3.4+/-11.3 TREATED                              1 +/-0.3            3.5+/-11.2 GRAND AVERAGE                        0.9 +/-0.5          3.4+/-E 1.2 63
TABLE C-8 2001 CONCENTRATIONS OF GROSS ALPHA ANDGROSS BETAEMITTERS AND TRITIUM IN RAW AND TREATED POTABLE WATER TYPE RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED Results SAMPLING PERIOD 1/1-3-1/2001 1/1-31/2001 2/1-28/2001 2/1-28/2001 3/1-31/2001 3/1-31/2001 4/1-30/2001 4/1-30/2001 5/1-31/2001 5/1-31/2001 6/1-30/2001 6/1-30/2001 7/1-31/2001 7/1-31/2001 8/1-31/2001 8/1-31/2001 9/1-301/2001 9/1-30/2001 10/1-31/2001 10/1-31/2001 11/1-30/2001 11/1-30/2001 121/1-31/2001 12/1-31/2001 AVERAGE RAW TREATED GRAND AVERAGE in Units of pCi/L +/- 2 sigma  
. GROSS GROSS ALPHA BETA  
.. +/-0.5..
3.6+/-0.5 1.1 +/-0.6 3.4+/-0.5 0.8+/-0.5 2.9+/-0.5  
<1.1 3.3+/-0.5 1.3+/-0.6 3-+/-0.5 1.1 +/-0.6 3.1 +/-0.5 0.7-+/-0.5 3.4+/-0.5 0.9-+/-0.6 2.8-+/-0.5  
<0.7 2.9+/-0.5  
<0.8 3+/-0.5 1.4+/-0.6 4.7-+/-0.6 1.6+/-0.8 4.7_+/-0.6  
<0.9 4.6+/-0.6  
< 1.1 3.9 +/-0.6 0.6+/-0.5 3.5+/-0.5 1 +/-0.7 4.4+/-0.6 0.8-+/-0.6 3-+/-0.6 0.8+/-0.6 3.2+/-0.6 0.7-+/-0.5 2.7-+/-0.5 0.8+/-0.6 3_+/-0.6 0.7_+/-0.5 2.8_+/-0.5  
<0.8 3.3+/-0.6 0.6-+/-0.4 3.5+/-0.6  
<0.6 3.7+/-0.6 0.8+/- 0.4 1 +/-0.3 0.9 +/-0.5 3.4+/-11.3 3.5+/-11.2 3.4+/-E 1.2 63 TRITIUM
< 150
<150
<160
<160
<160
<160
<150
< 1,50
<150
<1 50
< 150
<150
<150
<160
<180
<170
< 170
<170
<160
<160
<160
<160
<170
<170


TABLE C-9 2001 CONCENTRATIONS OF IODINE-131* AND GAMMA EMITTERS**
TABLE C-9 2001 CONCENTRATIONS OF IODINE-131* AND GAMMA EMITTERS**
S..
S..
IN .RAW.kND-.TREATrI POTABLE WATER .
IN.RAW.kND-.TREATrI POTABLE WATER  
                                      'Results in Units -of'p/ I + /-,2 s-gm..
'Results in Units -of'p/
SAMPLING                                <-----GAMMA EMITTERS -----
I + /-,2 s-gm..
TYPE              PERIOD               1-131                K-40        RA-NAT RAW                    1/1-31/2001             <0.2               33+/-13          <3.5 TREATED                1/1-31/200f'            <0.3               701.+/-18        <2.6 RAW                    2/1-28/2001             <0.2                  <17          <3.4 TREATED                2/1-28/2001             <0.2                <13          6.5+/-1.2 RAW                    3/1-31/2001             <0.3                61 +/-18          <1.7 TREATED                3/1-31/2001             <0.3'                <14            <1.8 RAW                    4/1-30/2001             <0.1               46 +/- 17          <2.1 TREATED                4/1-30/2001             <0.2                29+/-14            < 1.9 RAW                    5/1-31/2001             <0.2                 <14            <1.9 TREATED                5/1-31/2001            <0.4                 <16            <2.2 RAW                    6/1-30/2001            <0.1                  <33            <1.6 TREATED                6/1-30/2001            <0.2                   <7            <2 RAW                    7/1-3 ff2001            <0.2                 <14           <1.6 TREATED                7/1-31/2001            <0.2                  < 1.3          < 2.2 RAW                    8/1-31/2001            <0.3               61 +/-15         <2.3 TREATED                8/1-31/2001            <0.2                  <.16         5 +/-2.2 RAW                    9/1-30/2001            <0.3                  <14         4+/-1.4 TREATED                9/1-30/2001            <0.2                50'+/- 16         < 3-.2 RAW                    10/1-31/2001            <0.2              40+/-18           <1.9 TREATED                10/1-31/2001            <0.2                34+/-13           <4.5 RAW                    11/1-30/2001                                  <17           <1.7 TREATED                11/1-30/2001            < 0,14
TYPE RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED AVERAGES RAW TREATED GRAND AVERAGE 32_+/-35
                                                                          <16         6.1 +/-2.6 RAW                    12/1-31/2001            <0.3              31 +/-13 12/1-31/2001                                                < 1.8 TREATED                                        <0.2              26+/-11           5.4+/-_2 AVERAGES RAW                                                                32_+/-35 TREATED GRAND AVERAGE
* Iodine-1 31 analyzed to a sensitivity of 1.0 pCi/L.
* Iodine-1 31 analyzed to a sensitivity of 1 .0 pCi/L.
All other gamma emitters searched for were < LLD; typical LLDs are given in Table C-20.
**  All other gamma emitters searched for were < LLD; typical LLDs are given in Table C-20.
64 SAMPLING PERIOD 1/1-31/2001 1/1-31/200f' 2/1-28/2001 2/1-28/2001 3/1-31/2001 3/1-31/2001 4/1-30/2001 4/1-30/2001 5/1-31/2001 5/1-31/2001 6/1-30/2001 6/1-30/2001 7/1-3 ff2001 7/1-31/2001 8/1-31/2001 8/1-31/2001 9/1-30/2001 9/1-30/2001 10/1-31/2001 10/1-31/2001 11/1-30/2001 11/1-30/2001 12/1-31/2001 12/1-31/2001 1-131
64
<0.2  
<0.3
<0.2
<0.2
<0.3
<0.3'
<0.1  
<0.2
<0.2
<0.4  
<0.1
<0.2
<0.2  
<0.2  
<0.3
<0.2
<0.3
<0.2
<0.2
<0.2  
< 0,14
<0.3
<0.2
<-----GAMMA EMITTERS -----
K-40 RA-NAT 33+/-13
<3.5 701.+/-18
<2.6
<17
<3.4
<13 6.5+/-1.2 61 +/-18
<1.7
<14  
<1.8 46 +/- 17
<2.1 29+/-14
< 1.9
<14
<1.9
<16
<2.2  
<33
<1.6
<7
<2
<14
<1.6
< 1.3  
< 2.2 61 +/-15  
<2.3  
<.16 5 +/-2.2  
<14 4+/-1.4 50'+/- 16  
< 3-.2 40+/-18  
<1.9 34+/-13  
<4.5  
<17  
<1.7  
<16 6.1 +/-2.6 31 +/-13  
< 1.8 26+/-11 5.4+/-_2


TABLE C-10 2001 CONCENTRATIONS OF GAMMA EMITTERS* IN VEGETABLES Results in Units of. pCi/kg (Wet) +&#xf7;/- 2 sigma SAMPLING                             <--- GAMMA EMITTERS --- >
TABLE C-10 2001 CONCENTRATIONS OF GAMMA EMITTERS* IN VEGETABLES Results in Units of. pCi/kg (Wet) +&#xf7;/-
STATION ID           DATE           SAMPLE TYPE,             K-40     Ra-NAT SA-FP-29 ..           04/23/2001         Asparagus           2470 +/- 260   <15 SA-FPV-2G2 (C"       05/07/2001         Asparagus           2480+/-100     < 9.6 AVERAGE       ......                                        2400-+
2 sigma SAMPLING  
SA-FPL-14F3           07/24/2001           Cabbage,           1860+/-140     < 5.8 SA-FPL-3H5 (C)       07/18/2001           Cabbage           2510+/-140     <9.8 SA-FPL-6F2           07/23/2001           Cabbage           2190+/-140     <8.7 AVERAGE                                                       2190+/-650 SA-FPV-2F4           07/18/2001             Corn           2490+/-180     <7.7 SA-FPV-2F9           07/18/2001             Corn           2470+/-160     < 6.7 SA-FPV-1G1 (C)       07/10/2001             Corn           2710+/- 90     < 5.8 SA-FPV-3H5 (C)       07/18/2001             Corn           2430+/-100     < 9.2 SA-FPV-2G2 (C)       07/18/2001             Corn           2440+/-160     < 7.1 SA-FPV-14F3           07/24/2001             Corn.           2140+/-170     <6.8 SA-FPV-14G2 (C)       07/17/2001             Corn           2620+/-170     < 7.3 AVERAGE                                                     2470+/-360 SA-FPV-2F4           07/23/2001           Peppers           1700+/-140     < 8.6 SA-FPV-3F5           07/18/2001           Peppers           1440+/-160     < 8.5 SA-FPV- 1G 1 (C)     07/18/2001           Peppers           1500+/-160     < 9.3 SA-FPV-3H5   (C)     07/18/2001           Peppers           1230+/- 150     <11 SA-FPV-2G2   (C)     07/18/2001           Peppers           1380+/-100     < 9.3 SA-FPV-9G1   (C)     07/24/2001           Peppers           1480 +/- 130   <8 SA-FPV-6F2           07/23/2001           Peppers           1420+/-140     < 8.7 AVERAGE                                                       1450+28260 SA-FPV-2F4           07/24/2001         Tomatoes           2090+/-150     < 6.8 SA-FPV-2F9           07/24/2001         Tomatoes           1930+/- 130     <6.9 SA-FPV-3F5           07/18/2001         Tomatoes           2000+/-80       < 7.9 SA-FPV-1G1   (C)     07/18/2001         Tomatoes           1900+/-210     <7.2 SA-FPV-3H5   (C)     07/18/2001         Tomatoes           1930+/- 150     <7.4 SA-FPV-2G2   (C)     07/18/2001         Tomatoes           2160+/-150     < 6.9 SA-FPV-9G1   (C)     07/24/2001         Tomatoes           1810+/- 150     < 7.2 SA-FPV-6F2           07/2312001         Tomatoes           2570+/- 80     16 +/- 3 SA-FPV-14G2 (C)       07/24/2001         Tbmatoes           2290+/-160     < 6.6 SA-FPV-14F3           07/24/2001         Tomatoes           2500+/-90       < 5.4 AVERAGE                                                       2120+/- 520 GRAND AVERAGE                                                 2070+/-870 SAll other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20 (C) Control Station 65
<--- GAMMA EMITTERS --- >
STATION ID DATE SAMPLE TYPE, K-40 Ra-NAT SA-FP-29..
04/23/2001 Asparagus 2470 +/- 260  
<15 SA-FPV-2G2 (C" 05/07/2001 Asparagus 2480+/-100  
< 9.6 AVERAGE 2400-+
SA-FPL-14F3 07/24/2001
: Cabbage, 1860+/-140  
< 5.8 SA-FPL-3H5 (C) 07/18/2001 Cabbage 2510+/-140  
<9.8 SA-FPL-6F2 07/23/2001 Cabbage 2190+/-140  
<8.7 AVERAGE 2190+/-650 SA-FPV-2F4 07/18/2001 Corn 2490+/-180  
<7.7 SA-FPV-2F9 07/18/2001 Corn 2470+/-160  
< 6.7 SA-FPV-1G1 (C) 07/10/2001 Corn 2710+/- 90  
< 5.8 SA-FPV-3H5 (C) 07/18/2001 Corn 2430+/-100  
< 9.2 SA-FPV-2G2 (C) 07/18/2001 Corn 2440+/-160  
< 7.1 SA-FPV-14F3 07/24/2001 Corn.
2140+/-170  
<6.8 SA-FPV-14G2 (C) 07/17/2001 Corn 2620+/-170  
< 7.3 AVERAGE 2470+/-360 SA-FPV-2F4 07/23/2001 Peppers 1700+/-140  
< 8.6 SA-FPV-3F5 07/18/2001 Peppers 1440+/-160  
< 8.5 SA-FPV-1G 1 (C) 07/18/2001 Peppers 1500+/-160  
< 9.3 SA-FPV-3H5 (C) 07/18/2001 Peppers 1230+/- 150  
<11 SA-FPV-2G2 (C) 07/18/2001 Peppers 1380+/-100  
< 9.3 SA-FPV-9G1 (C) 07/24/2001 Peppers 1480 +/- 130  
< 8 SA-FPV-6F2 07/23/2001 Peppers 1420+/-140  
< 8.7 AVERAGE 1450+28260 SA-FPV-2F4 07/24/2001 Tomatoes 2090+/-150  
< 6.8 SA-FPV-2F9 07/24/2001 Tomatoes 1930+/- 130  
<6.9 SA-FPV-3F5 07/18/2001 Tomatoes 2000+/-80  
< 7.9 SA-FPV-1G1 (C) 07/18/2001 Tomatoes 1900+/-210  
<7.2 SA-FPV-3H5 (C) 07/18/2001 Tomatoes 1930+/- 150  
<7.4 SA-FPV-2G2 (C) 07/18/2001 Tomatoes 2160+/-150  
< 6.9 SA-FPV-9G1 (C) 07/24/2001 Tomatoes 1810+/- 150  
< 7.2 SA-FPV-6F2 07/2312001 Tomatoes 2570+/- 80 16 +/- 3 SA-FPV-14G2 (C) 07/24/2001 Tbmatoes 2290+/-160  
< 6.6 SA-FPV-14F3 07/24/2001 Tomatoes 2500+/-90  
< 5.4 AVERAGE 2120+/- 520 GRAND AVERAGE 2070+/-870 SAll other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20 (C) Control Station 65


TABLE C&#xfd;,i1 2001 CONCENTRATIONS Of GAMMA EMITTERS* IN GAME Results in Units of pCi/kg (wet) +1- 2 sigma SAMPLING                               GAMMA EM.ITTER5.
TABLE C&#xfd;,i1 2001 CONCENTRATIONS Of GAMMA EMITTERS* IN GAME Results in Units of pCi/kg (wet) +1-2 sigma SAMPLING GAMMA EM.ITTER5.
STATION ID               DATE             SAMPLE TYPE               K-40 SA-GAM-11 D1 (C)           02/26/2001             Muskrat           2840 +/-160 SA-GAM-3E1                02/20/2001              Muskrat            2600+/-190 AVERAGE                                            Muskrat            2720+/-340
STATION ID DATE SAMPLE TYPE K-40 SA-GAM-11 D1 (C)
SA-GAM-3E1 02/26/2001 02/20/2001 AVERAGE Muskrat Muskrat Muskrat 2840 +/-160 2600+/-190 2720+/-340
*All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20.
*All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20.
66
66


TABLE C-1-2 2001 CONCENTRATIONS;OF GAMMA- EMITT*ERS* iN FODDER CROPS Results in Units of pCi/kg (wet) +1- 2 sigma SAMPLING                                   <- GAMMA EMITTERS ->
TABLE C-1-2 2001 CONCENTRATIONS;OF GAMMA-EMITT*ERS* iN FODDER CROPS Results in Units of pCi/kg (wet) +1-2 sigma SAMPLING  
          "STATION ID         DATE --     SAM PLE IYPE         be-7           K-40   Ra-NAT SA-VGT-2F9         10/22/2001           Silage          670+/-_70      2560+/-150      <10 SA-VGT-3G1 (C)    10/30/2001           Silage         350+/-70       4380+/-180    10_+/-5 SA-VGT- 14F4      10/22/2001          Silage          370 +/- 60      2920+/-160       <5 SA-VGT- 11 F3      10/30/2001          Silage          210+/-_50      4990 +/-220      <8 AVERAGE                                                400+/-390       3710+/-2320 SA-VGT-1 1 F3      10/30/2001       Soybeans           <40         14900+/-_320   <10 SA-VGT-14F4        11/1412001        Soybeans            <30        16800_+/-310   20_+/-6 AVERAGE                                                              15900+/- 2700  15__14
<- GAMMA EMITTERS ->  
"STATION ID DATE --
SAM PLE IYPE be-7 K-40 Ra-NAT SA-VGT-2F9 SA-VGT-3G1 (C)
SA-VGT-14F4 SA-VGT-11 F3 AVERAGE SA-VGT-1 1 F3 SA-VGT-14F4 10/22/2001 10/30/2001 10/22/2001 10/30/2001 Silage Silage Silage Silage 670+/-_70 350+/-70 370 +/- 60 210+/-_50 2560+/-150 4380+/-180 2920+/-160 4990 +/-220
<10 10_+/-5
<5
<8 400+/-390 3710+/-2320 10/30/2001 11/1412001 Soybeans Soybeans
<40  
<30 AVERAGE 14900+/-_320 16800_+/-310 15900+/- 2700
<10 20_+/-6 15_ _14
* All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20.
* All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20.
(C) Location 3G1 is the Control Station.
(C) Location 3G1 is the Control Station.
67
67


TABLE C-13 2001 CONCENTRATIONS OF GAMMA EMITTERS* IN SOIL Results in Units of pCi/kg (dry) +/- 2 sigma SAMPLING STATION ID           DATE           Be-7         K-40         Cs-137   Ra-NAT     Th-232 SA-SOL-6S2         05/15/2001       <110        5540 +/- 220        26+/-7    260+/-+15
TABLE C-13 2001 CONCENTRATIONS OF GAMMA EMITTERS* IN SOIL Results in Units of pCi/kg (dry) +/- 2 sigma SAMPLING STATION ID DATE Be-7 K-40 Cs-137 Ra-NAT Th-232 SA-SOL-6S2 SA-SOL-2F7 SA-SOL-2F9 SA-SOL-5F1 S.L:j-SOL-10DI1 SA-SOL-14F4 SA-SOL-16E1 SA-SOL-1 1 F3 SA-SOL-3G 1 (C) 05/15/2001 05/16/2001 05/15/2001 05/15/2001 05/14/2001 05/15/2001 05/15/2001 05/15/2001 05/16/2001
                                                                -                      350 +/-40 SA-SOL-2F7          05/16/2001       <85       7910+/-+300      290 +/- 18  590 +/- 23    710+/--51 SA-SOL-2F9          05/15/2001      120+/-54      6100+/- 140       240+/-9    490+/-11      530 +/- 24 SA-SOL-5F1          05/15/2001      150+/- 56      4610+/-130        260+/-9    550 +/-12    620 +/- 31 S.L:j-SOL-10DI1    05/14/2001        <70        9070+/-290       350+/-19    850+/- 27    990+/- 50 SA-SOL-14F4        05/15/2001      <130      12900 +/- 380      180*+/- 12 910+/-22    1090+/- 54 SA-SOL-16E1        05/15/2001      <120      11900 +/- 290      110+/-13    660_+/-16    840+/-60 SA-SOL-1 1 F3      05/15/2001    360+/-130      12800 +/- 390        <49    970+/-29     1200 +/- 54 SA-SOL-3G 1 (C)    05/16/2001      < 140      8190+/- 250        160+/-13    700+/-16    850 +/- 57 GRAND AVERAGE                                  8780+/-6290        190+/-220  660+/-450    800+/-550
<110
* All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20 (C) Control Station 68
<85 120+/-54 150+/- 56
<70
<130
<120 360+/-130
< 140 5540 +/- 220 7910+/-+300 6100+/- 140 4610+/-130 9070+/-290 12900 +/- 380 11900 +/- 290 12800 +/- 390 8190+/- 250 GRAND AVERAGE 8780+/-6290 190+/-220 660+/-450 800+/-550
* All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20 (C) Control Station 68 26+/-7 290 +/- 18 240+/-9 260+/-9 350+/-19 180*+/- 12 110+/-13
<49 160+/-13 260+/-+15 590 +/- 23 490+/-11 550 +/-12 850+/- 27 910+/-22 660_+/-16 970+/-29 700+/-16 350 +/-40 710+/--51 530 +/- 24 620 +/- 31 990+/- 50 1090+/- 54 840+/-60 1200 +/- 54 850 +/- 57


TABLE C-14 2001 CONCENTRATIONS OFGROSS BETA EMITTERS IN SURFACE WATER Results in Units of pCi/L +/- 2 sigma
TABLE C-14 2001 CONCENTRATIONS OFGROSS BETA EMITTERS IN SURFACE WATER Results in Units of pCi/L +/- 2 sigma STATION ID --------.......................................... >
                                      ------------------- ----    STATION ID --------.......................................... >
SAMPLING SA-SWA-11 Al SA-SWA-1 2C1 SA-SWA-1 6F1 SA-SWA-1 F2 SA-SWA-7E1 AVERAGE DATE (Control)
SAMPLING SA-SWA- 11 Al             SA-SWA- 1 2C1       SA-SWA-1 6F1         SA-SWA-1 F2                 SA-SWA-7E1         AVERAGE DATE                                 (Control)
January February March April May C'
January           114+/-7                       86+/-6                 72+/-5              61 +/-5                        126+/-8          92+/- 55 February          78+/-6                       75 +/- 6               44+/-4                33+/-4                        98+/- 7          66 +/- 53 March              89 +/- 6                     77+/-6                 58+/-_5              40+/-4                         122+/-8          77 +/-62 16+/-3                        6+/-+2                  5+/-2                5+/-2                        34+/-4            13+/-25 April May                41 +/-4                     33+/-4                  25+/-3               21+/-3                         66+/-5            37 _36 C'
June July August September October November December AVERAGE 114+/-7 78+/-6 89 +/- 6 16+/-3 41 +/-4 56+/-5 71 +/-6 80+/-6 128+/-9 163+/-9 156+/-12 150+/-12 95 +/- 95 86+/-6 75 +/- 6 77+/-6 6+/-+2 33+/-4 29+/-4 43+/-5 67+/-6 85+/-7 129+/-8 112+/-10 108-+/--11 71 +/-74 72+/-5 44+/-4 58+/-_5 5+/-2 25+/-3 20-+/-3 32+/-4 48+/-5 79+/-6 114+/-7 109+/-10 111_+/-11 60 +/- 75 61 +/-5 33+/-4 40+/-4 5+/-2 21+/-3 23+/-3 23+/-4 57-5 77-+/-6 100+/-7 108 +/-10 100-+/-10 54+/-71 126+/-8 98+/- 7 122+/-8 34+/-4 66+/-5 60+/-5 99+/-7 104+/--7 138+/-9 224.+/- 11 167 +/-12 173+/-13 92+/- 55 66 +/- 53 77 +/-62 13+/-25 37 _36 37 #t38 53+/-62 71 -43 101 +/-58 146 +/-99 130-+/--57 128+/-63 118+/-106 GRAND AVERAGE 79++/-95 y
June                                          29+/-4                  20-+/-3              23+/-3                        60+/-5            37 #t38 56+/-5 July              71 +/-6                      43+/-5                 32+/-4               23+/-4                         99+/-7            53+/-62 67+/-6                48+/-5                57-5                 *. 104+/--7      y 71 -43 August            80+/-6 September        128+/-9                      85+/-7                 79+/-6              77-+/-6                      138+/-9            101 +/-58 October          163+/-9                      129+/-8                 114+/-7              100+/-7                      224.+/- 11          146 +/-99 November        156+/-12                    112+/-10                109+/-10              108 +/-10                    167 +/-12           130-+/--57 December        150+/-12                    108-+/--11              111_+/-11            100-+/-10                    173+/-13            128+/-63 4
4
AVERAGE          95 +/- 95                    71 +/-74                60 +/- 75            54+/-71                      118+/-106 GRAND AVERAGE                                     79++/-95


TABLE'C-I 5 2001 CONCENTRATIONS OF GAMMA EMITTERS* IN SURFACE' WATER Results in Units of pCi/L +/- 2 sigma SAMFLING                   GAMMA EMITTERS STATION ID             DATE                           K-40 SA-SWA- 1F2            01/08/2001                        60+/-_19 SA-SWA-7E1             01/08/2001                        120+/-22 SA-SWA-11 Al             01/08/2001                        137+/-_21 SA-SWA-1 2C1 (C)         01/08/2001                        85+/--19 SA-SWA-1 6F1             01/08/2001                        62 +/- 25 SA-SWA-1 F2             02/06/2001                        80+/-24 SA-SWA-7E1               02/06/2001                        131 +/-21 SA-SWA- 11 A1           02/06/2001                        1_18+/-28 SA-SWA-12C1 (C)         02/06/2001                        61+/-20 SA-SWA-1 6F1             02/06/2001                        68+/- 22 SA-SWA-1 F2             03/08/2001                        73 +/- 20 SA-SWA-7E1               03/08/2001                      101 +/-23 SA-SWA- 11 A1           03/08/2001                      103 +/-25 SA-SWA- 12C1 (C)         03/08/2001                      134-+/-23 SA-SWA-16F1              03/08/2001                        53+/--18 SA-SWA- 1F2              04/06/2001                        43-+/-19 SA-SWA-7E1              04/06/2001                        65+/-_18 SA-SWA- 11 A1            04/06/2001                        58_+/- 19 SA-SWA-i 2C1 (C)         04/06/2001                       38 +/-13 SA-SWA-1 6F1            04/06/2001                       58 +/- 23 SA-SWA-1 F2              05/11/2001                       42+/-19 SA-SWA-7E1              05/11/2001                       75 +/-21 SA-SWA- 11 A1            05/11/2001                       54+/- 20 SA-SWA-12C1 (C)          05/11/2001                         <21 SA-SWA-16F1              05/11/2001                         <28 SA-SWA-1 F2              06/06/2001                         <23 SA-SWA-7E1              06/06/2001                       71 +/-15 SA-SWA-1 lA1            06/06/2001                       101 +/-20 SA-SWA-12C1 (C)          06/06/2001                        87+/-12 SA-SWA-1 6F1            06/06/2001                        72+/- 20 SA-SWA-1 F2              07/03/2001                        64+/-17 SA-SWA-7 E1              07/03/2001                      102-+/-19 SA-SWA- 11A1            07/03/2001                        88_+/-18 SA-SWA-i 2C1 (C)        07/03/2001                        67_+/-16 SA-SWA-16F1              07/03/2001                        74+/-17 70
TABLE'C-I 5 2001 CONCENTRATIONS OF GAMMA EMITTERS* IN SURFACE' WATER Results in Units of pCi/L +/- 2 sigma SAMFLING GAMMA EMITTERS STATION ID DATE K-40 SA-SWA-1 F2 SA-SWA-7E1 SA-SWA-11 Al SA-SWA-1 2C1 (C)
SA-SWA-1 6F1 SA-SWA-1 F2 SA-SWA-7E1 SA-SWA-11 A1 SA-SWA-12C1 (C)
SA-SWA-1 6F1 SA-SWA-1 F2 SA-SWA-7E1 SA-SWA-11 A1 SA-SWA-12C1 (C)
SA-SWA-16F1 SA-SWA-1 F2 SA-SWA-7E1 SA-SWA-11 A1 SA-SWA-i 2C1 (C)
SA-SWA-1 6F1 SA-SWA-1 F2 SA-SWA-7E1 SA-SWA-11 A1 SA-SWA-12C1 (C)
SA-SWA-16F1 SA-SWA-1 F2 SA-SWA-7E1 SA-SWA-1 lA1 SA-SWA-12C1 (C)
SA-SWA-1 6F1 SA-SWA-1 F2 SA-SWA-7 E1 SA-SWA-11A1 SA-SWA-i 2C1 (C)
SA-SWA-16F1 01/08/2001 01/08/2001 01/08/2001 01/08/2001 01/08/2001 02/06/2001 02/06/2001 02/06/2001 02/06/2001 02/06/2001 03/08/2001 03/08/2001 03/08/2001 03/08/2001 03/08/2001 04/06/2001 04/06/2001 04/06/2001 04/06/2001 04/06/2001 05/11/2001 05/11/2001 05/11/2001 05/11/2001 05/11/2001 06/06/2001 06/06/2001 06/06/2001 06/06/2001 06/06/2001 07/03/2001 07/03/2001 07/03/2001 07/03/2001 07/03/2001 70 60+/-_19 120+/-22 137+/-_21 85+/--19 62 +/- 25 80+/-24 131 +/-21 1_18+/-28 61+/-20 68+/- 22 73 +/- 20 101 +/-23 103 +/-25 134-+/-23 53+/--18 43-+/-19 65+/-_18 58_+/- 19 38 +/-13 58 +/- 23 42+/-19 75 +/-21 54+/- 20
<21
<28
<23 71 +/-15 101 +/-20 87+/-12 72+/- 20 64+/-17 102-+/-19 88_+/-18 67_+/-16 74+/-17


TABLEC-15 2001 CONCENTRATIONS. OF GAMMA EMITTERS*. INSURFACE WATER Results in Units. of pCi.L0 1-*/- 2-sigma SAMPLING                       GAMMA EMITTERS STATION !P.               DA'                                 K,40 SA-SWA-1 F2                   08/08/2001                            92+/-19 SA-SWA-7E1                   08/08/2001                            111+/-21 SA-SWA-1 1 Al                 08/08/2001                            93+/-19 SA-SWA-i 2C1 (C)             08/08/2001                            102+/-19 SA-SWA-1 6F1                 08/08/2001                            75+/-16 SA-SWA-1 F2                   09/03/2001                            50+/-18 SA-SWA-7E1                   09/03/2001                            117+/-_22 SA-SWA-11 A1                 09/03/2001                            162_+/-20 SA-SWA- 1 2C1 (C)             09/03/2001                            79_+/-14 SA-SWA-1 6F1                 09/03/2001                            74+/-22 SA-SWA-1 F2                   10/03/2001                          112+/-20 SA-SWA-7E1                   10/03/2001                            101 +/-23 SA-SWA- 11 A1                 10/03/2001                            178 +/-28 SA-SWA-i 2C1 (C)             10/03/2001                            107 +/-23 SA-SWA-1 6F1                 10/03/2001                              <14 SA-SWA-1 F2                   11/13/2001                            79_+/-19 SA-SWA-7E 1                   11/13/2001                            153 +/-18 SA-SWA- 11A 1                 11/13/2001                            101 +/-23 SA-SWA-i 2C1 (C)             11/13/2001                            165 +/-25 SA-SWA-116F1                 11/13/2001                            124+/-_16 SA-SWA-1 F2                   12/10/2001                            110+/-_21 SA-SWA-7 E1                   12/10/2001                          176+/- 24 SA-SWA-11 A1                   12/10/2001                          138_+/-20 SA-SWA-1 2C1 (C)               12/10/2001                           164+/-32 SA-SWA-1 6F1                  12/10/2001                           144+/--29 AVERAGE                                                             91 +/-79
TABLEC-15 2001 CONCENTRATIONS. OF GAMMA EMITTERS*. INSURFACE WATER Results in Units. of pCi.L0 1-*/- 2-sigma SAMPLING GAMMA EMITTERS STATION !P.
DA' K,40 SA-SWA-1 F2 SA-SWA-7E1 SA-SWA-1 1 Al SA-SWA-i 2C1 (C)
SA-SWA-1 6F1 SA-SWA-1 F2 SA-SWA-7E1 SA-SWA-11 A1 SA-SWA-1 2C1 (C)
SA-SWA-1 6F1 SA-SWA-1 F2 SA-SWA-7E1 SA-SWA-11 A1 SA-SWA-i 2C1 (C)
SA-SWA-1 6F1 SA-SWA-1 F2 SA-SWA-7E 1 SA-SWA-11A 1 SA-SWA-i 2C1 (C)
SA-SWA-116F1 SA-SWA-1 F2 SA-SWA-7 E1 SA-SWA-11 A1 SA-SWA-1 2C1 (C)
SA-SWA-1 6F1 08/08/2001 08/08/2001 08/08/2001 08/08/2001 08/08/2001 09/03/2001 09/03/2001 09/03/2001 09/03/2001 09/03/2001 10/03/2001 10/03/2001 10/03/2001 10/03/2001 10/03/2001 11/13/2001 11/13/2001 11/13/2001 11/13/2001 11/13/2001 12/10/2001 12/10/2001 12/10/2001 12/10/2001 12/10/2001 AVERAGE
* All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20.
* All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20.
C) Control Station 71
C) Control Station 71 92+/-19 111+/-21 93+/-19 102+/-19 75+/-16 50+/-18 117+/-_22 162_+/-20 79_+/-14 74+/-22 112+/-20 101 +/-23 178 +/-28 107 +/-23
<14 79_+/-19 153 +/-18 101 +/-23 165 +/-25 124+/-_16 110+/-_21 176+/- 24 138_+/-20 164+/-32 144+/--29 91 +/-79


TABLE C-16 2001 CONCENTRATIONS OF TRITIUM IN QUARTERLY COMPOSITES OF SURFACE WATER Results in Units of pCi/L +/- 2 sigma STA TIO N ID ----------------------------------       >
TABLE C-16 2001 CONCENTRATIONS OF TRITIUM IN QUARTERLY COMPOSITES OF SURFACE WATER Results in Units of pCi/L +/- 2 sigma STA TIO N ID ----------------------------------
SAMPLING     SA-SWA-1 1A1         SA-SWA-12C1           SA-SWA-16F1             SA-SWA-1F2             SA-SWA-7E1               AVERAGE PERIOD                               (Control) 01 /08/2001 to         < 150                 < 160                   < 160               < 160                   < 150 03/08/2001 04/06/2001 to           < 160                 < 160                 < 160                 < 160                   -<150 06/06/2001 07/03/2001 to           < 190                 < 170                 < 170                 < 170                   <170 09/03/2001 10/03/2001 to           <150                   < 160                 < 160                 < 160                   < 160 12/10/2001
SAMPLING SA-SWA-1 1A1 SA-SWA-12C1 SA-SWA-16F1 SA-SWA-1F2 SA-SWA-7E1 AVERAGE PERIOD (Control) 01 /08/2001 to  
< 150  
< 160  
< 160  
< 160  
< 150 03/08/2001 04/06/2001 to  
< 160  
< 160  
< 160  
< 160  
-<150 06/06/2001 07/03/2001 to  
< 190  
< 170  
< 170  
< 170  
<170 09/03/2001 10/03/2001 to  
<150  
< 160  
< 160  
< 160  
< 160 12/10/2001


TABLE C- 17 2001 CONCENTRATIONS OF STRONTIUM-89, STRONTIUM-90*
TABLE C-17 2001 CONCENTRATIONS OF STRONTIUM-89, STRONTIUM-90*
AND GAMMA EMITTERS** IN EDIBLE FISH Results in Units of pCi/kg (wet) +/- 2 sigma (Strontium in bone is reported in pCi/kg (dry))
AND GAMMA EMITTERS** IN EDIBLE FISH Results in Units of pCi/kg (wet) +/- 2 sigma (Strontium in bone is reported in pCi/kg (dry))
STRONTIUM                 GAMMA EMITTERS BONE ------- >              (FLESH)
STRONTIUM GAMMA EMITTERS BONE -------
SAMPLING STATION ID             PERIOD             Sr-89           Sr-90                 K-40 SA-ESF-7E1                   5/14-16/2001                                               3390+/- 220 SA-ESF-11 A1                5/14-16/2001           < 600         <130               3240+/-190 SA-ESF-1 2C1 (C)             5/14-16/2001                                             3700+/-180 AVERAGE                                                                                3440+/-470 SA-ESF-7E1                  9/12-13/2001             *
(FLESH)
* 3580+/-210 SA-ESF- 11 Al                9/12-13/2001            *
SAMPLING STATION ID PERIOD Sr-89 Sr-90 K-40 SA-ESF-7E1 SA-ESF-11 A1 SA-ESF-1 2C1 (C) 5/14-16/2001 5/14-16/2001 5/14-16/2001
* 3910+/-100 SA-ESF-12C1 (C)              9/12-13/2001            *
< 600
* 3650+/-190 AVERAGE                                                                                3710+/- 350 GRAND AVERAGE                                                                          '3580+/-470
<130 AVERAGE SA-ESF-7E1 SA-ESF-11 Al SA-ESF-12C1 (C) 9/12-13/2001 9/12-13/2001 9/12-13/2001 AVERAGE GRAND AVERAGE 3390+/- 220 3240+/-190 3700+/-180 3440+/-470 3580+/-210 3910+/-100 3650+/-190 3710+/- 350  
'3580+/-470
* Strontium results for one location for the first semi annual collection are analyzed and reported by Duke Engineering & Services Environmental Laboratory as MDC.
* Strontium results for one location for the first semi annual collection are analyzed and reported by Duke Engineering & Services Environmental Laboratory as MDC.
This is done as a management audit sample.
This is done as a management audit sample.  
** All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20 (C) Control Station 73
** All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20 (C) Control Station 73


                                                                                  . - -&#xfd; I I TABLE C-18 2001 CONCENTRATIONS OF GAMMA EMITTERS* IN CRABS Results in Units of pCi/kg (wet) +1-2 sigma GAMMA EMITTER "SAMPLING                     (FLESH)
TABLE C-18 2001 CONCENTRATIONS OF GAMMA EMITTERS* IN CRABS Results in Units of pCi/kg (wet) +1-2 sigma GAMMA EMITTER "SAMPLING (FLESH)
STATION ID                     PERIOD                       K-40 SA-ECH-1 1 A1                       07/16-19/2001                  2910+/-190 SA-ECH-12C1 (C)                     07/16-19/2001,                3080+/-200 AVERAGE                                                             3000+/-240 SA-ECH-1 1A1                         09/11-13/2001                  2510+/- 220 SA-ECH-12C1 (C)                     09/11-13/2001                 2660+/-160 AVERAGE                                                             2590+/-210 GRAND AVERAGE                                                       2790 +/- 510
STATION ID PERIOD K-40 SA-ECH-1 1 A1 SA-ECH-12C1 (C) 07/16-19/2001 07/16-19/2001, AVERAGE SA-ECH-1 1A1 SA-ECH-12C1 (C) 09/11-13/2001 09/11-13/2001 AVERAGE 2590+/-210 GRAND AVERAGE 2790 +/- 510
* All other gamnma emitters searched for were < LLD; Typical- LLDs are given in Table C-20.
* All other gamnma emitters searched for were < LLD; Typical-LLDs are given in Table C-20.
(C) Control Station 74
(C) Control Station 74 2910+/-190 3080+/-200 3000+/-240 2510+/- 220 2660+/-160
-&#xfd; I I


TABLE C-19 2001 CONCENTRATIONS OF GAMMA EMITTERS* IN SEDIMENT Results in Units of pCi/kg (dry) +/- 2 sigma SAMPLING               < -------------------------------------    GAMMA EMITTERS ------------------------------------- >
TABLE C-19 2001 CONCENTRATIONS OF GAMMA EMITTERS* IN SEDIMENT Results in Units of pCi/kg (dry) +/- 2 sigma SAMPLING GAMMA EMITTERS STATION ID DATE Be-7 K-40 Co-60 Cs-134 Cs-1 37 RA NAT Th-232 SA-ESS-6S2 SA-ESS-11A1 SA-ESS-15A1 SA-ESS-16A1 SA-ESS-1 2C1 (C)
STATION ID         DATE         Be-7               K-40                     Co-60     Cs-134   Cs-1 37             RA NAT               Th-232 SA-ESS-6S2         07/02/2001     <110            1020 +/- 140                      <2        <2.2    <4.1                98+/-9.2                82 +/- 20 SA-ESS-11A1        06/27/2001   870 +/- 150       15600+/-400                        <8      19 +/-6.9  72+/-11              630+/-17                840 +/- 49 SA-ESS-15A1        06/27/2001      < 250          9310 +/- 300                     <10        <4.9    44+/-11              530 +/- 20            660 +/-49 SA-ESS-16A1        06/27/2001    220 +/- 100        15100+/-410                        <10        <5.9    120+/-16              620+/-23              990 +/- 60 SA-ESS- 1 2C1 (C)   06/27/2001       <78          15600 +/- 440                      <11        <4.8    <7.6              550+/- 19              480 +/- 89 SA-ESS-7E1          06/27/2001       <80          12600 +/- 330                      <9      27+/- 8.2    <23              760+/-19              840 +/- 60 SA-ESS-16F1        06/27/2001   820 +/- 120       15100 +/- 350                     <20        <6.8    46 +/- 9.6            570+/-1,6              860 +/-49 AVERAGE                                -        12000+/-10700                                          45+/-81              540+/-420              780+/-360 SA-ESS-6S2          10/22/2001      <40            1570+/- 94                      <2.8       <1.8     <3.7                96 +/- 6.8            92+/-18 SA-ESS- 11 A1      10/10/2001      <76          13800 +/- 350                      <22        <5.7   50+/-14               660+/- 19            S790 +/-41 SA-ESS-1 5A1        10/10/2001    370 +/- 120        11200+/-410                        <11        <6.4    38+/-12              580+/-20               750::+/- 58 SA-ESS-16A1        10/10/2001    480+/-160          15900+/-430                        <15        <5.4    76 +/-16              630+/-26              -880+/-.54 SA-ESS-1 2C1 (C)    10/10/2001    350 +/- 63        15600 +/- 220                      <11        <7.2    58+/-9.2              820 +/- 13            1100: 30 SA-ESS-7E1          10/10/2001      <55          12000 +/- 290                      <13        <3.9   19+/-7.1             570+/-14              620 +/-:37 SA-ESS-16F1        10/10/2001      <79          15400 +/- 470                      <14        <6.4    67+/- 21              660 +/- 32            1130+/-72 AVERAGE                                          12200 +/-10100                                          45+/-52            -570+/-450              880+/-400 GRAND AVERAGE                                    12100 +/-10000                                          45 +/- 66            560+/-420              830+/-380
SA-ESS-7E1 SA-ESS-16F1 07/02/2001 06/27/2001 06/27/2001 06/27/2001 06/27/2001 06/27/2001 06/27/2001
* All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20 (C) Control Station
<110 870 +/- 150  
< 250 220 +/- 100
<78
<80 820 +/- 120 1020 +/- 140 15600+/-400 9310 +/- 300 15100+/-410 15600 +/- 440 12600 +/- 330 15100 +/- 350 12000+/-10700 45+/-81 540+/-420 780+/-360 SA-ESS-6S2 SA-ESS-11 A1 SA-ESS-1 5A1 SA-ESS-16A1 SA-ESS-1 2C1 (C)
SA-ESS-7E1 SA-ESS-16F1 AVERAGE 10/22/2001 10/10/2001 10/10/2001 10/10/2001 10/10/2001 10/10/2001 10/10/2001
<40
<76 370 +/- 120 480+/-160 350 +/- 63
<55
<79 1570+/- 94 13800 +/- 350 11200+/-410 15900+/-430 15600 +/- 220 12000 +/- 290 15400 +/- 470
<2.8  
<22
<11
<15
<11
<13
<14
<1.8  
<5.7
<6.4
<5.4
<7.2
<3.9
<6.4 12200 +/-10100 12100 +/-10000 GRAND AVERAGE
<3.7 50+/-14 38+/-12 76 +/-16 58+/-9.2 19+/-7.1 67+/- 21 96 +/- 6.8 660+/- 19 580+/-20 630+/-26 820 +/- 13 570+/-14 660 +/- 32 45+/-52
-570+/-450 92+/-18 S790 +/-41 750::+/- 58
-880+/-.54 1100: 30 620 +/-:37 1130+/-72 880+/-400 45 +/- 66 560+/-420 830+/-380
* All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20 (C) Control Station AVERAGE
<2
<8
<10  
<10  
<11
<9
<20
<2.2 19 +/-6.9
<4.9
<5.9  
<4.8 27+/- 8.2
<6.8
<4.1 72+/-11 44+/-11 120+/-16
<7.6
<23 46 +/- 9.6 98+/-9.2 630+/-17 530 +/- 20 620+/-23 550+/- 19 760+/-19 570+/-1,6 82 +/- 20 840 +/- 49 660 +/-49 990 +/- 60 480 +/- 89 840 +/- 60 860 +/-49


TABLE     C-20 2001 MAPLXWOOD TESTING SERVICES LLDs, FOR GAMMO. "SPECTROMETRY SAMPLE TYPE:   < ----------
TABLE C-20 2001 MAPLXWOOD TESTING SERVICES LLDs, FOR GAMMO.  
AIR I R-             >                WATER ----------   > <----     MILK-......... >
"SPECTROMETRY SAMPLE TYPE:  
IODINE                       PARTICULATES     GAMMA SCAN           IODINE       GAMMA SCAN       IODINE 3                  3 ACTIVITY:       10-3 pCi/m                  10-3 pCi/m        pCi   -                pCi/L   pCi/L           pCi/L GEOMETRY:       47 ML                       13 FILTERS       3.5 LITER             100 ML     3.5 LITER       100 ML COUNT TIME:     120 MINS                       500 MINS       1000 MIN           1000 MINS     500 MINS     1000 MINS DELAY TO COUNT:   2 DAYS                       5 DAYS         .7 DAYS-               3 DAYS   2 DAYS         2 DAYS NUCLIDES BE-7                                               7.2             7.8             -                  18 NA-22               -                              1.2                 8           -                6.7 K-40               -                              7.0                 30           -                  50 CR-51               -                              1.8             9.1             -                  14 MN-54               -                              0.22             1.2             -                3.6 CO-58               -                              0.30             1.3             -                2.8 FE-59               -                              0.80           1.6                             10.3 CO-60               -                              0.39           1.3                               5.6 ZN-65               -                              0.70           2.1                                 12 ZRNB-95             -                              0.57           2.0             -                4.5 MO-99               -                                27               60           -                  27 RU-103             -                              0.30           1.2             -                1.9 RU- 106             -                              3.0             9.5             -                  18 AG-II1M             -                              0.45           2.3             -                  3.3 SB-125             -                              0.66           2.7             -                  5.1 TE-129M           -                              8.0               47           -                    81 1-131.           9.5                               0.52           2.5           0.3                 2.0       0.4 TE-132             -                              0.6             4.3             -                  1.7 BA-133             -                              0.29             1.6             -                  1.8 CS-134             -                              0.34             1.3             -                  1.6 CS-136             -                              0.54             1.9             -                  3.0 CS-137             -                              0.44             2.4             -                  3.7 BALA-140                                         1.3             3.8             -                  7.5 CE-141             -                              0.25             1.3             -                  2.5 CE-144             -                              0.65             7.5             -                  9.8 RA-NAT             -                              0.57             2.9             -                  5.4 TH-232                                           55.0               11           -                  37         -
< ---------- AIR
76
------------------ I R-WATER ----------
MILK-......... >
IODINE PARTICULATES GAMMA SCAN IODINE GAMMA SCAN IODINE ACTIVITY:
10-3 pCi/m3 10-3 pCi/m3 pCi pCi/L pCi/L pCi/L GEOMETRY:
47 ML 13 FILTERS 3.5 LITER 100 ML 3.5 LITER 100 ML COUNT TIME:
120 MINS 500 MINS 1000 MIN 1000 MINS 500 MINS 1000 MINS DELAY TO COUNT:
2 DAYS 5 DAYS  
.7 DAYS-3 DAYS 2 DAYS 2 DAYS NUCLIDES BE-7 7.2 7.8 18 NA-22 1.2 8
6.7 K-40 7.0 30 50 CR-51 1.8 9.1 14 MN-54 0.22 1.2 3.6 CO-58 0.30 1.3 2.8 FE-59 0.80 1.6 10.3 CO-60 0.39 1.3 5.6 ZN-65 0.70 2.1 12 ZRNB-95 0.57 2.0 4.5 MO-99 27 60 27 RU-103 0.30 1.2 1.9 RU-106 3.0 9.5 18 AG-II1M 0.45 2.3 3.3 SB-125 0.66 2.7 5.1 TE-129M 8.0 47 81 1-131.
9.5 0.52 2.5 0.3 2.0 0.4 TE-132 0.6 4.3 1.7 BA-133 0.29 1.6 1.8 CS-134 0.34 1.3 1.6 CS-136 0.54 1.9 3.0 CS-137 0.44 2.4 3.7 BALA-140 1.3 3.8 7.5 CE-141 0.25 1.3 2.5 CE-144 0.65 7.5 9.8 RA-NAT 0.57 2.9 5.4 TH-232 5 5.0 11 37 76


TABLE C-2 0   (-Cont ' d) 2001 MAPLEWOOD ' TEETIN       'SERVICES L.LDe FOR GOAMA;,S3PECTROMETRY SAMPLE TYPE:   FOOD PRODUCTS     VEGETATION       GAME         FISH & SHELLFISH SEDIMENT & SOIL ACTIVITY:         pCi/kg WET     pCi/kg WET   pCi/kg WET         pCi/kg WET       pCi/kg DRY GEOMETRY:           500 ml         3.5 LITER     500 ml             500 ml           500 ml COUNT TIME:       500 MINS         500 MINS     500 MINS           500 MINS         500 MINS DELAY TO COUNT:     3 DAYS           7 DAYS       5 DAYS             5 DAYS           30 DAYS NUCLIDES BE-7                   50                35            32                  82                80 NA-22                   13                13        14.4                    12                14 K-40                   70                70            70                  70              70 CR-51                   32                28            28                  32              127 MN-54                   10              6.0          5.8                  5.0              30 CO-58                 6.6              5.0          5.0                  6.0              19 FE-59                   27              16        14  .1                10              49 CO-60               17.5              7.8          5.5                    12              22 ZN-65                   17                13        12.0                    10              22 ZRNB-95                 11            11.0          8.0                  8.1              34 MO-99                 104                49            20              272          166000 RU-103               5.2              5.0          3.2                5.5                14 RU-106               114                36            35                  36                81 AG-IlOM                 14              7.0          7.5                8.9                39 SB-125                 11              9.9            II                6.4                29 TE-129M               225              286          157                207                470 1-131                 5.8               4.0          6.2                6.4              108 TE-132                7.0               3.9          9.0                 5.1              5600 BA-133                5.4              4.0           3.7                6.4                12 CS-134                4.9              4.2           4.2                 6.4               27 CS-136                8.6               4.2           6.1                 6.1                 70 CS-137                9.1              7.9          6.1                7.2                33 BALA-140                26            12.6             20              13.4                143 CE-141                6.1               5.0          5.0                4.4                 21 CE-144                  20                16      19.6               14.0                  5o RA-NAT                  15                14         8.0                 8.2                 45 TH-232                  34                35      40.0                    41                50 77
TABLE C-2 0 (-Cont ' d) 2001 MAPLEWOOD ' TEETIN  
'SERVICES L.LDe FOR GOAMA;,S3PECTROMETRY SAMPLE TYPE:
FOOD PRODUCTS VEGETATION GAME FISH & SHELLFISH SEDIMENT & SOIL ACTIVITY:
pCi/kg WET pCi/kg WET pCi/kg WET pCi/kg WET pCi/kg DRY GEOMETRY:
500 ml 3.5 LITER 500 ml 500 ml 500 ml COUNT TIME:
500 MINS 500 MINS 500 MINS 500 MINS 500 MINS DELAY TO COUNT:
3 DAYS 7 DAYS 5 DAYS 5 DAYS 30 DAYS NUCLIDES 50 13 70 32 10 6.6 27 17.5 17 11 104 5.2 114 BE-7 NA-22 K-40 CR-51 MN-54 CO-58 FE-59 CO-60 ZN-65 ZRNB-95 MO-99 RU-103 RU-106 AG-IlOM SB-125 TE-129M 1-131 TE-132 BA-133 CS-134 CS-136 CS-137 BALA-140 CE-141 CE-144 RA-NAT TH-232 14 11 225 5.8 7.0 5.4 4.9 8.6 9.1 26 6.1 20 15 34 35 13 70 28 6.0 5.0 16 7.8 13 11.0 49 5.0 36 7.0 9.9 286 4.0 3.9 4.0 4.2 4.2 7.9 12.6 5.0 16 14 35 32 14.4 70 28 5.8 5.0 14.1 5.5 12.0 8.0 20 3.2 35 7.5 II 157 6.2 9.0 3.7 4.2 6.1 6.1 20 5.0 19.6 8.0 40.0 82 12 70 32 5.0 6.0 10 12 10 8.1 272 5.5 36 8.9 6.4 207 6.4 5.1 6.4 6.4 6.1 7.2 13.4 4.4 14.0 8.2 41 80 14 70 127 30 19 49 22 22 34 166000 14 81 39 29 470 108 5600 12 27 70 33 143 21 5o 45 50 77


APPENDIX D
APPENDIX D
Line 683: Line 2,067:
OF RESULTS FROM ANALYTICS AND ENVIRONMENTAL RESOURCE ASSOCIATES INTERLABORATORY COMPARISON PROGRAMS 79
OF RESULTS FROM ANALYTICS AND ENVIRONMENTAL RESOURCE ASSOCIATES INTERLABORATORY COMPARISON PROGRAMS 79


APPENDIX D
APPENDIX D  


==SUMMARY==
==SUMMARY==
OF RESULTS FOR ANALYTICS AND ENVIRONMENTAL RESOURCE ASSOCIATES INTERLABORATORY COMPARISON PROGRAM Appendix D presents a summary of the analytical results                 for the 2001 Analytics and Environmental Resource Associates               (ERA)
OF RESULTS FOR ANALYTICS AND ENVIRONMENTAL RESOURCE ASSOCIATES INTERLABORATORY COMPARISON PROGRAM Appendix D presents a summary of the analytical results for the 2001 Analytics and Environmental Resource Associates (ERA)
Interlaboratory Comparison Program.
Interlaboratory Comparison Program.
TABLE OF CONTENTS TABLE NO.                       TABLE DESCRIPTION                                  PAGE D-1     Gross Alpha and Gross Beta Emitters in             Water ....         82 D-2      Gamma Emitters in Water and Milk .................                   83 D-3      Gamma Emitters in Air and Soil ...................                   84 D-4      Tritium Analysis in Water and Iodine in Air ......                   85 81
TABLE OF CONTENTS TABLE NO.
D-1 D-2 D-3 D-4 TABLE DESCRIPTION Gross Alpha and Gross Beta Emitters in Water....
Gamma Emitters in Water and Milk.................
Gamma Emitters in Air and Soil...................
Tritium Analysis in Water and Iodine in Air......
PAGE 82 83 84 85 81


TABLE D-1 RESULTS FOR ANALYTICS AND ERA INTERLABORATORY COMPARISON PROGRAM Gross Alpha and Gross Beta Emitters In   Water (pCi/L)
TABLE D-1 RESULTS FOR ANALYTICS AND ERA INTERLABORATORY COMPARISON PROGRAM Gross Alpha and Gross Beta Emitters In Water (pCi/L)
ANALYTICS/ERA Acceptance ANALYTICS    Criteria DATE         PSEG                                PSEG            ERA    Lower & Upper MM-YY     SAMPLE CODE   MEDIUM     ANALYSIS Mean +/- s.d.         Known  Limit      Limit 06-2001  ANL-WAT-AB529    Water      Alpha        33+/-2           35      25            45 Beta        321+4           248    176          320 07-2001  ERA-WAT-AB528    Water      Alpha        29+/-1.2           18    9.3        26.7 Beta        60+/-2.9           53    35.7        70.3 12-2001  ANL-WAT-AB539    Water      Alpha      51+/-3             72      48            96 Beta      269+/-9             214     148         280
DATE MM-YY 06-2001 PSEG SAMPLE CODE ANL-WAT-AB529 07-2001 ERA-WAT-AB528 12-2001 ANL-WAT-AB539 MEDIUM Water Water Water ANALYSIS Alpha Beta Alpha Beta Alpha Beta PSEG Mean +/- s.d.
* s.d. -  one standard deviation of three individual analytical   results 83
33+/-2 321+4 29+/-1.2 60+/-2.9 51+/-3 269+/-9 ANALYTICS ERA Known 35 248 18 53 72 214 ANALYTICS/ERA Acceptance Criteria Lower & Upper Limit Limit 25 45 176 320 9.3 26.7 35.7 70.3 48 96 148 280
* s.d.
one standard deviation of three individual analytical results 83


TABLE D-2 RESULTS FOR ANALYTICS AND ERA INTERLABORATORY       COMPARISON PROGRAM Gamma Emitters In   Water and Milk   (pCi/L)
TABLE D-2 RESULTS FOR ANALYTICS AND ERA INTERLABORATORY COMPARISON PROGRAM Gamma Emitters In Water and Milk (pCi/L)
ANALYTICS/ERA Acceptance
ANALYTICS/ERA Acceptance ANALYTICS Criteria DATE PSEG PSEG ERA Lower & Upper MM-YY SAMPLE CODE MEDIUM ANALYSIS Mean +/- s.d.
* ANALYTICS         Criteria DATE           PSEG                                     PSEG           ERA       Lower & Upper MM-YY     SAMPLE CODE   MEDIUM   ANALYSIS       Mean +/- s.d.         Known     Limit         Limit 0J-0uul   ANL-WAT-G524   Water     Cr-51             270+19          242        170          314 Mn- 54             112+/-2          .101 71          131 Fe-59             100+2              84        60          108 Co-60             162+6          147        105          189 Zn-65             211+6            186        132          240 1-131             98+/-2              90        60          120 Cs-137             112+2            102          72          132 Ce-141             105+2              94        64          124 03-2001  ANL-MLK-G526  Milk      Cr-51             436+/-19           418      292            544 Mn-54              186+/-6           175      121          229 Fe-59              162+7           146      104            188 Co-60              256+7           254      176          332 Zn-65            346+/-10           322      226          418
Known Limit Limit 0J-0uul ANL-WAT-G524 Water 03-2001 ANL-MLK-G526 Milk 06-2001 ERA-WAT-G528 12-2001 ANL-WAT-G541 Water Water Cr-51 Mn-54 Fe-59 Co-60 Zn-65 1-131 Cs-137 Ce-141 Cr-51 Mn-54 Fe-59 Co-60 Zn-65  
                                  .1-131              79+5             77        53          101 Cs-134            195+/-6           223      157          289 Cs-137            181+1           176      63            230 Ce-141            165+/-3           162      114          210 06-2001  ERA-WAT-G528  Water    Ba-133            36+/-1.2           36      27.3          44.7 Co-60              48+/-1.5           47        38.3          55.7 Cs-134            16+/-0.6           16      7.3          24.7 Cs-137          203+/-1             197      160          214 Zn-65              37+/-1.5           36 27.3          44.7 12-2001  ANL-WAT-G541  Water    Cr-51              284+5           293        203          383 Mn-54                89+/-3             88        64          112 Fe-59                71+/-3             60        42            78 Co-60            2 06+/-6           209        149          269 Zn-65            127+14           122          86          158 1-131              97+5             93        63          123 Cs-134            101+/-7           117          81          153 Cs-137            196+/-6           188        134          242 Ce-141            227+8           224       158           290
.1-131 Cs-134 Cs-137 Ce-141 Ba-133 Co-60 Cs-134 Cs-137 Zn-65 Cr-51 Mn-54 Fe-59 Co-60 Zn-65 1-131 Cs-134 Cs-137 Ce-141 270+19 112+/-2 100+2 162+6 211+6 98+/-2 112+2 105+2 436+/-19 186+/-6 162+7 256+7 346+/-10 79+5 195+/-6 181+1 165+/-3 36+/-1.2 48+/-1.5 16+/-0.6 203+/-1 37+/-1.5 284+5 89+/-3 71+/-3 2 06+/-6 127+14 97+5 101+/-7 196+/-6 227+8 242
* s.d. - one standard deviation of three individual analytical       results 84
.101 84 147 186 90 102 94 418 175 146 254 322 77 223 176 162 36 47 16 197 36 293 88 60 209 122 93 117 188 224 170 71 60 105 132 60 72 64 292 121 104 176 226 53 157 63 114 27.3 38.3 7.3 160 27.3 203 64 42 149 86 63 81 134 158 314 131 108 189 240 120 132 124 544 229 188 332 418 101 289 230 210 44.7 55.7 24.7 214 44.7 383 112 78 269 158 123 153 242 290
* s.d. -
one standard deviation of three individual analytical results 84


TABLE D-3 RESULTS OF ANALYTICS AND ERA. INTERLA1ORATORY COMPARISON PROGRAM Gamma Emitters In-Soil-(pCi/Kg-dry) and Air Particulate Samples (pCi/m3 )
TABLE D-3 RESULTS OF ANALYTICS AND ERA. INTERLA1ORATORY COMPARISON PROGRAM Gamma Emitters In-Soil-(pCi/Kg-dry) and Air Particulate Samples (pCi/m3 )
ANALYTICS/ERA Acceptance
ANALYTICS/ERA Acceptance ANALYTICS Criteria DATE PSEG PSEG ERA Lower & Upper MM-YY SAMPLE CODE MEDIUM ANALYSIS Mean + s.d.
* ANALYTICS     Criteria DATE         PSEG                                 PSEG           ERA     Lower & Upper MM-YY     SAMPLE CODE   MEDIUM     ANALYSIS   Mean + s.d.       Known   Limit       Limit 03-2001 ANL-SOL-G525   Soil       Cr-51         470+24         479      335          623 Mn-54          208+/-9           201      141          261 Fe-59          180+/-4           167      119          215 Co-60          284+4           291      201          381 Zn-65          353+11         369      261          477 Cs-137        316+/-9           328      232          424 Ce-141        172+7           186      132          240 06-2001  ANL-APT-G531  APT        Cr-51          237+10         210    144          276 Mn-54          156+/-7           141      99          183 Co-60          132+4           127      91          163 Fe-59          99+6           82      58          106 Zn-65          193+10         170    116          224 Cs-134        108+3           125      89          161 Cs-137        128+4           114      78          150 Co-58          192+/-4           90      60          120 Ce-141        175+/-12         153    105          201 09-2001  ANL-SOL-G536  Soil      Cr-51          439+/-13         404      284          524 Mn-54        .237+4           226      160          292 Co-60          292+2           294      198          390 Fe-59          113+/-5           95        65        125 Zn-65          271+/-16         281      197          365 Cs-134        172+5           177      123          231 Cs-137        437+59         480      336          624 Ce-141        135+/-14         134       92         176
Known Limit Limit 03-2001 ANL-SOL-G525 06-2001 ANL-APT-G531 09-2001 ANL-SOL-G536 Soil APT Soil Cr-51 Mn-54 Fe-59 Co-60 Zn-65 Cs-137 Ce-141 Cr-51 Mn-54 Co-60 Fe-59 Zn-65 Cs-134 Cs-137 Co-58 Ce-141 Cr-51 Mn-54 Co-60 Fe-59 Zn-65 Cs-134 Cs-137 Ce-141 470+24 208+/-9 180+/-4 284+4 353+11 316+/-9 172+7 237+10 156+/-7 132+4 99+6 193+10 108+3 128+4 192+/-4 175+/-12 439+/-13  
* s.d. - one standard deviation of three individual analytical results 85
.237+4 292+2 113+/-5 271+/-16 172+5 437+59 135+/-14 479 201 167 291 369 328 186 210 141 127 82 170 125 114 90 153 404 226 294 95 281 177 480 134 335 141 119 201 261 232 132 144 99 91 58 116 89 78 60 105 284 160 198 65 197 123 336 92 623 261 215 381 477 424 240 276 183 163 106 224 161 150 120 201 524 292 390 125 365 231 624 176
* s.d.  
- one standard deviation of three individual analytical results 85


TABLE D-4 RESULTS OF ANALYTICS AND ERA INTERLABORATORY COMPARISON PROGRAM Tritium Analysis In Water (pCi/L)
TABLE D-4 RESULTS OF ANALYTICS AND ERA INTERLABORATORY COMPARISON PROGRAM Tritium Analysis In Water (pCi/L)
And Iodine In Air Samples (pCi/m3 )
And Iodine In Air Samples (pCi/m3 )
* AV...... P"*,     -A Acceptance ANALYTICS      Criteria DATE            PSEG                                PSEG          ERA    Lower & Upper MM-YY        SAMPLE CODE   MEDIUM    ANALYSIS  Mean +  s.d. Known    Limit        Limit 03-2001    ANL-WAT-H523*   Water    H-3.        3,145+/-~171'    3114        2178          4050 03-2001    ANL-AIO-I527   AIO       1-131          90+/-0            90        60          120 06-2001    ANL-AIO-I530    AIO       1-131          77+1            80        56          104 06-2001    ANL-WAT-H532    Water     H-3         7890+/-85        7494        5244          9744 09-2001    ANL-AIO-I535    AIO      1-131         64+4            68        50            86 08-2001    ERA-WAT-H534    Water    H-3         2719+/-36        2730        2113          3347 10-2001    ERA-WAT-1538    Water    1-131        6.6+0.4         7.7      -6.6          21.9 12 -2001  ANL-AIO-I540    AIO      1-131          96+5             92        62          122 12-2001    ANL-WAT-H542    Water    H-3        14950+417       14060       9842        18278
AV...... P"*,  
* s.d. - one standard deviation of three individual analytical results 86
-A Acceptance Criteria Lower & Upper Limit Limit 2178 4050 60 120 56 104 5244 9744 50 86 2113 3347
-6.6 21.9 62 122 9842 18278 PSEG SAMPLE CODE ANL-WAT-H523*
ANL-AIO-I527 ANL-AIO-I530 ANL-WAT-H532 ANL-AIO-I535 ERA-WAT-H534 ERA-WAT-1538 ANL-AIO-I540 ANL-WAT-H542 MEDIUM Water AIO AIO Water AIO Water Water AIO Water ANALYSIS H-3.
1-131 1-131 H-3 1-131 H-3 1-131 1-131 H-3 PSEG Mean +
s.d.
3,145+/-~171' 90+/-0 77+1 7890+/-85 64+4 2719+/-36 6.6+0.4 96+5 14950+417 ANALYTICS ERA Known 3114 90 80 7494 68 2730 7.7 92 14060
* s.d. -
one standard deviation of three individual analytical results 86 DATE MM-YY 03-2001 03-2001 06-2001 06-2001 09-2001 08-2001 10-2001 12 -2001 12-2001


APPENDIX E SYNOPSIS OF LAND USE CENSUS 87
APPENDIX E SYNOPSIS OF LAND USE CENSUS 87


APPENDIX E SYNOPSIS OF 2001 LAND USE CENSUS A land use census was conducted 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 50m2 (500ft 2 )
APPENDIX E SYNOPSIS OF 2001 LAND USE CENSUS A land use census was conducted to identify, within a distance of 8 km (5 miles),
producing broad leaf vegetation, in each of the 16 meteorological sectors.
the location of the nearest milk animal, the nearest residence, and the nearest garden of greater than 50m2 (500ft 2) producing broad leaf vegetation, in each of the 16 meteorological sectors.
Tabulated below are the results of these surveys:
Tabulated below are the results of these surveys:
Milk           Nearest        Vegetable Animal         Residence        Garden Meteorological    July, 2001       July, 2001      July, 2001 Sector        km (miles)     km (miles)       km (miles)
Meteorological Sector Milk Animal July, 2001 km (miles)
N                None           None             None NNE              None           None             None NE              None         6.4 (4.0)         None ENE              None          5.8 (3.6)         None E                None          5.4 (3.4)         None ESE              None            None            None SE              None            None            None SSE              None            None            None S                None           None             None SSW              None          5.5 (3.4)         None SW              None          6.9 (4.3)         None WSW              None          7.1 (4.4)         None W              7.8  (4.9)      6.5 (4.0)         None WNW              None          5.5 (3.4)         None NW              None          5.9 (3.7)         None NNW              None          6.8 (4.2)         None 89}}
Nearest Residence July, 2001 km (miles)
Vegetable Garden July, 2001 km (miles)
None None None None None None None None None None None None 7.8 (4.9)
None None None None None 6.4 (4.0) 5.8 (3.6) 5.4 (3.4)
None None None None 5.5 (3.4) 6.9 (4.3) 7.1 (4.4) 6.5 (4.0) 5.5 (3.4) 5.9 (3.7) 6.8 (4.2) 89 N
NNE NE ENE E
ESE SE SSE S
SSW SW WSW W
WNW NW NNW None None None None None None None None None None None None None None None None}}

Latest revision as of 18:31, 16 January 2025

2001 Annual Radiological Environmental Operating Report
ML021330145
Person / Time
Site: Salem, Hope Creek  PSEG icon.png
Issue date: 04/30/2002
From: Salamon G
Public Service Enterprise Group
To:
Document Control Desk, Office of Nuclear Reactor Regulation
References
LRN-02-0147
Download: ML021330145 (86)
v • d • e


Text

PSEG Nuclear LLC P.O. Box 236, Hancocks Bridge, New Jersey 08038-0236 APR 3 0 2002 0 PSEG Nuclear LLC LRN-02-0147 United States Nuclear Regulatory Commission Document Control Desk Washington, DC 20555 Gentlemen:

2001 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT SALEM AND HOPE CREEK GENERATING STATIONS DOCKET NOS. 50-272, 50-311 AND 50-354 As required by Section 6.9.1.7 of Appendix A to Facility Operating Licenses DPR-70 and DPR-75 for Salem Generating Station, Unit Nos. 1 and 2, and Section 6.9.1.6 of Appendix A to Facility Operating License NPF-57 for Hope Creek Generating Station, PSEG Nuclear hereby transmits one copy of the 2001 Annual Radiological Environmental Operating Report. This report summarizes the results of the radiological environmental surveillance program for 2001 in the vicinity of the Salem and Hope Creek Generating Stations. The result of this program for 2001 was specifically compared to the Tesult of the pre-operational program.

If you have any questions or comments on this transmittal, please contact Michael Mosier at (856) 339-5434 Sincerely, C

Gabor Salamon Nuclear Safety and Licensing Manager Attachment 95-2168 REV. 7/99

Document Control Desk 2

APR 0 ZOOZ LRN-02-0147 C

Mr. H. Miller, Administrator - Region I U. S. Nuclear Regulatory Commission 475 Allendale Road King of Prussia, PA 19406 USNRC Senior Resident Inspector - Salem (X24)

USNRC Senior Resident Inspector - Hope Creek (X24)

Mr. G. Wunder, Project Manager - Hope Creek U. S. Nuclear Regulatory Commission Mail Stop 8B3 Washington, DC 20555 Mr. R. Fretz, Project Manager - Salem U. S. Nuclear Regulatory Commission Mail Stop 08B1A Washington, DC 20555 Mr. K. Tosch, Manager IV Bureau of Nuclear Engineering 33 Arctic Parkway - CN415 Trenton, NJ 08625 Mr. K. Kille Delaware Emergency Management Agency 165 Brick Store Landing Road Smyrna, DE 19977

o PSEG R ADIOLOtGICAL LN v IK(NINTAJ MONITORiNGi PROGrAM For Salem Generating Station, Unit 1: Docket Neo. 50-1272 Salem Generating Station, U/nit 2: Do&ket N(. 50-311 Hope Creek Generating Station : Docket No. 50-3 54 2001 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT JANUARY 1 TO DECEMBER 31, 200 1 P.'eared b-/

PSEG MAP..-

',WOOD TESTINU S'7"VICES APRIL 2002

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM & HOPE CREEK GENERATING STATIONS 2001 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT JANUARY 1 TO DECEMBER 31, 2001

TABLE OF CONTENTS PAGE

SUMMARY

THE RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM...........

Objectives..............................................

Data Interpretation.........................

Quality Assurance Program...................

Results and Discussion.......................

Atmospheric.............................

Direct Radiation........................

Terrestrial.............................

Aquatic.................................

Conclusions.................................

REFERENCES......................................

APPENDIX A -

PROGRAM

SUMMARY

APPENDIX B -

SAMPLE DESIGNATION AND LOCATIONS...

APPENDIX C -

DATA TABLES....................................

5 5

6 6

7 8

13 17 29 31 39 47 APPENDIX D APPENDIX E -

SUMMARY

OF RESULTS FROM ANALYTICS & ENVIRONMENTAL RESOURCE ASSOCIATES INTERLABORATORY COMPARISON PROGRAMS 79 SYNOPSIS OF LAND USE CENSUS....................

87 i

1 3

4

°......

o......

°.....

LIST OF'TABLES TABLE NUMBER TABLE DESCRIPTION PAGE

1.

Salem and Hope Creek Generating Stations' Radiological Environmental Monitoring Program (Program Overview) 18 LIST OF FIGURES FIGURE NUMBER FIGURE DESCRIPTION PAGE

1.

Gross Beta Activity in Air Particulate 1980 through 2001 (Quarterly).

21

2.

Ambient Radiation - Off-site vs Control Station 1980 through 2001 (Quarterly)..,

..................... 22

3.

Iodine-131 Activity in Milk 1980 through 2001 (Quarterly)........................

23

4.

Gross Beta Activity in Surface Water 1980 through 2001 (Quarterly).........................

.24

5.

Tritium Activity in Surface Water 1980 through 2001 (Quarterly)..

25 6A.

Cesium-137 Activity in Aquatic Sediment 1980 through 2001 (Semi-Annual)...........................

26 6B.

Cobalt-60 Activity in Aquatic Sediment 1980 through 2001 (Semi-Annual).........................

27

7.

Cesium-137 Activity in Soil 1980 through 2001 (Every Three Years)...................

28 ii

SUTMMARY During normal operations of a nuclear power generating station there are releases of small amount-is 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 environment around Artificial Island where the Salem Generating Stations (SGS) and Hope Creek Generating Station (HCGS) are located.

The results of the REMP are published annually, providing a summary and interpretation of the data collected.

PSEG's Maplewood Testing Services (MTS) has been responsible for the collection and analysis of environmental samples during the period of January 1, 2001, through December 31, 2001, and the results are discussed in this report.

The REMP for SGS/HCGS was conducted in accordance with the SGS-and HCGS Technical Specifications/Offsite Dose Calculation Manual.

The Lower Limit of Detection (LLD) values required by.the Technical Specifications/ODCM were achieved for this reporting period.

The objectives of, the program were also met during this period.

The data collected assists in demonstrating that SGS and HCGS were operated in compliance with Technical Specifications/ODCM.

Most of the radioactive materials noted in this report are normally present in the environment, either naturally, such as potassium-40, or as a result of non-nuclear generating station activity, such as nuclear bomb testing.

Measurements made in the vicinity of SGS/HCGS were compared to background or control measurements and the preoperational REMP study performed before Salem Unit 1 became operational.

Samples of air particulates, air iodine, milk, surface, ground and drinking water, vegetables, game, fodder crops, fish, crabs, and sediment were collected and analyzed.

External radiation dose measurements were also made in the vicinity of SGS/HCGS using thermoluminescent dosimeters.

From the results obtained, it can be concluded that the levels and fluctuations of radioactivity in environmental samples were as expected for an estuarine environment.

No unusual radiological characteristics were observed in the environs of SGS/HCGS during this reporting period.

Since these results were comparable to the results obtained during the preoperational phase of the program, and with historical results collected since commercial operation, we can conclude that the operation of SGS and HCGS had no significant impact on the radiological characteristics of the environs of these stations.

To demonstrate compliance with Technical Specifications/ODCM (Sections 3/4.12.1 & 6.8.4.h -1,2,3),

samples were analyzed for one or more of the following: gamma emitting isotopes, tritium (H-3),

iodine-131 (1-131),

gross beta and gross alpha.

The results of these analyses were used to assess the environmental impact of SGS and HCGS operations, 1

thereby demonstrating compliance with 'technical Specifications/ODCM (Section 3/4.11) and applicable Federal and State regulations, and to verify the adequacy of radioactive effluent control systems.

The results provided in this report are summarized below:

M There were a total of 1397 analyses on 1121 environmental samples during 2001.

Direct radiation dose measurements were made using 196 thermoluminescent dosimeters (TLDs).

  • In addition to the detection of naturally-occurring isotopes (i.e.

Be-7, K-40, Ra-226 and Th-232) trace levels of Cs-134 and Cs-137 were also detected.

The concentrations of these nuclides were well below the Technical Specification reporting limit.

E Dose measurements made with quarterly TLDs at 31 offsite locations around the SGS/HCGS site, averaged 49 millirems for the year 2001.-

The average dose measurements at the control locations (background) was 54 millirems for the year.

This was comparable to the preoperational phase of the program which had an average of 55 millirems per year for 1973 to 1976.

2

THE RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Lower All6ways Creek Township, Salem County, New Jersey is the site of Salem (SGS)and Hope Creek (HCGS)' Generating Stations.

SGS consists of two operating pressurized water nuclear power reactors.

Salem Unit One has a net rating of; 1133 megawatt electric(MWe) cnd Salem Unit Two has a net rating of"1134 MWe.

The licensed core power for both units is 3459 megawatt thermal (MWt).

HCGS is a

boiling water nuclear power reactor, which has a net rating of 1091 MWe (3339 MWt)

SGS/HCGS 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 environment surrounding SGS/HCGS is characterized mainly by the Delaware River 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.

Most of the 'remaining land is used for agriculture [1,21.

More specific information on the demograp1-y, hydrology, meteorology, and land use of the area may be found in the Environmental Reports

[1,2],

Environmental Statements [3,4],

and the Updated Final Safety Analysis Reports for SGS and HCGS [5,6].

Since 1968, a radiological environmental monitoring program (REMP) has been conducted at the SGS/HCGS Site.

Starting in December, 1972, more extensive radiological monitoring programs were initiated.

The operational REMP was initiated in December,

1976, when Salem Unit 1 achieved criticality.

PSEG's Maplewood Testing Services (MTS) has been involved in the REMP since its inception.

MTS is responsible for the collection of all radiological environmental samples and, from 1973 through June, 1983, conducted a quality assurance program in which duplicates of a portion of those samples analyzed by the primary laboratory were also analyzed by MTS.

From January, 1973, through June, 1983, Radiation Management Corporation (RMC) had primary responsibility for the analysis of all samples under the SGS/HCGS REMP and annual reporting of results. RMC reports for the preoperational and operational phase of the program are referenced in this report [7-9].

On July 1, 1983, MTS assumed primary responsibility for the analysis of all samples (except TLDs) and the reporting of results.

Teledyne Brown Engineering Environmental Services (TBE),

assumed responsibility for third-party QA analyses and TLDs. An additional vendor, Controls for Environmental Pollution Inc.

(CEP),

was retained to provide third party QA analyses and certain non-routine analyses from May,

1988, until June 1, 1992.

Currently, Duke Engineering and Services Environmental Laboratory (DE&SEL) is the third party QA vendor and the laboratory which performs the TLD analyses.

MTS reports for the operational phase from 1983 to 2000 are referenced in this report

[10].

3

An overview of the 2001 Program is provided in Table 1.

Radioanalytical data from samples collected under this program were compared with results from the preoperational phase.

Differences between these periods were examined statistically to determine the effects of static'n operations.

This report presents the results from January 1 t ::ough December 31, 2001, for the SGS/HCGS REMP.

OBJECTIVES The objectives of the Operational REMP 'are:

0 To fulfill the requirements of the Radiological Surveillance sections of the Technical. Specifications/ODCM for SGS/HCGS.

N To determine whether any significant increase occurred in the concentration of radionuclides in critical pathways.

  • To determine if SGS or HCGS has caused an increase in the radioactive inventory of long-lived radionuclides.

"* To detect any change in ambient gamma radiation levels.

"* To verify that SGS and HCGS operations have no detrimental effects on the health and safety of the public or on the environment.

This report, as required by Section 6.9.1.7 of the Salem Technical Specifications/ODCM and Section 6.9.1.6 of the Hope Creek Technical Specifications/ODCM, summarizes the findings of the 2001 REMP. "

Results of the four-year preoperational program have been summarized for comparison with subsequent operational reports [8]

In order to meet the objectives., an operational REMP was developed.

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: (1),

established critical pathways for the transfer of radionuclides through the environment to man, and, (2),

experience gained during the preoperational phase.

Sampling locations were determined based on site meteorology,,

Delaware estuarine hydrology, local demography, and land uses.

Sampling locations were 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 distance.

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.

Appendix A describes and summarizes, in accordance with.Section 6.9.1.7 of the Salem TS and Section 6.9.1.6 of the Hope Creek TS, the operational program as performed in 2001.

4

Appendix B describes the coding system which identifies sample type and location.

Table B-l lists the sampling stations and the types of samples collected at each station.:: These sampling stations are indicated on Maps B-I and B-2.

DATA INTERPRETATION Results of analyses are grouped according to sample type and presented in Appendix C.

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 Regulatory Guide 4.8, LLD is the smallest concentration of radioactive material ýin a sample that will yield a net count (above system background) that will be detected with 95% probability, Vith ýonly 5% probability of falsely concluding that a blank observation represents a '"real signal".

LLD is normally calculated as 4.66 times the standard deviation of the background counting rate, or of the blank sample, count, as appropriate, divided by counting efficiency, sample size, 2.22 (dpm per picocurie),

the radiochemical yield when applicable, the radioactive decay constant and. the-elapsed time between sample collection and time of counting.

The Minimum Detectable Concentration (MDC) is defined as the. smallest concentration of radioactive material that can be dotected at a given confidence level.

The MDC differs from the LLD in that the MDC-takes into consideration the interference caused by the presence of other nuclides while the LLD does not-.

The grouped data were averaged and standard deviations calculated in accordance with Appendix B of Reference" 16.

Thus, the 2 sigma deviations of the averaged data represent sample and not analytical variability.

For reporting and calculation of averages, any result occurring at or below the LLD is considered to be at that level.

When a group of data-was composed of 50% or more LLD values, averages were not calculated.

Grab sampling is a useful and acceptable procedure for taking environmental samples of a medium in which the concentration of radionuclides is expected to vary slowly with time or where intermittent sampling is deemed sufficient to'establish the radiological characteristics of the medium.

This method, however, is only representative of *the sampled medium for that specific location and instant of time.

As a result, variation in the radionuclide concentrations of the samples will normally occur.

Since these variations wil'l tend to counterbalance one another, averages based upon repetitive grab samples is considered valid.

QUALITY ASSURANCE PROGRAM MTS has a quality assurance program designed to ensure confidence in the analytical program.

Approximately 20% of the total analytical effort is spent on quality control, including process quality 5

control, instrument quality control, interlaboratory cross-check analyses, and data review.

The quality of the results-obtained by MTS is ensured by the implementation of. the Quality Assurance Program as described in the Maplewood Testing Services Quality Assurance 'Plan [i1 and the Environmental and Chemical Division Procedures Manual.

The internal quality control activity of MTS includes the quality control of instrumentation, equipment and reagents; the use of reference standards in calibration, documentation of established procedures and computer programs, and analysis of duplicate and spiked samples.

The external quality control activity is implemented through participation in both the Analytics and the Environmental Resource Associates Interlaboratory Comparison Programs.

The result's of these Interlaboratory Comparison Programs are listed in Tables D-1 through D-4 in Appendix D.

RESULTS AND DISCUSSION The analytical results of the 2001 REMP samples are divided into categories based on exposure pathways: atmospheric, direct, terrestrial, and aquatic.

The analytical results for the 2001 REMP are summarized in Appendix A.

The data for individual samples are presented in Appendix C.

The data collected demonstrates that the SGS and HCGS REMP was conducted in compliance with the Technical Specifications/ODCM.

The REMP for the SGS/HCGS Site has historically included samples and analyses not specifically required by these Stations' Technical Specifications/ODCM.

MTS continues to collect and analyze some of these samples in order to maintain personnel proficiency in performing these non-routine analyses.

These analyses are referenced throughout the report as Management Audit samples.

The summary tables in this report include these additional samples and analyses.

ATMOSPHERIC Air particulates were collected on Schleicher-Schuell No.

25 glass fiber filters with low-volume air samplers.

Iodine was collected from the air by adsorption on triethylenediamine (TEDA-) impregnated charcoal cartridges connected in series after the air particulate filters.

Air sample volumes were measured with calibrated dry-gas meters and were corrected to standard temperature and pressure.

Air Particulates (Tables C-1, C-2)

Air particulate samples were collected weekly, at 6 locations.

Each of the 318 samples collected for the year were analyzed for gross beta.

Quarterly composites of the weekly samples from each station were analyzed for specific gamma emitters.

Total data recovery for the 6 sampling stations in 2001 was 99.91 percent.

6

0 Gross beta activity was detected in 265 of the indicator station samples at concentrations ranging from 8 x 10-3 to 44 x 10-3 pCi/m3 and in 53 of the control station samples from 11 x I0-3 to 44 x 10-3 pCi/mUh The averages for the indiqator and control station.samples were 231and 25 x i0o3 PCi/m3, respectively. - Theý maximum preoperational

.level detected was 920 x 10v pCi/m3, with an average of 74 x 10-3 pci/m3.

Results:from-1980 to current year are plotted on Figure 1 as quarterly-averages.

Included along with this plot, for purposes of comparison, is an inset depicting a continuation of this plot from the current year all the wayback to 1973-.

Gamma spectroscopy, performed on each of the 24 quarterly composite samples analyzed, Aindicated the presence of the naturally-occurring radionuclides Be-7 and K-40.

All other gamma emitters searched for were below the LLD.

O Beryllium-7, attributed to cosmic ray activity in the atmosphere, was detected in all 20 indicator station composites that were.analyzed, :at concentrations ranging from 36 x 10-3 to 78 x 10-pCi/mý, with an average of 56 x 10-3 pCi/m',.

It was detected in the 4 control station composites ranging from 33 x 10-3 to 66 x 10- 3 pCi/m3, with an average of 53 x 10-3 pCi/M3..

The maximum preoperational level detected was 330 x l:-3 pCi/rn3, with an average of 109 x 10-3 pCi/m 3.

o Potassium-40 activity was detected in 13 of the indicator station samples,:with-concentrations ranging from7 x 10-3 tC 14 x 10-3 pCi/m3, with an average of 10 x 10-3 pCi/m 3.

K-40 was also detected in 2 control station samples, with concentrations of 9 x 10; and 11 x i0-1 pCi/m 3.

No preoperational data is available for comparison.

Air Iodine (Table C-3)

Iodine in filtered air samples was collected weekly, at 6 locations.

Each of the 318 samples collected for the year was analyzed for I -131.

Iodine-131 was not detected in any of the weekly samples analyzed.

LLD sensitivities for all the stations,- both indicator and control, ranged from *1 x 10-3 to <i0 X 1i0-1 pCi/m3-.

The maximum preoperational level detected-was 42 x 10-3 pCi/m3.

DIRECT RADIATION Ambient radiation levels in, the environs: were-measured with energy compensated CaSO4 (TI) thermoluminescent dosimeters (TLDs) supplied and read by DE&SEL.

Packets containing TLD's for quarterly exposure were placed in the owner controlled area and around the Site at various distances.

7

Direct Radiation (Table C-4)

A total of 49 locations were monitored for direct radiation during 2001, including 12 on-site locations, -31 off-site locations within the 10 mile zone,, and 6 control locations beyond 10 miles.

Effort was made to locate TLD's at schools and population centers -in the area.

Five readings for each TLD (ie; 5 elements) at each location were taken in order to obtain a more statistically valid result.

For these measurements, the rad is considered equivalent to the rem, in accordance with 10CFR20.1004.

The average dose rate for the 31 quarterly off-site indicator TLDs was 4.1 millirads per standard month, and the average control rate was 4.5 millirads per standard month.

The preoperational average for the quarterly TLD readings was 4.4 millirads per standard month.

In Figure 2, the quarterly average radiation levels of the off-site indicator stations versus the control stations, are plotted for the period 1980 through 2001, with an inset graph depicting the current year back to 1973.

TERRESTRIAL Milk samples were taken semi-monthly when cows were on pasture and monthly when cows were not grazing on open pasture.

Animals are considered on pasture from April to November of each year.

Samples were collected in new polyethylene containers and transported in ice chests with no preservatives added.

A well water sample was collected monthly.

Separate. raw and treated potable water samples were composited daily at the City cf Salem water treatment plant.

All samples were collected in new polyethylene containers.

Locally grown vegetable and fodder crops were collected at the time of harvest.

Such samples were weighed and packed in plastic bags.

Game (muskrat) has been collected annually (time of year dependent on weather conditions, which affect pelt thickness). from local farms after being trapped, stripped of their pelts and gutted.

The carcasses were packed in plastic bags and kept chilled in ice chests during transport.

Milk (Table C-5)

Milk samples were collected at 4 local dairy farms (2 farms in NJ and 2 in Delaware).

Each sample was analyzed for 1-131 and gamma emitters.

N Iodine-131 was not detected in any of the 80 samples analyzed.

8

LLD sensitivities for both the indicator and the control station samples ranged from <0.1 to <0.4 pCi/L.

The maximum preoperational level detected was 65 pCi/L which occurred following a period of atmospheric nuclear weapons tests.

Results from 1980 to 2001 are plotted on Figure 3, with an inset graph depicting the current year back to 1973.,

U Gamma spectroscopy performed on each of the 80 samples indicated the presence of the naturally-occurring radionuclide K-40.

All other gamma emitters searched for were below the LLD.

0 Potassium-40 was detected in all 80 samples.

Concentrations for the 60 indicator station samples ranged from 1220 to 1460 pCi/L, with an average of 1350 pCi/L.

The 20 control station sample concentrations ranged from 1220 to 1390 pCi/L, with an average of 1310 *pCi/L.

The maximum preoperational level detected was 2000 pCi/L, with an average of 1437 pCi/L.

Well Water (Ground Water) (Tables C-6, C-7)

Although wells in the vicinity of SGS/HCGS are not directly affected by plant operations, water samples were collected monthly from one farm's well during January through December of the year.

Each sample was analyzed for gross alpha; gross beta, tritium, and gamma emitters.

N Gross alpha activity was detected in 9 of the well water samples at concentrations ranging. from 1.2 to 2.6 pCi/L and an average of 2.2 pCi/L.

The maximum preoperational level detected was 9.6 pCi/L,.

There was no preoperational average determined for this analysis...

Gross beta activity was detected in all 12 well water samples.

Concentrations for the samples ranged from 9.8 to 14 pCi/L, with an average of 12 pCi/L.

The 2001 gross beta results are comparable with the preoperational -results which ranged from

<2.1 to 38 pCi/L, with an average value of 9 pCi/L.

"[

Tritium activity was not detected in any of the well water samples.

The LLD, sensitivities, ranged from <-150 to <180 pCi/L.

The maximum preoperational level detected was 380.:pCi/L.

Gamma spectroscopy performed on each of the 12 well water samples indicated the presence of the naturally-occurring radionuclides K-40 and Radium.

All other gamma emitters searched for were below the LLD.

0 Radium was deteqted in all 12 of the well water samples at concentrations ranging from 90 to 193 pCi/L with an average of 146 pCi/L.

The maximum preoperational level detected was 2.0 pCi/L.

9

These values are similar to those found in the past 11 years.

However, as with-the 1989 through 2000 results, they are higher than those tfound in the preoperational program.

The results are most likely due to a procedural change for sample preparation.

The change results in less-removal of radon (and its daughter products) from the sample.

It is reasonable to conclude that values currently observed are typical for this region.,

o Potassium-40,was detected in 4 of the samples at concen trations ranging from 48 to 85 pCi/L and an average of 71 pCi/L.

The maximum preoperational level detected was 30 pCi/L.

Potable Water (Drinking Water) (Tables C-8, C-9)

Both raw and treated potable water samples were collected and composited by Salem water treatment plant personnel.

Each sample consisted of daily aliquots composited into a -imonthly sample.

The raw water source forthis plant is Laurel Lake. and adjacent wells.

Each of the 24 individual samples.was analyzed for gross alpha, gross beta, tritium, iodine-131 and gamma emitters.

  • ]

Gross alpha activity was detected in 10 raw water samples at concentrations of 0.6 to 1.4 pCi/L and in 7 treated water samples ranging from 0.8 to 1.6 pCi/L.

The averages for both raw and treated water samples was 0.9 pCi/L.

The maximum pre operational level detected was 2.7 pCi/L.

M Gross beta activity was:detected in all 24 samples at concentrations ranging from 2.7 to 4.7 pCi/L for both the raw and treated water.

The average concentration for both raw and treated was 3.4 pCi/L.

The maximum preoperational level detected was 9-.0 pCi/L, with an average of 4.2 pCi/L.

Tritium activity was not detected in any of the raw and treated water samples.

LLD sensitivities ranged from <150 to <180 pCi/L.

The maximum preoperational level detected was 350 pCi/L, with an average of 179 pCi/L.

Iodine-131 measurements to:a sensitivity of 1.0 pCi/L were performed.

Since the receiving water body (Delaware River) is brackish, the water is not used for human consumption.

Drinking water supplies are not affected by discharges from the site.

Iodine-131 measurements for all 24 samples were below the LLD sensitivities.

The LLD sensitivities ranged from <0.1 to <0.4 pCi/L.

Gamma spectroscopy performed on each of the 24 monthly water samples indicated the presence of the naturally-occurring radionuclides K-40 and Radium.

All other gamma emitters searched for were below the LLD.

10

o The radionuclide K-40 was detected in 11 of the raw and treated potable waters at concentrations ranging from 26 to 70 pCi/L.

The combined average ýfor both raw-and treated positive results was 44 pCi/L.

There was no preoperational Sdata available for comparison.

o Radium was detected iAn-one potable raw samples and in four of the treated samples at concentrations of 4 to 6.5 pCi/L.

LLD sensitivities for the remaining raw and treated waters

  • ranged from <1.6 to <3.5 pCi/L. The maximum preoperational level detected was 1.4 pCi/L.

The higher results in the two measurable samples are most likely due to the procedural change for sample preparation, as discussed in the Well Water section.

Vegetables (Table C-10)

Although vegetables-in the region are not irrigated with water into which liquid plant-effluents have been discharged, a-variety of food products grown in-the area for human consumption were sampled at 5 indicator stations (14 samples) and 5 control'stations (15 samples).

The vegetables collected as management audit samples were analyzed for gamma emitters and included asparagus, cabbage, sweet corn, peppers and tomatoes.

Gamma spectroscopy performed on each of the 29 samples indicated the presence of the naturally occurring radionuclides K-40 and Radium.

All other gamma emitters searched for were below the LLD.

Potassium-40 was detected in all 29 samples.

Concentrations for the 14 indicator station samples ranged from.1420 to 2570 pCi/kg wet and averaged 2090 pCi/kg-wet. :: Concentrations for the 15 control station samples ranged from 1230 to 2710 pCi/kg-wet, and averaged 2060 pCi/kg-wet.

The average concentration detected for all samples, both indicator and control, was 2070 pCi/kg-wet.

The maximum preoperational level detected was 4800 pCi/kg-wet, with an average of 2140 pCi/kg-wet.

Radium was detected in 1 indicator sample (tomato) at a concentration of 16 pCi/kg-wet.

It was not detected in any of the control station samples.

No preoperational data is available for comparison.

Game (Table. C-II)

Although not required by the SGS or HCGS Technical Specifications/ODCM, samples of muskrats, inhabiting the marshlands surrounding the site, are collected.

This game is consumed-by local residents.

The samples, when available, are collected from 2 locations once a year as management audit samples and analyzed for gamma emitters.

11

Gamma spectroscopy performed on the flesh indicated the presence of the naturally-occurring radionuclide K-40.

All other gamma emitters searched for were below the LLD.

Potassium-40 was detected. in the. indicator station sample at a concentration of 2600 pCi/kgwKet.-:and the control station sample at 2840 pCi/kg-wet.

The average. forboth muskrat samples was 2720 pCi/kg-wet.

The maximum preoperational level detected was 27000 pCi/kg-wet, with an average*Qof-4400 pCi/kg-wet.

Fodder Crops (Table C--12)

Although not required by the SGS or HCGS Technical Specifications/ODCM, six samples of crops normally used as cattle feed (silage and soybeans) were collected from three indicator stations (5 samples) and one control station. (1 sample).

It was determined that these products may be a significant element in the food-chain pathway.

Fodder crops are collected as management audit samples and analyzed for gamma emitters.

All of the locations from which samples were collected this year are milk sampling stations.

Gamma spectroscopy performed on each of the 6 samples indicated the presence of the naturally-occurring radionuclides Be-7, K-40 and Radium.

All other gamma emitters searched for were below the LLD.

Beryllium-7, attributed to cosmic ray activity in the atmosphere, was detected in the 3 indicator silage samples at concentrations of 210 to 670 pCi/kg-wet.

It was detected in the control station silage sample at 350 pCi/kg-wet.

The average for all the silage samples was 400 pCi/kg-wet.

The maximum preoperational level detected for silage was 4700 pCi/kg-wet, with an average of 2000 pCi/kg-wet.

Be-7 was not detected in either of the two indicator soybean samples.

LLD sensitivities for the soybean samples were

<30 and <40 pCi/kg-wet.

The maximum preoperational level detected for soybean samples was 9300 pCi/kg-dry.

-Potassium-40 was detected in all 6 samples.

Concentrations for the 5 indicator station samples ranged from 2560 to 16800 pCi/kg wet and for the 1 control station sample at 4380 pCi/kg-wet.

The average concentration detected for the silage samples (both indicator and control) was 3710 pCi/kg-wet.

Preoperational results averaged 7000 pci/kg-wet.

Results for the soybean samples (both indicator and control) averaged 15900 pCi/kg-wet which is comparable to preoperational studies when the average wet/dry factor of 1.2 is used.

Preoperational soybean results averaged 22000 pCi/kg-dry.

Soil (Table C-13)

Soil is sampled every three years at nine stations, including one control, and analyzed for gamma emitters.

Samples are collected at each station, in areas that have been relatively undisturbed since 12

the last collection, in order to determine any change in the radionuclide inventory of the area.

Gamma spectroscopy performed on each of the 9 samples indicated the presence of the naturally-occurring radionuclides Be-7, K-40, Radium and Th-232, in addition to low levels of the fission product`C.-137.

All other gamma emitters searched 'for were below the LLD' Beryllium-7, attributed to cosmic ray activity in the atmosphere, was detected in 3 of the indicator station samples at concentrations of 120 to 360 pCi/kg-dry and an average of 210 pCi/kg-dry. It was not detected in the control station sample.

The maximum preoperational level detected for soil samples was 21000 pCi/kg-dry.

Potassium-40 was detected in all 8 samples of the indicator station samples at. concentrations ranging from 4610 to 12900 pCi/kg-dry with an average of 885.0 pCi/kg-dry.

The control station sample was.8190 pCi/kg-dry.

The maximum preoperational level detected was.24000 pCi/kg-dry with an average of 10000 pCi/kg-dry.

Cesium-137 was detected in 7 of the indicator station samples ranging from 26 to 350 pCi/kg-dry:,-with an average of 210 pCi/kg dry.

The control station sample showed a concentration of 160 pCi/kg-dry.

The maximum preoperational level detected was 2800 pCi/kg-dry with an average of 800 pCi/kg-dry.

Results from 1974 to the current year are plotted on. FigUre 7.

Radium was detected in all 8 of the indicator stationt samples in concentrations of 260 to 970 pCi/kg-dry, with an average of 660 pCi/kg-dry.

The control station. samp-le showed a concentration of 700 pCi/kg-dry.

The maximum preoperational level detected was 1500 pCi/kg-dry with. an average-of 870 pCi/kg-dry.

Thorium-232 was detected in all 8 indicator station samples in ranges of 350 to 1200 pCi/kg-dry, and had an average of 790 pCi/kg-dry.

The-control station' sampleý showed a concentration of 850 pCi/kg-dry.

'The.

maximum preoperatiofial level detected was 1400 pCi/kg-dry with an average of 740 pCi/kg-dry.

AQUATIC All aquatic samples were. collected by Environmental Consulting Services, Inc.

Surface water samples were collected in new polyethylene containers that were rinsed twice with the sample medium prior to collection.

Edible fish and crabs are taken by net and then processed.

In processing, the flesh is separated from the bone and shell and placed in sealed polyethylene containers and frozen before being transported in-ice-chests.

13

Sediment samples were taken with a bottom grab sampler and frozen in sealed polyethylene containers before being transported in ice chests.

Surface Water (Tables C-14,-C-15, C-16)

Surface water samples were collected monthly at 4 indicator stations and 1 control station in the-Delaware estuary.

One location is at the outfall area (which is the area where liquid radioactive effluents from the Salem Station are allowed to be discharged into the Delaware River),

another is downstream from the outfall area, and another is directly west of the outfall area at the mouth of the Appoquinimink River.

Two upstream locations are in the Delaware River and at the mouth of the Chesapeake and Delaware Canal, the latter being sampledý when thel flow is from the Canal into the river.

Station 12C1, at the mouth of the Appoquinimink River, serves as the operational control.

All surface water samples were analyzed monthly for gross beta and gamma emitters.

Quarterly composites were analyzed for tritium.

0 Gross beta activity was detected in all 48 of the indicator station samples ranging from 4.7 to 224 pCi/L, with an average of 82 pCi/L.

Beta activity was detected in all 12 of the control station samples with concentrations ranging from 6.4 to 129 pCi/L, with an average of 71 pCi/L.

The maximum preoperational level detected was 110 pCi/L, with an average of 32 pCi/L.

Quarterly results for all locations are plotted on Figure 4, for the years 1980 to 2001, withý an inset graph depicting the current year back to 1973.

H Tritium activity was not detected in any of the indicator or Scontrol station composites.

LLD sensitivities for the station composites, both indicator and control, ranged from <150 to

<190 pCi/L.

The maximum preoperational level detected was 600 pCi/L, with an average of 210 pCi/L.

Positive results from 1980 to 2001 are plotted on Figure 5, with an inset graph depicting the current year back to 1973.

E Gamma spectroscopy performed on each of the 48 indicator station and 12 control station surface water samples indicated the presence of the naturally-occurring radionuclide K-40.

All other gamma emitters searched for were below the LLD.

Potassium-40 was detected in 45 samples from the indicator stations at concentrations ranging from 42 to 178 pCi/L and in 11 of the control station samples ranging from 38 to 165 pCi/L.

The average for the indicator station locations was 95 pCi/L, while the average for the control station locations was 99 pCi/L.

The maximum preoperational level detected was 200 pCi/L, with an average of 48 pCi/L.

14

Fish (Table C-17)

Edible species of fish were collected semi-annually at 3 locations and analyzed for gamma emitters (flesh), and for Sr-89 and Sr-90 (bones) in one location (1AI).

This location was chosen since it is the outfall area for the Salem Station.

Samples included catfish, weakfish, white perch and striped bass.

Gamma spectroscopy performed an each of the 4 indicator station samples and 2 control station samples indicated the presence of the naturally-occurring radionuclide K-40. All other gamma emitters searched for were below the LLD.

o Potassium-40 was detected in all 4 samples from the indicator stations at concentrations ranging from 3240 to 3910 pCi/kg-wet for an average of 3500 pCi/kg-wet.

K-40 was detected in, both samples from the control location at 3650 and 3700 pCi/kg-wet.

The average for the. control samples, was 3675 pCi/kg-wet.

The maximum preoperational level detected was 13000 pCi/kg-wet, with an average of 2900 pCi/kg-wet.

Strontium-89 and strontium-90 analyses were performed by DE&SLL oz one sample of the first semi-annual sample collection (location IIAl),

and reported as MDC.

These are management audit analyses which are performed in recognition of the high bioaccumulation factor of strontium in bone.

o Strontium-89 was not detected.in the bone sample.

The MDC value for the-sample was <600 pCi/kg-dry. The maximum preoperational level detected was 100 pCi/kg-dry.

o Strontium-90 was not detected in-the bone sample.

The MDC value for the sample was <130 :pCi/kg-dry. The maximum preoperational level detected was 940.pCi/kg-dry, with an average of 335 pCi/kg-dry..

Blue Crab (Table C-18)

Blue crab samples were collected semi-annually at 2 locations, 1 indicator and 1 control, arid the edible portions were analyzed for gamma emitters.

Gamma spectroscopy performed on the flesh of each of the 2 indicator station samples and 2 control station samples indicated the presence of the naturally-occurring radionuclide K-40.

All other gamma emitters searched for were below the LLD.

Potassium-40 was detected in both indicator station samples at concentrations of 2510 and 2910 pCi/kg-wet and in both ofý the control station samples at 2660 and 3080 pCi/kg-wet.

The average for both the indicator and control station samples was 2790 pCi/kg-wet.

The maximum preoperational level detected was 12000 pCi/kg-wet, with an average of 2835 pCi/kg-wet.

15

Sediment (Table C-19)

Sediment samples were collected semi-annually from 7 locations, 6 indicator stations and 1 control.station.

Each of the 14 samples was analyzed for gamma emitters.. Although trace levels of man-made nuclides were detected in some sediment.samples, these levels were expected and well within the-acceptable levels specified-in section 3/4.12.1 of the Technical Specifications/ODCM.

Gamma spectroscopy was performed on each of the 12 indicator station samples and 2 control station samples.

In addition to the detection of the naturally-occurring radionuclides Radium, K-40, Be-7 and Th-232, low levels

'f Cs-134 and Cs-137 were also detected.

All other gamma emitters searched for were below the LLD.

Cesium-134 was detected in 2 of the 12 indicator station samples at concentrations of 19 and 27 pCi/kg-dry.

It was not detected in either control station samples.

LLD sensitivities for the remaining station samples, both indicator and control ranged from

<2.2 to <7.2 pCi/kg-dry.

No pre-operational data is available for comparison.

Cesium-137 was detected in 9 indicator station samples at concentrations ranging from 19 to 120 pCi/kg-dry and an average of 59 pCi/kg-dry.

It was detected in 1 control station sample at a concentration~of 58 pCi/kg-dry.

The maximum preoperational level detected was 400.1Ci/kg-dry with an average of 150 pCi/kg dry.

Results from 1980 to 2000 are plotted on Figure 6A, with an inset graph depicting the current year back to 1973.

Cobalt-60 was not detected in any of the sediment samples for the second year in a row.

LLD sensitivities for these 14 samples, indicator and control, ranged from <2 to <22 pCi/kg-dry.

Results of all the positive values from 1980 to 2001 are plotted on Figure 6B, with an inset graph depicting the current year back to 1973.

Potassium-40 was detected in all 12 indicator station samples at concentrations ranging from 1020 to 15900 pCi/kg-dry, with an average of 11550 pCi/kg-dry.

Concentrations detected in both of the control station samples were at 15600 pCi/kg-dry.

The average for both the indicator and control station samples was 12100 pCi/kg-dry. The maximum preoperational level detected was 21000 pCi/kg-dry, with an average of 15000 pCi/kg-dry.

Radium was detected in all 12 indicator station samples at con centrations ranging from 96 to 760 pCi/kg-dry, with an average of 530 pCi/kg-dry.

Concentrations detected in both of the control station samples were at 550 and 820 pCi/kg-dry, with an average of 690 pCi/kg-dry.

The grand average for both the indicator and control station samples was 560 pCi/kg-dry.

The maximum pre operational level detected was 1200 pCi/kg-dry, with an average of 760 pCi/kg-dry.

16

Thorium-232 was detected in all 12 indicator station samples at concentrations ranging from 82 to 1130 pCi/kg-dry, with an average of 710 pCi/kg-dry.

Concentrations detected in both Of the. control station samples were at 480 and II00 pCi/kg-dry, with an average of; 790 pCi/kg-dry... The grand average for both the indicator and control station samples was 830 pCi/kg-dry.

The maximum pre-operational level detected was 1300 pCi/kg-dry, with an average of 840 pCi/kg-dry..

Beryllium-7 was detected in 5 of the 12 indicator station samples at concentrations of 220 to 870 pCi/kg-dry, with an average of 550 pCi/kg-dry.

It was detected in 1 of the control station samples at a concentration of 350 pCi/kg-dry.

The LLD sensitivities for the remaining samples, both indicator and control, ranged from <40 to <250 pCi/kg-dry.

The maximum preoperational level detected was 2300 pCi/kg-dry.

CONCLUSIONS The Radiological Environmental Monitoring Program for Salem and Hope Creek Generating Stations was conducted-during 2001 in accordance with the SGS and HCGS-Technical Specifications/ODCM.

The LLD values required by the Technical Specifications/ODCM were achieved for this reporting period.,

The, objectives of the program were also met during this period.

The. data collected-.assists in demonstrating that SGS and--HCGS.were operated in coifpliance with Technical Specifications/ODCM.

From the results obtained, it can be.concluded that the levels and fluctuations of radioactivity in environmental samples were as expected for an estuarine environment-.:

No unusual radiological characteristics, were observed in the environs of SGS/HCGS-during this reporting period.

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, we can.'conclude that the operation of the Salem and Hope Creek Stations had no-significant impact on the radiological characteristics of. the environs of that area.

17

TABLE 1 SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (PROGRAM OVERVIEW)

STATION CODE COLLECTION MEDIUM INDICATOR CONTROL FREQUENCY TYPE/FREQUENCY* OF ANALYSIS I.

ATMOSPHERIC ENVIRONMENT

a. Air Particulate
b.

Air Iodine 5SI SDI 16El IF1 2F6 5S1 5DI 16EI FI!

2F6 14G1 14G1 Weekly Weekly Gross beta/weekly Gamma scan/quarterly Iodine-131/weekly II.

DIRECT RADIATION

a.

Thermoluminescent Dosimeters I11 2S2 5S1 6S2 7S1 1051 4D2 lIE2 16F2 I1F3 2S4 5DI ODI 14D1 15SI 16E1 7F2 9E1 15D1 10F2 14F2 3SI 2E1 3El 13E1 16SI 5FI 11F1 2F5 12EI 12FI 15F3 4S1 IF1 2F2 2F6 4F2 6FI 13F4 3F2 3F3 13F2 3G1 IG3 1OGI 16G1 14GI 3H1 Quarterly Gamma dose/ quarterly III.

Terrestrial Environment 2F9 1IF3 14F4 3GI Monthly (when animals are on pasture)

Semi-monthly (when animals are on pasture)

Iodine-131/monthly Gamma scan/monthly Iodine-13 1/semi -monthly Gamma scan/semi-monthly P"

a.

Milk

TABLE 1 (cont'd)

SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (PROGRAM OVERVIEW)

STATION CODE INDICATOR CONTROL COLLECTION FREQUENCY TYPE/FREQUENCY* OF ANALYSIS

b. Well Water
c. Potable Water (Raw & Treated) 3E1 2F3 3E1 3F5 6F2
d. Vegetables Monthly Monthly (composited daily) 2F4 2F9 3F6 3F8 14F3 iG1 2G2 3H5 9G1 14G2 Annually (at harvest)

Gross alpha/monthly Gross beta/monthly Tritium/monthly Gamma scan/monthly Gross alpha/monthly Gross beta/monthly Tritium/monthly Gamma scan/monthly Iodine-131/monthly Gamma scan/on collection e, Game (Muskrat)

f.

Fodder Crops_

I!DI 3E1 2F9 11F3 14F4 3GI Annually Annually Gamma scan/on collectiOn Gamma scan/on collection Every 3 years Gamma scan/on collection MEDIUM

g.

Soil 6S2 10DI 16E1 2F7 2F9 5F1 11F3 14F4 3GI

TABLE 1 (cont'd)

SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (PROGRAM OVERVIEW)

STATION CODE COLLECTION MEDIUM INDICATOR CONTROL FREQUENCY TYPE/FREQUENCY* OF ANALYSIS IV. AQUATIC ENVIRONMENT

a. Surface Water
b. Edible Fish
c. Blue Crabs
d. Sediment IIAl 7E1 IF2 12CI 16F1 IIAl 7El IIAl 11AI 1hAl 15A1 16AI 12C1 12C1 6S2 16FI 7E1 12C1 Monthly Semi annually Semi annually Semi annually.

Gross beta/monthly Gamma scan/monthly Tritium/quarterly Sr-89 & Sr-90 (bones)/on 1 loc.**

Sr-89 & Sr-90 (flesh/on 1 loc.**

Gamma scan (flesh)/on collection Gamma scan (flesh)/on collection Gamma scan/on collection

  • Except for TLDs, the quarterly analysis is performed on a composite of individual samples collected during the quarter.
    • Management audit analyses, not required by Technical Specifications or by specific commitments to local officials.

0O

FIGURE 1 GROSS BETA IN AIR PARTICULATE 1980 TH4ROUGH 2001 Weapons Test 10-15-80 Chernobyl 04-26-86 Salem - 2 Criticality I

08-02-80 Hope Creek Criticality 06-28-86 1983 1985 1987 1989 "1991 1993 1995 1997 1999 2001 QUARTERLY AVERAGE 1000 100 C,

0 GROSS RTA IN AIR PARTICULATE 1973 THROUGH 2001 1~i 97979 l5, l997 O0 "1M 10-1 1981 i.

l I l I I I.

I I I I I I I I I I I

I I I I I I I I Il I I I 1 1 1 1 1 1

1.

I.

I I I I

I I I I a I I I I

I I I I I.

I

22 z

0 0

lz w

0 M

z LL 0

0 0

0 z

0, N

UJ w

t:

U) 0 00 LL z

0 m

P qjuow PIS/wom

FIGURE 3 IODINE - 131 ACTIVITY IN MILK 1980 THROUGH 2001 20 ODINE0.13i ACTVrrY IN MILK 1973 THROUGH 2001 Chernobyl

- 5.

04/26/86 0.00 10

-.00 001o 909 1905 199 1997 Weapons Test 1

I 10-15-80 I

  • Hope Creek Criticality 06-28-86 0

Salem-2 Criticality 08-02-80

-10 OII I I I

IS

,I II I

I

,I 0

IIIII I

1 11 1

1I I

I I I III I

IIIIIII II I

1981 1983 1985 1987 1989 1991 1993 1995 1997 1999 2001 IQUARTERLY AVERAGE

FIGURE 4 GROSS BETA ACTIVITY IN SURFACE WATER 1980 THROUGH 2001 Weapons Test 10-15-80 Chernobyl 04-26-86 Salem - 2 Criticality 08-02-80 GROSS BETA ACTIVITY IN SURFACE WATER 1971 THROUGH 2091 100 1973 1979 1986 1991 1997 Hope Creek Criticality 06-28-86

1987, 1989.

.1991, 1993 1995 1997 1999 I QUARTERLY AVERAGE I 1000.0 100.0 r11:

,J C.)

10.0 -

1.0 1981 1983 1985 2001 "il f

l l

l l

l 1 1 1

1 1

1 1 1 1 1 1 1 1 1 1 1 1 1 1

1 1

1 1 1 1.

I I I I I I I a I l I l I

I 1 I 1000 ]....

FIGURE 5 TRITIUM ACTIVITY IN SURFACEWATER-,.

1980 THROUGH 2001 10,000 TRITIL "10000 1000 tOO 10 1973 1979 Chernobyl 04-26-86 1,000 Weapons Test 10-15-80

-J 100 Hope Creek Criticality

.Salem-2 Criticality 06-28-86 08-02-80 10 1

8 I

I I

I I

I I

I I

i I

I I I

I I I

I I

I I I.

I I

I I

1 9ýI i,

I 1981 1983 1985

  • 1987*:
1989, 1991

.199,3 1995 1997 1999 2001 QUARTERLY AVERAGEj

FIGURE 6A CESIUM-137 ACTIVITY IN AQUATIC SEDIMENT 1980 THROUGH 2001 Weapons Test 10-15-80 CESIUM-137 ACTIVITY IN AQUATIC SEDIMENT 1977 THROUGH 2001 I=00 0

1985 19B9 290 1997 2001 IChernobyl 04-26-86 I

Salem - 2 Criticality 08-02-80 Hope Creek Criticality 06-26-86 1983 1985 1987 1989 1991 I

I I

I I

I I

I I

I I

I I

I I

I I

I 1993 1995 1997 1999 2001 I SEMI-ANNUAL AVERAGEI 10000 1000 CL 0"

0.

100 10 1981 I

I I

.1

...I I

I I

t973 1977 19"1

FIGURE 6B COBALT-60 ACTIVITY IN AQUATIC SEDIMENT 1980 THROUGH 2001 10000 1000 C)

Chernobyl 04-26-86 Solem - 2 Criticality 08-02-80 Hope Creek Criticality 06-26-86 1981 1983 1985 1987 1989 1991 1993 1996 1997 1999 2001 SEMI-ANNUAL AVERAGE Weapons Test 10-15-80.

100 COBALT-60 ACTIVITY IN AQUATIC SEDIMENT 1977 THROUGH 2001 10000 m 1000 10 lO.

.o.

10 1973 1977 1981 1985 1989 1993 1997 2001 10 I

I I

I I

I I

l lI Il I

I

FIGURE 7 CESIUM -137 ACTIVITY IN SOIL 1974 THROUGH 2001 10000.0 Salem - 2 Criticality 08-02-80 Hope Creek Criticality 06-28-86 4

I IF Salem - 1 Crticality 12-11-76 Weapons Test Chernobyl 10-15-80 04-26-86 1974 1977 1980 1983 1986 1000.0 -

C, 100.0 10.0 1989 1992 1995 1998 2001 YEARLY AVERAGE i

REFERENCES

[1]: Public Service Enterprise Group "Environmental Report, Operating License Stage - Salem Nuclear Generating Station Units 1 and 2".

1971.

[2] _ Public Service Enterprise Group "Environmental Report, Operating License Stage -

Hope Creek Generating Station".

1983.

[3]

United States Atomic Energy Commission.

"Final Environmental Statement Salem Nuclear Generating Station, Units 1 and 2".

Docket No. 50-272 and 50-311.

1973.

[4]

United States Atomic Energy Commission.

"Final Environmental Statement Hope Creek Generating Station, Docket No.

50-354. 1983.

[5]

Public Service Enterprise Group "Updated Final Safety Analysis Report - Salem Nuclear Generating Station, Units 1 and 2".

1982.

[6]

Public Service Enterprise Group "Updated Final Safety Analysis Report - Hope Creek Generating Station.

[71 Radiation Management Corporation.

"Artificial Island Radiological Environmental Monitoring Program - Annual Reports 1973 through 198.2".

[8]

Radiation Management Corporation.

"Artificial Island Radiological Environmental Monitoring Program - Preoperation Summary -

1973 through 1976".

RMC-TR-77-03, 1978.

[9]

Radiation Management Corporation.

"Artificial Island Radiological Environmental Monitoring Program

- December 11 to December 31, 1976"..

RMC-TR-77-02, 1977.

[10]

PSEG Power LLC Maplewood Testing Services.

"Salem'and Hope Creek Generating Stations' Radiological Environmental Monitoring Program - Annual Reports 1983 through 2000".

[11]

PSEG Power LLCMaplewood Testing Services. "Quality Assurance Plan."

June, 2001

[12]

Public Service Enterprise Group "Salem Nuclear Generating Station Technical Specifications",. Appendix A to Operating License No.

DPR-70, 1976, Sections 6.8.4.h -

1,2,3 and 6.9.1.7.

[13)

Public Service Enterprise Group "Hope Creek Generating Station Technical Specifications", Appendix A to Facility Operating License No. NPF-57, 1986, Sections 6.8.4.h - 1,2,3 and 6.9.1.6.

[14]

Public Service Enterprise Group "Offsite Dose Calculation Manual" Salem Generating Station.

29

REFERENCES (cont' d)

[15]

Public Service Enterprise Group

- Hope Creek Generating Station.

"Offsite Dose Calculation Manual"

[16]

U.S. Environmental Protection Agency.

"Prescribed Procedures for Measurement of Radioactivity in Drinking Water.*I" ;E-PA-600/4-80-032,

August, 1980.

30

APPENDIX A PROGRAM

SUMMARY

31

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY JANL DOCKET 50-272/-311 DOCKET NO. 50-354 JARY 1, 2001 to DECEMBER 31, 2001 MEDIUM OR PATHWAY Analysis And Lower All Indicator Locations Location with Highest Mean Control Location Number of SAMPLE 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 Beta 318 6.0 23 (265 /265 (8-44)

Gamma Be7 24 7.2 K-40 24 7.0 1-131 318 10 Air Iodine (10o-pCi/m 3) 56 (20/20)

(36-78) 11 (13/20)

(7-14)

< LLD 14G1 11.8 mi WNW 2F6 7.3 mi NNE 16E1 4.1 mi NNW 25 (53/53)

(11-44) 25 (53/53)

(11-44) 62 (4/4) 53 (4/4)

(49-78)

(33-66) 13 (2/4) 10 (2/4)

(12-14)

(9-11)

< LLD

< LLD II DIRECT Direct Radiation (mrad/std. month)

III TERRESTRIAL Milk (pCi/L)

Quarterly Badges 196 1-131 80 0.4 Gamma K-40 80 50 4.1 (172/172)

(2.6-6.1) 2S2 0.4 mi NNE

< LLD 1350 (60 /60)

(1220-1460) 5.6 (4/4) 4.5 (24/24)

(4.7-6.1)

(3.4-5.3)

< LLD 2F9 7.5 mi NNE

<LLD 1370 (20/20) 1310 (20/20)

(1250-1450)

(1220-1390)

I. AIRBORNE Air Particulates (10.3 pCi/m3) 0 0

0 0

0 0

0

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY JANU DOCKET 50-272/-311 DOCKET NO. 50-354 ARY 1, 2001 to DECEMBER 31, 2001 MEDIUM OR PATHWAY Analysis And Lower All Indicator Locations Location with Highest Mean Control Location Number of SAMPLE 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 Alpha 12 1.7 Beta 12 1.0***

H-3 Potable Water (pCi/L) 12 180 2.2 ý9/12)

(1.2-2.6) 12 (12/12)

(9.8-14)

< LLD Gamma K-40 12 30 71 (4/12)

(48-85)

RA-NAT 12 2.9 146 (12/12)

(90-193)

Alpha 24 1.0 0.9 (17/24)

(0.6-1.6)

Beta 24 1.0***

3.4 (24/24)

(2.7-4.7)

H-3 24 180

< LLD Gamma K-40 1-131 24 30' 44 (11 /24)

(26-70) 24 0.3

<LLD RA-NAT 24' 2.9 5.4 (5/24)

(4-6.5) 3E1 4.1 mi NE 3E1 4.1 mi NE 3E1 4.1mi NE 3E1 4.1mi NE 2F3 8.0 mi NNE 2F3 8.0 mi NNE 2F3 8.0 mi NNE 2F3 8.0 mi NNE 2.2' (9/12)

-(1.2-2.6) 12 (12/12)

(9.8-14)

< LLD 71 (4/12)

(48-85) 146 (12/12)

(90-193) 0.9 (17/24)

(0.6-1.6) 3.4 (24124)

(2.7-4.7)

< LLD No Control Location No Control Location No Control Location No Control Location No Control Location No Control Location No Control

-Location No Control Location 44 (11 /24)

No Control (26-70)

Location.

< LLD No Control Location 5.4 (5 /24)

No Control (4-6.5)

Location III TERRESTRIAL Well Water (pCi/L) 0 0

0 0

0 0

0 0

0 0

0

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY JANL DOCKET 50-272/-311 DOCKET NO. 50-354 JARY 1, 2001 to DECEMBER 31, 2001 MEDIUM OR PATHWAY Analysis And Lower All Indicator Locations Location with Highest Mean Control Location Number of SAMPLE 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 III TERRESTRIAL Fruit &

Vegetables (pCi/Kg-wet)

Game (pCi/Kg-wet)

Fodder Crops (pCi/Kg-wet)

Gamma K-40 RA-NAT Gamma K-40 Gamma Be-7 K-40 29 70 2090 (14/14)

(1420-2570) 29 15 16 (1 /1)

(16) 2 70 6

35 6

70 RA-NAT 6

14 Soil (pCi/kg (dry)

Gamma Be-7 K-40 9

80 9

70 Cs-137 9

33 Ra-NAT 9

45 Th-232 9

50 2600 (1/1)

(2600) 420 (3/5)

(210-670) 8430 (5/5)

(2560-16800) 20 (1 /5)

(20) 210 (3/8)

(120-360) 8850 (8/8)

(4610-12900) 210 (7/8)

(26-350) 660 (8/8)

(260-970) 790 (8/8)

(350-1200) 14G2 12.1 mi WNW 6F2 8.2 mi ESE 11D1 3.5miSW 2F9 7.5 mi NNE 11F3 5.3 mi SW 14F4 7.6 mi. WNW 11F3 5.3 mi. SW 14F4 7.6 mi. WNW S1ODI -3.9 mi. SSW 11F3 5.3 mi. SW 11F3 5.3 mi. SW 2460 (2/2)

(2290-2620) 16 (1 /1)

(16) 2060 (15 /15)

(1230-2710)

< LLD 2840 (1 /1) 2840 '(1/1)

(2840)

(2840) 670 (1/1)

(670) 9950 (2/2)

(4990-14900) 20 (1/1)

(20) 360 (1 /1)

(360) 12900 (1 /1)

(12900) 350 (1 /1)

(350) 970 (1 /1)

(970) 1200 (1 /1)

(1200) 350 (1 /i (350) 4380 (1 /1 )

(4380-4380) 10 (1/1)

(10)

< LLD 8190 (1./1)

(8190) 160 (1 /1)

(160) 700 (1 /1)

(700) 850 (1/1)

(850) 0 0

0 0

0 0

0 0

0 0

0

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY JANU DOCKET 50-272/-311 DOCKET NO. 50-354 JARY 1, 2001 to DECEMBER 31, 2001 MEDIUM OR PATHWAY Analysis And Lower All Indicator Locations Location with Highest Mean Control Location Number of SAMPLE Total Number Limit of Mean Name Mean Mean Nonroutine (UNIT OF MEASUREMENT) of Analyses Detection (Range)

Distance and Direction (Range)

(Range)

Reported Performed ILLD)

  • Measurements Beta 60 3.8 H-3 Gamma K-40 Gamma K-40 Sr-89 (bones)

Sr-90 (bones)

Gamma K-40 Blue Crabs (pCi/kg-wet)

Edible Fish (pCi/kg-dry)

(pCi/kg-wet)

Sediment (pCi/kg-dry) 20 180 60 30 4

70 1

600 1

130 6

70 82 (48/48)

(4.7-224)

< LLD 95 (45/48)

(42-178) 2710 (2 /2)

(2510-2910)

<LLD

< LLD 3530 -(4 /4)

(3240-3910)

Gamma Be-7 14 80 550 (5/12)

(220-870)

K-40 14 70 11550 (12/12)

(1020-15900)

Co-60 14 22

<LLD 7E1 4.5 mi SE 11A1 0.2 miSW 12CI 2.5 mi WSW 118 (12/12)

(34-224) 111 (12/12)

(54-178) 71 (12/12)

(6.4-129)

< LLD 99 (11 /12)

(38-165) 2870 (2/2) 2870 (2/2)

(2660-3080)

(2660-3080)

LLD LLD 12C1 2.5 mi WSW 11A1 0.2 mi SW 12C1 2.5 mi WbW

"<LLD LLD 3675 (2/2) 3675 (2/2)

(3650-3700)

(3650-3700) 870 (1 /2)

(870) 15600 (2/2)

(15600)

< LLD 350 (1 /2)

(350) 15600 (2/2)

(15600)

< LLD IV AQUATIC Surface Water (pCi/L) 0 0

0 0

0 0

0 0

0 0

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY JANL DOCKET 50-272/-311 DOCKET NO. 50-354 IARY 1, 2001 to DECEMBER 31, 2001 MEDIUM OR PATHWAY Analysis And Lower All Indicator Locations Location with Highest Mean Control Location Number of SAMPLE Total Number Limit of Mean Name Mean Mean Nonroutine (UNIT OF MEASUREMENT) oft Analyses, Detection (Range)

Distance and Direction (Range)

(Range)

Reported Performed (LLD)

  • Measurements IV AQUATIC Sediment (pCi/kg-dry)

Cs-134 14 27 23 (2/12)

(19-27)

Cs-137 14 33 59 (9/12)

(19-120)

RA-NAT 14 45 530 (12/12)

(96-760)

Th-232 14 50 710 (12/12)

(82-1130) 7E1 4.5 mi SE 16A1 0.7 mi NNW 12C1 2.5 mi WSW 16F1 6.9 mi NNW

  • LLD listed is the lower limit of detection which we endeavored to achieve during this reporting period. In some instances nuclides were detected at concentrations above the LLD values shown. All strontium results are reported by DESEL as MDC..
    • Mean calculated using values above LLD only. Fraction of measurements above LLD are in parentheses.

Typical LLD values.

27 (1 /2)

(27) 98 (2/2)

(76-120) 690 (2/2)

(550-820) 995 (2/2)

(860-1130)

< LLD 58 (1 /2)

(58) 690 (2/2)

(550-820) 790 (2/2)

(480-1100) 0 0

0 0

APPENDIX SAMPLE DESIGNATION AND LOCATIONS 39 B

APPENDIX B SAMPLE DESIGNATION The PSEG's Maplewood Testing Services 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.

= Air Iodine

= Air Particulate

= Hard Shell Blue Crab

= Edible Fish

= Sediment

= Green Leafy Vegetables

= Vegetables (Various)

= Game (Muskrat)

IDM MLK PWR PWT SOL SWA VGT WWA Immersion Dose (TLD)

Milk Potable Water (Raw)

Potable Water (Treated)

Soil Surface Water Fodder Crops (Various)

Well Water The last four symbols are a location code based on direction and distance from a standard reference point.

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; e.g.,

2=NNE, 3=NE, 4=ENE, etc.

The next digit is a

letter which represents the radial distance from the reference point:

S = On-site location A = 0-1 miles off-site B = 1-2 miles off-site C = 2-3 miles off-site D = 3-4 miles off-site E =

4-5 miles off-site F =

5-10 miles off-site G =

10-20 miles off-site H =

>20 miles off-site The last number is the station numerical designation within each sector and zone; e.g., 1,2,3,...

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 450 (north east) with respect to the reactor site 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.

41 AIO APT ECH ESF ESS FPL FPV GAM

TABLE B-1 SAMPLING LOCATIONS Specific information about the individual sampling locations are given in Table B-I.

Maps B-I 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.

The Datem used was WGS 84.

STATION CODE ISi 2S2 2S4 3S1 4S1 5S1 4-6S2 7S1 15SI 16SI 11A1 15AI 16A1 12Cl 4D2 5DI 10DI lID1 14D1 15D1 2El 3E1 STATION LOCATION 0.55mi.

N of vent 0.4 mi.

NNE of vent 0.59 mi.

NNE of vent 0.58 mi.

NE of vent 0.60 mi.

ENE of vent 1.0 mi.

E of vent; site access road 0.2 mi. ESE of vent; observation building 0.12 mi.

SE of vent; station personnel gate 0.14 mi.

SSW of vent; inlet cooling water bldg.

0.09 mi.

SW of vent; service water inlet bldg.

0.57 mi.

NW of vent 0.54 mi.

NNW of vent 0.2 mi.

SW of vent; outfall area 0.3 mi.

NW of vent; cooling tower blowdown discharge line outfall 0.7 mi.

NNW of vent; south storm drain discharge line 2.5 3.7 3.5 3.9 3.5 3.4 3.8 4.4 mi.

mi.

mi.

mi.

mi.

mi.

mi.

mi.

WSW of vent; west bank of Delaware River ENE of vent; Alloway Creek Neck Road E of vent; local farm SSW of vent; Taylor's Bridge Spur SW of vent WNW of vent; Bay View, Delaware NW of vent; Rt.

9, Augustine Beach NNE of vent; local farm 4.1 mi.

NE of vent; local farm LATITUDINAL DEG.

MIN.

SEC 39 -

28 16 39 -

28 -

07 39 -

28 16 39 -

28 08 39 -

28 02 39--

27 -

38 39 -

27 43 39 - 27 44 39 -

27 39, 39 -

27 -

43 39 -

28 -

10 39 -

28 -

13 39 - 27 59 39 -

27 67 39 28 24 39 39 39 39 39 39 39 39 27 29 28 24 24 29 30 31 L 22 18 24 37 49 02 08 23 LONGITUDINAL DEG.

MIN.

SEC -

75 75 75 75 75 75 75 75 75 75 75 75 75 75 32 -

15 31 -

57 31 -

55 31 -

41 31 33 31 08 31 -

55 32 -

03 32 -

10

-32 12 32 32 32 26 32 -

25 32 19 75 -

32 58 75 75 75 75 75 75 75 75 75 39 -

30 -

07 34 32 28 33 34 35 35 30 28 08 22 44 26

-31 02 26 41 SAMPLE TYPE IDM IDM IDM IDM IDM AIO,APT, IDM IDM, SOL., ESS',

IDM IDM IDM IDM IDM ECH, ESF, ESS, SWA ESS ESS ECH, ESF, ESS, SWA IDM AIO,APT, IDM IDM, SOL

GAM IDM IDM IDM GAM, IDM,VGT,WWA,FPV

TABLE B-1 (cont' d)

STATION CODE 7E1 9E1 11E2 12E1 13E1 16El IF1 1F2 2F2 2F3 2F4 2F5 2F6 2F7 t

2F8 2F9 3F2 3F3 3F5 3F6 3F8 4F2 5F1 6F1 6F2 7F2 10F2 1IF!

11F3 12F1 STATION LOCATION 4.5 mi.

4.2 mi.

5.0 mi.

4.4 mi.

4.2 mi.

4.1 mi.

5.8 mi.

7.1 mi.

8.7 mi.

Salem 8.0 mi.

6.3 mi.

7.4 mi.

7.3 mi.

5.7 mi.

5.3 mi.

7.5 mi.

Tilbury 5.1 mi.

8-.6 mi.

9.4 mi.

  • 6.5 mi.

Road 5.1 mi.

Bridge 6.0 mi.

6.5 mi.

6.4 mi.

8.2 mi.

9.1 mi.

5.8 mi.

6.2 mi.

5.3 mi.

9.4 mi.

SE of vent; 1 mi.

W of Mad Horse Creek S of vent SW of vent; Rt.

9 WSW of vent; Thomas Landing W of vent; Diehl House Lab NNW of vent; Port Penn "N of vent; Fort Elfsborg "N of vent; midpoint of Delaware River NNE of vent; Corner of 5t

&Howell, NNE of vent; Salem Water Company NNE of vent; local farm NNE of vent; Salem High School NNE of vent; Southern Training Center NNE of vent; local farm NNE OF vent; local farm NNE of vent; Tilbury Farms

, 45 S.

Rd, Salem NE of vent;Hancocks Eridge Municipal Bld NE of vent; Quinton Township School NE of vent; Harris's Farm Market NE of vent; #324 Salem/Hancocks Bridge NE of vent; 33 Maple Ave.,

Hancocks ENE of vent; Mays Lane, Harmersville E of vent; Canton ESE of vent; Stow Neck Road ESE of vent; RD#3 Box 160 Bridgeton, NJ SE of vent; Bayside, New Jersey SSW of vent; Rt.

9 SW of vent; Taylor's Bridge Delaware SW of vent; Townsend, Delaware WSW of vent; Townsend Elementary School LATITUDINAL DEG.

MIN.

SEC 39 39 39 39 39 39 39 39 39 39 39 39 39 39 39 39 39 39 39 39 -

25 24 24 26

  • 27 30 32 33 34 33 33 33 33 32 31 33 08 10 20 52 59 47 45 08 38 40 21 27 43 40 54 55 LONGITUDINAL DEG.

MIN.

SEC 75 75 75 75 75 75 75 75 75 75 75 75 75 75 75 75 75 75 75 75 30 25 32 -

38 33 29 32 03 39 -

30 -25 39 39 39 39 39 39 39 39 39 29 28 26 26 22 23 24 24 23 58 22 24 04 56 01 44 06 47 28 32 35 36 36 34 31 32 28 27 30 28 28 30 29 29 27 24 24 28 64 42 33 59 44 34 06 54 04 18 33 31 48 53 18 30 36 45 54 00 75 -

27 -

37 75 75 75 75 75 75 75 75 75 26 24 25 23 24 34 37 36 41 03 59 09 09 17 09 37 20 18 SAMPLE TYPE ESF,ESS,SWA IDM IDM IDM IDM AIO,APT, IDM,SOL AIO,APT, IDM SWA IDM PWR, PWT FPV, FPL IDM AIO,APT, IDM SOL FPV MLK,FPV,VGT,SOL IDM IDM FPV FPV FPV,FPL IDM IDM,SOL IDM FPV, FPL IDM IDM IDM MLK, VGT, SOL IDM 13F2 6.5 mi.

W of vent; Odessa, Delaware21

ý39, - 27 7 18 75 21 IDM

TABLE B-I (cont'd)

STATION CODE 13F3 13F4 14F2 14F3 14F4 15F3 16F1 16F2 IGI 1G3 IG4 2G2 3G1

ý4-9G1 10GI 14GI 14G2 16G1 3H1 3H5 3H3 STATION LOCATION 9.3 mi.

W ofvent; Redding Middle School, Middletown, Delaware 9.8 mi.

W of vent; Middletown, Delaware 6.6 mi.

5.4 mi.

7.6 mi.

5.4 mi.

6.9 mi.

8.1 mi.

10.3 mi.

WNW of vent; Boyds Corner WNW of vent; local farm WNW of vent; local farm NW of vent NNW of vent; C&D Canal NNW of vent; Delaware City Public School N of vent; local farm 19 mi.

N of vent; N.

Church St. Wilmington, Del 10.8 mi.

N of vent; (Dads Produce);Rte.

49, South Broadway, Pennsville 13.5 mi.

NNE of vent; Moore's Market; 324 Pointers Auburn Road (Rt.. 540),

Salem, NJ 08079 17 mi.

NE of vent; Mr. Lee Williams Farm 10.3 mi.

S of Vent; Mr.

Goldsburrough-, 1784 Woodland Beach Rd.,

Smyrnas, Delaware 12 mi.

SSW of vent; Smyrna, Delaware 11.8 mi.

WNW of vent; Rte. 286; Bethel Church Road; Delaware 12.1 mi.

WNW of vent; Locust Grove Farm & Garden Center; 1084 Bethel Church Road; Middletown, DE 19709 15 mi.

NNW of vent; Greater Wilmington Airport 32 mi.

NE of vent; National Park, New Jersey 25 mi.

NE of vent; Sorbello Girl's:Market 110 mi.

NE of vent; Maplewood Testirng Services LATITUDINAL DEG. MIN.

SEC 39 -

27 -

14 39 39 39 39 39 39 39 39 39 39 26 30 29 30 30 33 34 36 44 37 51 00 33 44 58 55 18 31 16 55 LONGITUDINAL SAMPLE TYPE "DEG. MIN.

SEC 75 42 32 75 75 75 75 75 75 75 75

-75 75 43 38 37 40 36 34 35 29 32 30 07 59 55 52 36 25 25 59 31 44 39 -

38 19 75 -

26 10 39 -

35 56 39 -

18 -

47 39 18 13 39 31 18 39' -

31 21 39 39 39 40 40 51 41 43 32 36 02 25 75 75 75 75 16 -

47 33 50 36 -

05 46 -

30 IDM IDM IDM FPV, FPL MLK,VGT,SOL.

IDM ESS,SWA IDM FPV, FPL IDM FPV FPV IDM,MLK,VGT,SOL FPV IDM AIO,APT, IDM 75 -

44 - 57 FPV 75 75 75 74 35 11 12 15 06 23 09 IDM IDM FPL, FPV IDM NOTE:

All station locations are referenced to the midpoint of location are:

Latitude N 390 -

27'

- 45.3" and Longitude W 750 the two Salem Units' 32' 09.7".

Vents.

The coordinates of this All Game (GAM),

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 Station's ODCM.

Vegetable samples are not always collected in consecutive years from the same farmer since they rotate the type of crop they grow.

L

MAP B-1 ON-SITE SAMPLING LOCATIONS 1

5 9

45 D~~~nttav4~jq an.

R0kA ff) 1

.flfS ()

nom R

rina pIn÷lý++

nn 1

, Ic ý 1")0(')

MAP B-2 SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM OFF-SITE SAMPLING LOCATION 15 NW 16 NNý I

AML1 N

2 NNE A

HdUNDRED PE 8R VTW HU2NDR**D i

14G E R ES 3F2 2702 HUNDRED Fl H E

L w

to 2/.

br E~46

(-00--

APPENDIX C DATA TABLES 47

APPENDIX C DATA TABLES Appendix C presents the analytical results of the 2001 Radio logical Environmental Monitoring Program for the period of January 1 to December 31, 2001.

TABLE OF CONTENTS TABLE NO.

TABLE DESCRIPTION PAGE ATMOSPHERIC ENVIRONMENT AIR PARTICULATES C-I 2001 Concentrations of Gamma Emitters in Quarterly Composites of Air Particulates............................................

53 C-2 2001 Concentrations of Gross Beta Emitters in Air Particulates.

54 AIR IODINE C-3 2001 Concentrations of Iodine-131 in Filtered Air.................

56 DIRECT RADIATION THERMOLUMINESCENT DOSIMETERS C-4 2001 Direct Radiation Measurements

- Quarterly TLD Results.....

58 TERRESTRIAL ENVIRONMENT MILK C-5 2001 Concentrations of Iodine-131 and Gamma Emitters in Milk...

59 WELL WATER C-6 2001 Concentrations of Gross Alpha and Gross Beta Emitters, and Tritium in Well Water......................................

61 49

IU III DATA TABLES (cont'd.)

TABLE NO TABLE.DESCRIPTION PAGE TERRESTRIAL ENVIRONMENT (cont, d)

C-7 2001 Concentrations of Gamma Emitters in Well Water...............

62 POTABLE WATER C-8 2001 Concentrations of Gross Alpha and Gross Beta Emitters, and Tritium in Raw and Treated Potable Waters......................

63 C-9 2001 Concentrations of Iodine 131 and Gamma Emitters in Raw and Treated Potable Water..........................................

64 FOOD PRODUCTS C-10 2001 Concentrations of Gamma Emitters in Vegetables...............

65 C-11 2001 Concentrations of Gamma Emitters in Game......................

66 FODDER CROPS C-12 2001 Concentrations of Gamma Emitters in Fodder Crops.............

67 SOIL C-13 2001 Concentrations of Gamma Emitters in Soil 68 AQUATIC ENVIRONMENT SURFACE WATER C-14 2001 Concentrations of Gross Beta Emitters in Surface Water....

69 C-15 2001 Concentrations of Gamma Emitters in Surface Water............

70 C-16 2001 Concentrations of Tritiuri in Quarterly Composites of Surface Water.................

72 EDIBLE FISH C-17 2001 Concentrations of Strontium-89, Strontium-90 and Gamma Emitters in Edible Fish........................................

73 50

DATA TABLES (cont'd'.d)

TABLE NO TABLE DESCRIPTION PAGE BLUE CRABS C-18 2001 Concentrations of Gamma Emitters in Crabs.....................

74 SEDIMENT C-19 2001 Concentrations of Gamma Emitters in Sediment..................

75 SPECIAL TABLES LLDs C-20 2001 PSE&G Maplewood Testing Services' LLDs for Gamma Spectrometry...................................................

76 51

Table C-1 2001 CONCENTRATIONS OF GAMMA EMITTERS*

IN QUARTERLY COMPOSITES OF AIR PARTICULATES Results in Units of 10-3 pCi/rn 3 +/- 2 sigma STATION Sampling Period

<--- Gamma Emitters --- >

ID Start Stop Be-7 K-40 SA-APT-5S 1 SA-APT-1 F1 SA-APT-2F6 SA-APT-5D 1 SA-APT-1 6E1 SA-APT-1 4G 1 (C)

SA-APT-5S 1 SA-APT-1 F1 SA-APT-2F6 SA-APT-5D 1 SA-APT-16E1 SA-APT-14G1 (C)

SA-APT-5S 1 SA-APT-1 F1 SA-APT-2F6 SA-APT-5D 1 SA-APT-16E1 SA-APT-14G1 (C)

SA-APT-5S 1 SA-APT-1 F1 SA-APT-2F6 SA-APT-5D1 SA-APT-1 6E1 SA-APT-14G1 (C) 12/26/2000 12/26/2000 12/26/2000 12/26/2000 12/27/2000 12/27/2000 3/27/2001 3/27/2001 3/27/2001 3/27/2001 3/28/2001 3/28/2001 6/25/2001 6/25/2001 6/25/2001 6/25/2001 6/26/2001 6/26/2001 9/24/2001 9/24/2001 9/24/2001 9/24/2001 9/25/2001 9/25/2001 AVERAGE

  • All other gamma emitters searched for were <LLD; typical LLDs are given in Table 20.

(C) Control Station 53 to to to to to to to to to to to to to to to to to to to to to to to to 3/27/2001 3/27/2001 3/27/2001 3/27/2001 3/28/2001 3/28/2001 6/25/2001 6/25/2001 6/25/2001 6/25/2001 6/26/2001 6/26/2001 9/24/2001 9/24/2001 9/24/2001 9/24/2001 9/25/2001 9/25/2001 1/2/2002 1/2/2002 1/2/2002 1/2/2002 1/3/2002 1/3/2002 38+/-4 36+/-3 51_+/-4 37+/-3 37+/-4 33+/-3 64+/-6 69_+/-5 69_+/-4 61 +/-4 68+/-4 66-+/-4 70+/-5 67_+/-4 78_+/-5 60+/-4 58+/-4 58+/-6 48+/-4 47+/-4 49+/-4 51 +/-4 51-+/-4 53+/-4 55+/-_25 11 _4 10+/-3 12+/-3 10+/-2 14+/-5 11+/-2

<4

<4

<4 12+/-3

<4

<4 10+/-2 9_+/-2

<6

<3

<4

<6 12+/-3 9_+/-2 11_+/-2 7-+/-3 12+/-3 9+/-3 8_+/-7

TABLE C-2 2001 CONCENTRATIONS OF GROSS BETA EMITTERS IN AIR PARTICULATES Results in Units of 10.3 pCi/M 3 +/- 2 sigma STATION ID..............................

Control MONTH SA-APT-14G1 SA-APT-16E1 SA-APT-1F1 SA-7APT-2F6 SA-APT-5D1 SA-APT-5S1 AVERAGE January February March April May June 23+/-2 18+/-3 17+/-2 19+/-2 34+/-3 17+/-2 21 +/-3 28+/-2 20+/-2 14+/-2 12+/-2 18+/-2 13+/-2 13+/-2 22+/-3 18+/-2 35+/-4 29+/-3 35+/-3 28+/-3 11+/-2 13+/-2 15 +/-2 24+/-3 25+/-2 39+/-3 24+/-2 22+/-3 21 +/-2 19+/-2 33+/-3 17+/-2 23+/-3 25+/-2 21 +/-2 18_+/-2 11+/-2 15+/-2 11+/-2 12+/-2 18+/-3 19+/-2 32+/-3 27+/-2 29+/-2 29+/-3 9+/-2 11+/-2 16+/-2 24+/-3 25+/-2 42+/- 3 21+/-2 17+/-2 17+/-2 18+/-2 32+/-3 15+/-2 16+/-2 25+/-2 20+/-2 19+/-2 15+/-2 16+/-2 1.7+/-2 11,+/-2 20+/-2 19+/-2 34+/-3 27+/-3 32+/-3 23+/-2 10+/-2 9+/-2 18+/-2 22+/-2 22+/-2 24+/- 2 21 +/-2 18+/-2 22+/-2 19+/-2 32+/-3 21+/-2 20+/-2 27+/-2 23+/-2 24+/-2 15+/-2 17+/-2 1.8+/-2 10+/-2 20+/-2 18+/-2 33+/-3 29+/-3 35+/-3 24+/- 2 11+/-2 8+/-2 15+/-2 23+/-2 21_+/-2 24+/-2 21+/-2 21 +/-3 20+/-2 15+/-2 30+/-3

.15+/-2 13+/-2 24+/-2 20+/-2 21 +/-3 18+/-2 17+/-2 17+/-2 9+/-2 19+/-2 19+/-2 29+/-3 27'+/- 2 32+/-3 26+/-2 8+/-2 11+/-2 13+/-2 21+/-2 21+/-2 20+/- 2 21 +/-2 19_+/-3 16_+/-2 18+/-2 32+/-3 17+/-2 15+/-2 28+/-2 18+/-2 20+/-2 16+/-2 14+/-2 18+/-2 11+/-2 19+/-3 15+/-2 29+/-3 27+/-3 28+/-3 25+/-3 9+/-2 9+/-2 16+/-2 21+/-2 24+/-2 20+/-2 22+/-3 19+/-4 19+/-5 18+/-3 32+/-3 17+/-4 18+/-8 26+/-33 20+/-3 14+/-5 16+/-3 16+/-6 11+/-3 20+/-3 18+/-3 32+/-5 27+/-2 32+/-6 26 +/-4 9+/-3 10+/-3 15+/-3 22+/-3 2,3:+/-t4 28+/- 20 L~n

TABLE C-2 2001 CONCENTRATIONS OF GROSS BETA EMITTERS IN AIR PARTICULATES Results in Units of 10,3 pCi/m 3 +/- 2 sigma STATION ID ------------------------------------

Control MONTH SA-APT-14G1 SA-APT-16E1 SA-APT-1F1 SA-APT-2F6 SA-APT-5D1 SA-APT-5S1 AVERAGE September 27+/- 2 25 +/-+3 25+/-2 29+/-3 July 22_+/-2 17+/-2 19+/-2 23-+/-3 18+/-2 22+/-3 24_+/-2 26_+/-2 29+/-3 28+/-3 20+/--2 20+/-2 24+/-3 19+/-2 29 3

23+/-2 33+/-2 28+/-3 28+/-3 16+/-2 20+/-2 23+/-3 17+/-2 27+/-3 29+/-3 26+/-2 27+/-3 25+/-2 23+/-3 23_+/-2 25+/-2 13+/-2 38+/-3 18+/-2 24+/- 2 23+/-2 28+/-3 31 +/-2 39+/-3 19+/-2 28+/-3 34+/--3 28-+/-2 25_+/-2 33+/-2 23 +/-15 26+/-2 23+/-2 22+/- 2 22_+/-3 19+/-2 26++/-3 23+/-2 29+/-2 29-+/-3 28+/-2 22+/--3 26_+/-2 28-+/-3 14+/-2 41 +/-3 22_+/-2 27-+/-3 24+/-2 26+/-3 31+/-2 39_+/-3 20+/- 2 338.+/-3 36-+/-3 26+/- 2 26+/-2 33+/-3 24+/-14 27_+/-2 24+/-3 23+/-2 32+/-3 16_+/-2 41+/-3 20+/-2 25_+/-3 21 +/-2 29+/-3 38_+/-3 40+/- 3 19_+/-2 32+/-3 34+/-3 26+/-2 28+/-2 37 +/- 3 August 23+/-15 U,n Ln 22+/-15 22+/-14 GRAND AVERAGE October November December AVERAGE 28+/-2 16+/- 2 15-+/-2 17-+/-2 15+/-2 24+/-3 19_+/-2 21 +/-2 26-+/-3 26-+/-2 18+/-+2 22+/-_2 32_+/-3 15+/-2 43-+/-3 18+/-2 28+/-3 24+/-2 29 +/-3 30+/-2 37 +/-3 20+/-2 34+/-3 35-+/-3 28+/-_2 28+/-2 35 +/-3 14+/-2 44+/-3 21 +/-_2 26+/-3 28+/-2 29+/-3 33+/-2 43+/-3 21 +/-2 34+/-3 41 +/-3 31+/-3

.26+/-2 36+/-2 25+/-16 27_+/-3 20+/-2 19_+/-2 20+/-3 13+/-2 20+/-3 26+/-3 22_+/-2 28+/-3 21 +/-2 25+/-3 20+/-2 30+/-3 16++/-2 44+/- 3 18-+/-2 24+/-3 23-+/-2 29_+/-3 28_+/-2 39-+/-3 15+/-2 30+/-_3 31 +/-3 29+/-2 29_+/-2 33+/-3 26_+/-5 19+/-5 19+/-4 21+/-5 17+/-5 24+/--7 24_+/-

26+/-9 28+/-3 26+/--5 23+/-5 23+/--5 29+/-6 15+/-2 42+/-5 20+/-4 26+/-3 24+/-5 28+/-2 32+/-7 40+/-4 19+/-4 32+/-4 35+/-7 28+/-4 27+/-2 34+/-4 23+/- 15

TABLE C-3 2001 CONCENTRATIONS OF IODINE-131* IN FILTERED AIR Results in Units of 10.3 pCi/m 3 STATION ID ----------------------------------------------

Control MONTH SA-AIO-14G1 SA-AIO-16E1 SA-AIO-1F1 SA-AIO-2F6 SA-AIO-5D1 SA-AIO-5S1 January February March April May June

<2.2

<2.3

<1.7

<2.3

<4.9

< 1.4

<3.4

<2.3

<2.5

<2.2

<2.9

<2.4

<1.7

<5.7

<2.9

<3.3

<6.1

<2.2

<3.7

<5.5

<2

<1.7

<2.8

<3.5

<2.4

<"1.7

<3.5

<5.3

<1.7

<3.4

<4.4

<1.8

<2.9

<2.7

<1.5

<2

<3.5

<2.7

<1.7

<3.5

<6.7

<2.7

<2.6

<3.7

<4.6

<5.7

<1.6

<4

<4.3

<2.5

<2.9

<3.2

<6.7

<2.2

<3.1

<1.3

<2.5

<1.8

<2.4

<3.8

<2.5

<1.6

<2

<4.4

<1.8

<2.6

<3.5

<3.6

<2.8

<2.3

<4.1

<2.8

<1.5

<2

<2.1

<1.4

<1.7

<3.1

<2

<2.4

<6.5

<1.2

<4.4

<1.9

<2.8

<*1.3

<2.2

<4.6

<3

<3.2

<3

<2.8

<2.9

< 2

<3.1

<3.7

<2

<2.5

<2.7

<2

<2.1

<1.9

<3..5

< 1.7ý

<5.1

<2.6

<2

<1.5

<2.3

<2.1

<2

<3.2

<1.9

<2.6

<2.2

<4.8

<*4*.. 3

<4.8

<2.8

< 1.7

< 5

<3.1

<4

<2.7

<3.6

<2.7

<3

<1.8

<2.4

<2.7

<3.3

<4.9

<2.5

<1.7

<1.9

<1.6

<2.2

<5.7

<2.5

<4

<2.1

<2.6

<4.3

<2.1

<5.3

<3

<2.1

<4

<4.2

<1.6

<1.6

<1.9

<5.1

<3.2

<2.6

<3.2 LnJ OPN

TABLE C-3 2001 CONCENTRATIONS OF IODINE-131* IN De,.Ia +

-"-nI e nf In.

3 n

  • rlm3 FILTERED AIR S

T A

T IO---------------------------------

STATION ID ----------------.. ----------------------------- >

Control MONTH SA-AIO-14G1 SA-AIO-16E1 SA-AIO-1F1 SA-AIO-2F6 SA-AIO-5D1 SA-AIO-5S1 July August September October November

<2.4

<1.7

<2.4

<3.7

<1.8

<.1.6

<2.3

<4.9

<2.4

<2,.3

<4.1

<1.3

<1.7

<4.9

<1.4

<1.8

<3.2

<2

<2.3

<2.9

<1.7

<4

<2

<4.5

<2.6

< 1.9

<2.6

<2.1

<2.3

<3.1

<2.2

<2.1

<1.7

<3

<4.2

<3.4

<3.1

<2.8

<1.6

<3.6

<1.1

<2.5

<2.2 December 2.9

< 3.3

<3.7

<3

<1.7

<3.1

<1.6

<2.1

<2.3

<1.5

  • 1-131 results are corrected for decay to sample

<1.9

<1.3

<5.9

<4

<1.9

<3.3

<3.4

<2.8

<2.6

<5.4

<3.6

<3.5

<3.9

<1.8

<2.4

<2.1

<1.5

<2.4

<9.5

<2.7

<6.6

<2.6

< 3.3"

<3.6

<1.9

"< 2

<3.7 stop date.

<5.9

<2

<3.7

<5.8

<1.4

<3.6

<1.7

<3$.9

<2.2

<1.2

<2.3

<1.2

<3

<1..7

<1

< 1.4

<6.4

<2.8

<2.5

<1.3

<4.5

<2.9

<3.9

<2.2

<2.3

<1.3

<3.5

<1.8

<4.2

<3.4

<1.5

<1.1

<3

<2.5

<2.8

<3.4

<3.2

<4.2

<4.9

<1.8

<3

<1.3

<4.7

<1

<2.1

<2.1

<3.6

<3.1

<4.5

<5.1

<2.1

<2

<1.7

<1.5

< 2.6

<2.5

<1.4

<3.7

<2.3

<2

<1.9

<3.1

<3.5

<2.6

<2.7

<1.7

<3.6

<1.5

<1.8

<4.

<1.6

<1.2

<4.1

<3.3

<1.7

<4.3

<1.4

<2.4

<1.8

<1.1

ti

-t I TA.BLE C-4 2001 DIRECT RADIATION MEASUREMENTS - QUARTERLY TLD RESULTS Results in mradfstandard month* +

2 sigma STATION ID SA-iDM-2S2 SA-IDM-5S1 SA-IDM-6S2 SA-lDM-7S1 SA-IDM-1 0S1 SA-IDM1 1 Si SA-IDM-4D2 SA-IDM-5D 1 SA-IDM-1OD1 SA-IDM-14D13 SA-IDM-1 5DI SA-lDM-2E1 SA-IDM-3E1 SA.IDM-9E 1 SA-IOM-11 1E2 SA-lDM-12E1 SA-lDM-13E1.

SA-IDM-1 6E1 SA-IDM.1 Fl SA-IDM-2F2 SA-IDM-2F5 SA-lDM-2F6 SA-IDM-3F2 SA-IDM-3F3 SA-IDM-4F2 SA-IDM-5F1 SA-IDM-6F1 SA-IDM-7F2.

SA-IDM-10F2 SA-IDM-1 1 Fl SA-IDM-1 2FI SA-IDM-1 3F2 SA-IDM-1 3F3 SA-IDM-1 3F4 SA-IDM-14F2 SA-IOM-1 SF3 SA-IDM-16F2 SA-IDM-1G3 (C)

SA-IDM-3G1 (C)

SA-IOM-1OGi (C)

SA-IDM-1 6G1 (C)

SA-IDM-3H1 (C)

SA-IDM-1 Si SA-1DM-3S1 SA-IDM-2S4 SA-1DM-4S 1 SA-IDM-1 5S1 SA-IDM-1 6S1 SA-IDM-1 4G1 (C)

AVERAGE The standard month = 30.4 days.

'Quarterly Element TLD results by DESEL.

(C) Control Station

"'JAN to MAR

-5.7,+/-0.5 3.5 +/-0.3 4.9+/-0.3 5.4+/-0.3 4.0 +/-0.4 3.6 +/-0.5 4.1 +/-0.4 3.7 +/-0.5 4.3 +/-0.4 3.8 +/-0.3 4.5 +/-0.4 4.1 +/-0.4 3.4 +/-0.4 4.0 +/-0.3 5.8 +/-4. 1 4.5 +/-0.5 3.7 +/-0.7 4.2 +/-0.4 4.0 +/-0.4 3.5 +/-0.3 4.1 +/-0.3 3.7 +/-0.3 3.5 +/-0.3 3.5 +/-0.4 3.4 +/-0.4 3.6+/-0.4 3.0+/-0.3 2.6+/-0.3 4.3 +/-0.9 4.5 +/-0.3 4.1 +/-0.4 3.9 +/-0.3 4.0 +/-0.5 4.4+/-0.4 4.5 +/-0.5 3.6 +/-0.3 5.0 +/-0.5 4.3 +/-0.5 4.2 +/-0.5 4.5 +/-0.3 3.4 +/-0.4 4.2 +/-0.3 3.4+/-0.4 3.6 +/-0.4 3.7 +/-0.3 3.3 +/-0.3 4.2 +/-0.6 4.4+/-0.4 4+/- 1.2 GRAND AVG APR to JUN 5.7 +/-0.5 3.8 +/-0.4 5.2 +/-0.5 5.6 +/-0.4 4.3 +/-0.5 4.1 +/-0.5 4.4+/-0.4 4.1 +/-0.4 4.6 +/-0.4 4.1 +/-0.4 4.7 +/-0.5 4.4+/-0.4 3.8 +/-0.4 4.3 +/-0.3 4.7 +/-0.5 4.6 +/-0.5 3.9 +/-0.3 4.4+/-0.4 4.3 +/-0.3 3.7 +/-0.4 4.4 +/-0.3 4.1 +/-0.3 3.7 +/-0.4 3.8 +/-0.5 3.8 +/-0.4 4.0+/-0.4 3.4+/-0.4 3.0 +/-0.4 4.6 +/-0.3

.4.9 +/-0.3 4.4+/-0.4 4.4+/-0.4 4.2 +/-0.3 4.2 +/-0.3 4.8 +/-0.4 5.0 +/-0.5 3.' 9 +/-0.4 5.0 +/-0.4 4.6 +/-0.4 4.5 +/-0.4 4.9 +/-0.4 3.7 +/-0.4 4.8 +/-0.5 3.6 +/-0.4 3.9 +/-0.4 4.0 +/-0.3 3.86+/-0.4 4.7 +/-0.4 4.6 +/-0.3 4.3+/- 1. 1 4.2 +/-1.2 58 JUL SEP 6.1 +/-0.5 3.8 +/-0.3 5.3 +/-0.4 5.3 +/-0.6 3,.9+/-0.3 3.4 +/-0.4 4.3 +/-0.3 4.0+/-0.7 4.9 +/-0.4 4.2 +/-0.5 4.7.+/-0D.4 4.3 +/-0.3 3.7 +/-0.6 4.6 +/-0.3 4.7+/-0.4 4.9,+/-0.3

ý3.8 +/-:0.4 4.4+/-0.4 4.31+/-0.4 3.6 +/-0.3 4.4+/-0.4 3.9+/-0.5 3.7 +/- 0.5 3.6 +/-0.4 3.7 +/-0.4 4.0+/-0.3 3.2 +/-0.4 2.9 +/-0.2 4.6 +/-0.3 4.8 +/-0.4 4.3t

+/-0.4 4.2 +/-0.6 4.4 +/-0.3 4.3 +/-0.4 4.8'+/-0.4 5.1 +/-0.6 4.2 +/-0.3 5.0+/-0.4 4.6 +/-0.3 4.5 +/-0.5 5.3 +/-0.7 3.6 +/-0.4 4.8+/-0.5 3.5 +/-0.4 3.9 +/-0.4 3.9 +/-0.3 3.8+/-t0.3 4.6+/-10.5 4.6 +/-0.5 4.3 +/-1.2 Oct to DEC 4.8+/-5 3.6 +/-0.3 4.8+/-0.4 5.9+/- 1.4 4.0 +/-0.3 3.6 +/-0.4 4.3 +/-0.4 3.9 +/-0.3 4.5 +/-0.4 4.1 +/-0.4 4.4+/-0.4 4.2 +/-0.4

.3.5 +/-0.4 4.4+/-0.4 4.5 +/-0.6 4.6+/-0.4 3.6:t+/-0.4 4.2 +/- 0.5 4.3 +/-0.4 3.6 +/-0.3 4.1 +/-0.4 3.9 +/-0.5 3.6 +/-0.3 3.5 +/-0.3

.3.5+/-0.3 3.7 +/-0.5 3.2 +/-0.3 2.8 +/-0.2 4.3 +/-0.4 4.5 +/-0.3 4.2 +/-0.3 4.0 +/-0.3 4.2+/-0.5 4.2 +/-0.4 4.6+/-0.4 4.9+/-0.4 3.9+/-0O.4 4.9 +/-0.3 4.5 +/-0.3

  • 4.3+/-0.3 5.1.+/-0.6
  • 3.5 +/-0.4 4.4 +/-0.3 3.4 +/-0.3 3.5 +/-0.4 4.0 +/-0.4 3.5 +/-0.4 4.2 +/-0.4 4.5 +/-0.4 4.1 +/-1.1 Q..-tR ELEMENTS AVG 3.7 +/-0.3 5.0 +/-0.5 5.6 +/-0.6 4.0 +/-0.4 3.7 +/-0.6 4.3 +/-0.3 3.9 +/-0.3 4.6+/-0.6 4.0+/-0.4 4.6 +/-0.3 4.3 +/-0.3 3.6+/-0.4 4.3 +/-0.4 4.9 +/-1.1 4.7 +/-0.4 3.8 +/-0.2 4.3 +/-0.2 4.2 +/-0.3 3.6+/-0.2 4.2 +/-0.*3 3.9 +/-0.4 3.6 +/-0.2 3.6 +/-0.3 3.6 +/-0.3 3.8 +/-0.4 3.2 +/-0.4.

2.8 +/- 0.3 4.5 +/-0.3 4.7 +/-0.5 4.2 +/-0.2 4.2 +/-0.3 4.2 +/-0.4 4.2 +/-0.2 4.7 +/-0.4 4.9 +/-0.5 3.9 +/-0.5 5.0 +/-0.2 4.5 +/-0.3 4.4 +/-0.3 5.0 +/-0.7 3.5 +/-0.3 4.5 +/-0.6 3.5 +/-0.2 3.7 +/-0.4.

3.9 +/-0.3 3.6 +/-0.5 4.4 +/-0.5 4.5 +/-0.2

TABLE C-5 2001 CONCENTRATIONS OF IODINE-131* AND GAMMA EMITTERS** IN MILK

..Resultsin Units ef pCi/. +A 2-sigma

.2.

SAMPLING PERIOD GAMMA EMITTERS STATION ID START STOPQR.

1-131 K..

40 SA-MLK-2F9 SA-MLK-11 F3 SA-MLK-14F4 SA-MLK-3G1 (C)

SA-MLK-2F9 SA-MLK-11F3 SA-M LK-14F4 SA-MLK-3G1 (C)

SA-MLK-2F9 SA-MLK-11F3 SA-MLK-14F4 SA-MLK-3G1 (C)

SA-MLK-2F9 SA-MLK-11F3 SA-M LK-14F4 SA-MLK-3G1 (C)

SA-MLK-2F9 SA-MLK-11F3 SA-MLK-14F4 SA-MLK-3G1 (C)

SA-MLK-2F9 SA-M LK-11 F3 SA-M LK-14F4 SA-MLK-3G1 (C)

SA-MLK-2F9 SA-MLK-11F3 SA-M LK-14F4 SA-MLK-3G1 (C)

SA-MLK-2F9 SA-MLK-1 1 F3 SA-MLK-14F4 SA-MLK-3G1 (C)

SA-MLK-2F9 SA-M LK-11 F3 SA-MLK-14F4 SA-MLk-3G1 (C)

SA-MLK-2F9 SA-MLK-1 1 F3 SA-MLK-14F4 SA-MLK-3G1 (C)

SA-MLK-2F9 SA-MLK-11F3 SA-M LK-14F4 SA-MLK-3G1 (C)

.01/01/2001 01/02/2001 01/02/2001 0.1/01/2001 02/05/2001

.02/05/2001 02/05/2001 02/04/2001 03/05/2001 03/05/2001 03/05/2001

'-63/04/2001 04/02/2001 04/03/2001 04/03/2001 04/02/2001 04/16/2001 04/17/2001

.04/17/2001 04/17/2001 05/06/2001 05/07/2001 05/07/2001 05/07/2001 05/22/2001 05/221/2001 05/22/2001 0/201/2002 06/03/2001 06/04/2001 06/05/2001 06/04/2001 06/25/2001 06/25/2001 06/2512001 06/24/2001 07/01/2001 07/01/2001 07/011/200 1 07/01/200 1 07/17/2001 07/17/2001 07/17/2001 07/16/2001 01/02/2001 01/03/2001 01/03/2001 01/02/2001

,02/06/2001 02/Q6/2001 02/06/2001 02/05/2001 03/06/2001

.03/06/2001 03/06/2001 03/05/2001 04/03/2001 04/04/2001 04/04/2001 04/03/2001 04/17/2001 04/18/2001 04/18/2001 04/18/2001 05/07/2001 05/08/2001 05/08/2001 05/08/2001 05/23/2001 05/23/2001 O5/2 3/2001 05/22/2002

06/04/2001 06/05/2001 06/05/2001 06/05/2001 06/26/2001 06/26/2001 06/26/2001 06/25/2001 07/02/2001 07/02/2001 07/02/2001 07/02/2001 07/18/2001 07/18/2001 07/18/2001 07/17/2001

<0.2

" <0.3

<0.2

<0.2

<0.1

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

<0.3

<0.2

<0.2

<0.2

<0.2

<0.2

<0.3

<0.2

<0.2

<0.2

<0.3

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

<0.1

<0.1

<0.2

<0.2

<0.2

<0.2

<0.1

<0.2

<0.2

<0.2

<0.2

<0.2 1250 t70 1310 +/-80 1220 +/- 100 1360 +/-70

.1340 +/-60 1320 +/-70 1390 +/-80 1340 +/-70 1390 +/-70 1410 +/-80 1370 +/-80 1320 +/-60 1350 +/-80 1370 +/-90 1340 +/-80 1390 +/-70 1330 +/-80 1360 +/- 90 1280 +/- 70 1330 +/- 70 1360 +/-70 1400 +/-70 1330 +/-90 1370 +/-60 1360 +/-80 1320 +/-70 1390 +/-90 1220 +/-70 1340 +/-60 1310 +/-50 1310 +/-50 1370 +/-+60 1390 +/-80 1370 +/-60 1350 +/-80 1270 +/-70 1430 +/-80 1370 +/- 70 1300 +/-100 1340 +/-70 1340 +/-70 1330 +/-70 1290 +/-70 1250 +/-70 59

TABLE C-5 2001 CONCENTRATIONS OF IODINE-Ibl

  • AND GAMMA EMITTERS** IN MILK Results n-ins bf 4Ci/L4+1-2 sigma SAMPLING PERIOD GAMMA EMITTERS STATION ID START STOP 1-131 K-40 SA-MLK-2F9 SA-MLK-1 1 F3 SA-MLK-14F4 SA-MLK-3G1 (C)

SA-MLK-2F9 SA-MLK-11 F3 SA-MLK-14F4 SA-MLK-3G1 (C)

SA-MLK-2F9 SA-MLK-1 1 F3 SA-MLK-14F4 SA-MLK-3G 1 (C)

SA-MLK-2F9 SA-MLK-1 1 =3 SA-MLK-14F4 SA-MLK-3G1 (C)

SA-MLK-2F9 SA-MLK-11 F3 SA-MLK-14F4 SA-MLK-3G1 (C)

SA-MLK-2F9 SA-MLK-1 1 F3 SA-MLK-14F4 SA-MLK-3G1 (C)

SA-MLK-2F9 SA-M LK-11 F3 SA-M LK-14F4 SA-MLK-3G1 (C)

SA-MLK-2F9 SA-MLK-1 1 F3 SA-MLK-14F4 SA-MLK-3G1 (C)

SA-MLK-2F9 SA-MLK-1 1 F3 SA-MLK-14F4 SA-MLK-3G1 (C) 08/06/2001 08/06/2001 08/06/2001 08/05/2001 08/20/2001 08/21/2001 08/21/2001 08/20/2001 09/03/2001 09/04/2001 09/03/2001 09/04/2001 09/17/2001 09/18/2001 09/17/2001 09/18/2001 10/01/2001 10/01/2001 10/01/2001 09/30/2001 10/21/2001 10/22/2001 10/21/2001

10/22/2001 11/12/2001 11/13/2001 11/13/2001 11113/2001 11/26/2001 11/26/2001 11/26/2001 11/27/2001 12/09/2001 12/09/2001 12/10/2001 12/09/2001 08/07/2001 "08/0712001 08/07/2001 08/061200.J 08/21/2001 08/22/2001 08/22/2001 08/21/2001 09/04/2001 09i05/2001 09/04/2001 09/05/2001 09/18/2001 09/19/2001 09/18/2001 09/19/2001 10/02/2001 10/02/2001 10/02/2001 10/01/2001 10/22/2001 10/22/2001 10/22/2001 10/23/2001 11/13/2001 11/14/2001 11/14/2001 11/1412001 11/27/2001 11/27/2001 11/27/2001 11/28/2001 12110/2001 12/10/2001 12/11/2001 12/10/2001

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

< 6.2

<0.2

<0.2'

<0.1

<0.2

<0.4

<0.2

<0.2

< 0.2

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

<0.2

<0:1

<0.2

<0.2

<0.2

<0.3

<0.2

<0.1

<0.2

<0.2

<0.3

<0.3 AVERAGE 11420 +/- 70 1420 +/-80 1280 +/-70 1220 +/-80 1380 +/-60 1330 +/-80 1320 +/- 80 1300 +/-70 130Q +/-70 1370 +/-- 70 1320 +/-60 1280 +/-t 70 1390 +/-80 1350 +/-t60 1320 +/-70 1390 +/-90 1400 -+/- 60 1460 +/-90 1230 +/-70 1350"+/-80 1380 +/-80 1350 +/-80 1240 +/-70 1230 +/-80 1450 +/-70 1380 +/-70 1270 + 90 1240 +/-60 1410 +/-80 1420 +/-80 1310 +/-70 1310 +/-90 1350 +/-80 1370 +/--80 1380 +/-80 1380 +/-70 1300 +/-100

  • Iodine-131 results are corrected for decay to midpoint of collection period & analyzed to a sensitivity of 1.0 pCi/L.
    • All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20.
      • Monthly sample collected during Jan., Feb., March and Dec., when animals are not on pasture (C) Control Station 60

TABLE C-6 2001 CONCENTRATIONS OF GROSS ALPHA AND GROSS BETA EMITTERS, AND TRITIUM IN WELL WATER Results..in Units of pCi/L +/- 2 sigma.

SAMPLING GROSS GROSS STATION ID DATE ALPHA BETA TRITIUM SA-WWA-3E1 SA-WWA-3El SA-WWA-3E1.

SA-WWA-3E1 SA-WWA-3E1 SA-WWA-3E1 SA-WWA-3E1 SA-WWA-3E1 SA-WWA-3E 1 SA-WWA-3E1 SA-WWA-3E1 SA-WWA-3E 1 01/29/2001 02/26/2001 03/2712001 04/30/2001 05/29/2001 06/25/2001 07/31/2001 08/27/2001 09/24/2001 10/30/2001 11/27/2001 12/26/2001 AVERAGE 1.8+/--1

<1.4

-2.4+/-1.1 2.6+/-1.2 2.5+/-.1.3 2.5_+/-!1.1

<1.7.

2.1 +/-1.1 2.2+/-1.2 2.1 +/--1.1 1.2+/-0.9

<1 13+/-1 11+/-0.8 10+/-0.8 1-1 +/-0.8 1.0+/-0.8 13+/-1 13+/-1 13+/- 0.9 12+/--0.9 14+/-1 13+/-1 13+/-1

<150

< 160

<160

<150

<150

<150

<160

<180

<170

<150

<160

<180 2+/-1.1 12+/-3 61

II Lii TABLE C-7 2001 CONCENTRATIONS OF GAMMA EMITTERS* IN WELL WATER Results in Units of pCi/L +1-2 sigma SAMPLING GAMMA EMITTERS ---- >

STATION ID DAtE...............

K-40 RA-NAT SA-WWA-3E1 01/29/2001

<46 193 +/-7 SA-WWA-3E 1 02/26/2001 77 +/- 26 178 +/- 5 SA-WWA-3E1 03/27/2001 74+/-251 193+/-6 SA-WWA-3E 1 04/30/2001

<45 144 +/-__

5 SA-WWA-3E1 05/29/2001

<18 154+/-5 SA-WWA-3E1 06/25/2001

<41 98+/-4 SA-WWA-3E1 07/31/2001

<28 138 +/-5 SA-WWA-3E1 08/27/2001

<16 124+/-4 SA-WWA-3E1 09/24/2001

<23 130+/- 5 SA-WWA-3E1

.10/30/2001 48+/-20 166 +/- 5 SA-WWA-3E1 11/27/2001

<16 90+4 SA-WWA-3E1 12/26/2001 85+/-35 139 +/-7 AVERAGE 146 +/-67

  • All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20.

62

TABLE C-8 2001 CONCENTRATIONS OF GROSS ALPHA ANDGROSS BETAEMITTERS AND TRITIUM IN RAW AND TREATED POTABLE WATER TYPE RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED Results SAMPLING PERIOD 1/1-3-1/2001 1/1-31/2001 2/1-28/2001 2/1-28/2001 3/1-31/2001 3/1-31/2001 4/1-30/2001 4/1-30/2001 5/1-31/2001 5/1-31/2001 6/1-30/2001 6/1-30/2001 7/1-31/2001 7/1-31/2001 8/1-31/2001 8/1-31/2001 9/1-301/2001 9/1-30/2001 10/1-31/2001 10/1-31/2001 11/1-30/2001 11/1-30/2001 121/1-31/2001 12/1-31/2001 AVERAGE RAW TREATED GRAND AVERAGE in Units of pCi/L +/- 2 sigma

. GROSS GROSS ALPHA BETA

.. +/-0.5..

3.6+/-0.5 1.1 +/-0.6 3.4+/-0.5 0.8+/-0.5 2.9+/-0.5

<1.1 3.3+/-0.5 1.3+/-0.6 3-+/-0.5 1.1 +/-0.6 3.1 +/-0.5 0.7-+/-0.5 3.4+/-0.5 0.9-+/-0.6 2.8-+/-0.5

<0.7 2.9+/-0.5

<0.8 3+/-0.5 1.4+/-0.6 4.7-+/-0.6 1.6+/-0.8 4.7_+/-0.6

<0.9 4.6+/-0.6

< 1.1 3.9 +/-0.6 0.6+/-0.5 3.5+/-0.5 1 +/-0.7 4.4+/-0.6 0.8-+/-0.6 3-+/-0.6 0.8+/-0.6 3.2+/-0.6 0.7-+/-0.5 2.7-+/-0.5 0.8+/-0.6 3_+/-0.6 0.7_+/-0.5 2.8_+/-0.5

<0.8 3.3+/-0.6 0.6-+/-0.4 3.5+/-0.6

<0.6 3.7+/-0.6 0.8+/- 0.4 1 +/-0.3 0.9 +/-0.5 3.4+/-11.3 3.5+/-11.2 3.4+/-E 1.2 63 TRITIUM

< 150

<150

<160

<160

<160

<160

<150

< 1,50

<150

<1 50

< 150

<150

<150

<160

<180

<170

< 170

<170

<160

<160

<160

<160

<170

<170

TABLE C-9 2001 CONCENTRATIONS OF IODINE-131* AND GAMMA EMITTERS**

S..

IN.RAW.kND-.TREATrI POTABLE WATER

'Results in Units -of'p/

I + /-,2 s-gm..

TYPE RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED RAW TREATED AVERAGES RAW TREATED GRAND AVERAGE 32_+/-35

  • Iodine-1 31 analyzed to a sensitivity of 1.0 pCi/L.

All other gamma emitters searched for were < LLD; typical LLDs are given in Table C-20.

64 SAMPLING PERIOD 1/1-31/2001 1/1-31/200f' 2/1-28/2001 2/1-28/2001 3/1-31/2001 3/1-31/2001 4/1-30/2001 4/1-30/2001 5/1-31/2001 5/1-31/2001 6/1-30/2001 6/1-30/2001 7/1-3 ff2001 7/1-31/2001 8/1-31/2001 8/1-31/2001 9/1-30/2001 9/1-30/2001 10/1-31/2001 10/1-31/2001 11/1-30/2001 11/1-30/2001 12/1-31/2001 12/1-31/2001 1-131

<0.2

<0.3

<0.2

<0.2

<0.3

<0.3'

<0.1

<0.2

<0.2

<0.4

<0.1

<0.2

<0.2

<0.2

<0.3

<0.2

<0.3

<0.2

<0.2

<0.2

< 0,14

<0.3

<0.2

<-----GAMMA EMITTERS -----

K-40 RA-NAT 33+/-13

<3.5 701.+/-18

<2.6

<17

<3.4

<13 6.5+/-1.2 61 +/-18

<1.7

<14

<1.8 46 +/- 17

<2.1 29+/-14

< 1.9

<14

<1.9

<16

<2.2

<33

<1.6

<7

<2

<14

<1.6

< 1.3

< 2.2 61 +/-15

<2.3

<.16 5 +/-2.2

<14 4+/-1.4 50'+/- 16

< 3-.2 40+/-18

<1.9 34+/-13

<4.5

<17

<1.7

<16 6.1 +/-2.6 31 +/-13

< 1.8 26+/-11 5.4+/-_2

TABLE C-10 2001 CONCENTRATIONS OF GAMMA EMITTERS* IN VEGETABLES Results in Units of. pCi/kg (Wet) +÷/-

2 sigma SAMPLING

<--- GAMMA EMITTERS --- >

STATION ID DATE SAMPLE TYPE, K-40 Ra-NAT SA-FP-29..

04/23/2001 Asparagus 2470 +/- 260

<15 SA-FPV-2G2 (C" 05/07/2001 Asparagus 2480+/-100

< 9.6 AVERAGE 2400-+

SA-FPL-14F3 07/24/2001

Cabbage, 1860+/-140

< 5.8 SA-FPL-3H5 (C) 07/18/2001 Cabbage 2510+/-140

<9.8 SA-FPL-6F2 07/23/2001 Cabbage 2190+/-140

<8.7 AVERAGE 2190+/-650 SA-FPV-2F4 07/18/2001 Corn 2490+/-180

<7.7 SA-FPV-2F9 07/18/2001 Corn 2470+/-160

< 6.7 SA-FPV-1G1 (C) 07/10/2001 Corn 2710+/- 90

< 5.8 SA-FPV-3H5 (C) 07/18/2001 Corn 2430+/-100

< 9.2 SA-FPV-2G2 (C) 07/18/2001 Corn 2440+/-160

< 7.1 SA-FPV-14F3 07/24/2001 Corn.

2140+/-170

<6.8 SA-FPV-14G2 (C) 07/17/2001 Corn 2620+/-170

< 7.3 AVERAGE 2470+/-360 SA-FPV-2F4 07/23/2001 Peppers 1700+/-140

< 8.6 SA-FPV-3F5 07/18/2001 Peppers 1440+/-160

< 8.5 SA-FPV-1G 1 (C) 07/18/2001 Peppers 1500+/-160

< 9.3 SA-FPV-3H5 (C) 07/18/2001 Peppers 1230+/- 150

<11 SA-FPV-2G2 (C) 07/18/2001 Peppers 1380+/-100

< 9.3 SA-FPV-9G1 (C) 07/24/2001 Peppers 1480 +/- 130

< 8 SA-FPV-6F2 07/23/2001 Peppers 1420+/-140

< 8.7 AVERAGE 1450+28260 SA-FPV-2F4 07/24/2001 Tomatoes 2090+/-150

< 6.8 SA-FPV-2F9 07/24/2001 Tomatoes 1930+/- 130

<6.9 SA-FPV-3F5 07/18/2001 Tomatoes 2000+/-80

< 7.9 SA-FPV-1G1 (C) 07/18/2001 Tomatoes 1900+/-210

<7.2 SA-FPV-3H5 (C) 07/18/2001 Tomatoes 1930+/- 150

<7.4 SA-FPV-2G2 (C) 07/18/2001 Tomatoes 2160+/-150

< 6.9 SA-FPV-9G1 (C) 07/24/2001 Tomatoes 1810+/- 150

< 7.2 SA-FPV-6F2 07/2312001 Tomatoes 2570+/- 80 16 +/- 3 SA-FPV-14G2 (C) 07/24/2001 Tbmatoes 2290+/-160

< 6.6 SA-FPV-14F3 07/24/2001 Tomatoes 2500+/-90

< 5.4 AVERAGE 2120+/- 520 GRAND AVERAGE 2070+/-870 SAll other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20 (C) Control Station 65

TABLE Cý,i1 2001 CONCENTRATIONS Of GAMMA EMITTERS* IN GAME Results in Units of pCi/kg (wet) +1-2 sigma SAMPLING GAMMA EM.ITTER5.

STATION ID DATE SAMPLE TYPE K-40 SA-GAM-11 D1 (C)

SA-GAM-3E1 02/26/2001 02/20/2001 AVERAGE Muskrat Muskrat Muskrat 2840 +/-160 2600+/-190 2720+/-340

  • All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20.

66

TABLE C-1-2 2001 CONCENTRATIONS;OF GAMMA-EMITT*ERS* iN FODDER CROPS Results in Units of pCi/kg (wet) +1-2 sigma SAMPLING

<- GAMMA EMITTERS ->

"STATION ID DATE --

SAM PLE IYPE be-7 K-40 Ra-NAT SA-VGT-2F9 SA-VGT-3G1 (C)

SA-VGT-14F4 SA-VGT-11 F3 AVERAGE SA-VGT-1 1 F3 SA-VGT-14F4 10/22/2001 10/30/2001 10/22/2001 10/30/2001 Silage Silage Silage Silage 670+/-_70 350+/-70 370 +/- 60 210+/-_50 2560+/-150 4380+/-180 2920+/-160 4990 +/-220

<10 10_+/-5

<5

<8 400+/-390 3710+/-2320 10/30/2001 11/1412001 Soybeans Soybeans

<40

<30 AVERAGE 14900+/-_320 16800_+/-310 15900+/- 2700

<10 20_+/-6 15_ _14

  • All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20.

(C) Location 3G1 is the Control Station.

67

TABLE C-13 2001 CONCENTRATIONS OF GAMMA EMITTERS* IN SOIL Results in Units of pCi/kg (dry) +/- 2 sigma SAMPLING STATION ID DATE Be-7 K-40 Cs-137 Ra-NAT Th-232 SA-SOL-6S2 SA-SOL-2F7 SA-SOL-2F9 SA-SOL-5F1 S.L:j-SOL-10DI1 SA-SOL-14F4 SA-SOL-16E1 SA-SOL-1 1 F3 SA-SOL-3G 1 (C) 05/15/2001 05/16/2001 05/15/2001 05/15/2001 05/14/2001 05/15/2001 05/15/2001 05/15/2001 05/16/2001

<110

<85 120+/-54 150+/- 56

<70

<130

<120 360+/-130

< 140 5540 +/- 220 7910+/-+300 6100+/- 140 4610+/-130 9070+/-290 12900 +/- 380 11900 +/- 290 12800 +/- 390 8190+/- 250 GRAND AVERAGE 8780+/-6290 190+/-220 660+/-450 800+/-550

  • All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20 (C) Control Station 68 26+/-7 290 +/- 18 240+/-9 260+/-9 350+/-19 180*+/- 12 110+/-13

<49 160+/-13 260+/-+15 590 +/- 23 490+/-11 550 +/-12 850+/- 27 910+/-22 660_+/-16 970+/-29 700+/-16 350 +/-40 710+/--51 530 +/- 24 620 +/- 31 990+/- 50 1090+/- 54 840+/-60 1200 +/- 54 850 +/- 57

TABLE C-14 2001 CONCENTRATIONS OFGROSS BETA EMITTERS IN SURFACE WATER Results in Units of pCi/L +/- 2 sigma STATION ID --------.......................................... >

SAMPLING SA-SWA-11 Al SA-SWA-1 2C1 SA-SWA-1 6F1 SA-SWA-1 F2 SA-SWA-7E1 AVERAGE DATE (Control)

January February March April May C'

June July August September October November December AVERAGE 114+/-7 78+/-6 89 +/- 6 16+/-3 41 +/-4 56+/-5 71 +/-6 80+/-6 128+/-9 163+/-9 156+/-12 150+/-12 95 +/- 95 86+/-6 75 +/- 6 77+/-6 6+/-+2 33+/-4 29+/-4 43+/-5 67+/-6 85+/-7 129+/-8 112+/-10 108-+/--11 71 +/-74 72+/-5 44+/-4 58+/-_5 5+/-2 25+/-3 20-+/-3 32+/-4 48+/-5 79+/-6 114+/-7 109+/-10 111_+/-11 60 +/- 75 61 +/-5 33+/-4 40+/-4 5+/-2 21+/-3 23+/-3 23+/-4 57-5 77-+/-6 100+/-7 108 +/-10 100-+/-10 54+/-71 126+/-8 98+/- 7 122+/-8 34+/-4 66+/-5 60+/-5 99+/-7 104+/--7 138+/-9 224.+/- 11 167 +/-12 173+/-13 92+/- 55 66 +/- 53 77 +/-62 13+/-25 37 _36 37 #t38 53+/-62 71 -43 101 +/-58 146 +/-99 130-+/--57 128+/-63 118+/-106 GRAND AVERAGE 79++/-95 y

4

TABLE'C-I 5 2001 CONCENTRATIONS OF GAMMA EMITTERS* IN SURFACE' WATER Results in Units of pCi/L +/- 2 sigma SAMFLING GAMMA EMITTERS STATION ID DATE K-40 SA-SWA-1 F2 SA-SWA-7E1 SA-SWA-11 Al SA-SWA-1 2C1 (C)

SA-SWA-1 6F1 SA-SWA-1 F2 SA-SWA-7E1 SA-SWA-11 A1 SA-SWA-12C1 (C)

SA-SWA-1 6F1 SA-SWA-1 F2 SA-SWA-7E1 SA-SWA-11 A1 SA-SWA-12C1 (C)

SA-SWA-16F1 SA-SWA-1 F2 SA-SWA-7E1 SA-SWA-11 A1 SA-SWA-i 2C1 (C)

SA-SWA-1 6F1 SA-SWA-1 F2 SA-SWA-7E1 SA-SWA-11 A1 SA-SWA-12C1 (C)

SA-SWA-16F1 SA-SWA-1 F2 SA-SWA-7E1 SA-SWA-1 lA1 SA-SWA-12C1 (C)

SA-SWA-1 6F1 SA-SWA-1 F2 SA-SWA-7 E1 SA-SWA-11A1 SA-SWA-i 2C1 (C)

SA-SWA-16F1 01/08/2001 01/08/2001 01/08/2001 01/08/2001 01/08/2001 02/06/2001 02/06/2001 02/06/2001 02/06/2001 02/06/2001 03/08/2001 03/08/2001 03/08/2001 03/08/2001 03/08/2001 04/06/2001 04/06/2001 04/06/2001 04/06/2001 04/06/2001 05/11/2001 05/11/2001 05/11/2001 05/11/2001 05/11/2001 06/06/2001 06/06/2001 06/06/2001 06/06/2001 06/06/2001 07/03/2001 07/03/2001 07/03/2001 07/03/2001 07/03/2001 70 60+/-_19 120+/-22 137+/-_21 85+/--19 62 +/- 25 80+/-24 131 +/-21 1_18+/-28 61+/-20 68+/- 22 73 +/- 20 101 +/-23 103 +/-25 134-+/-23 53+/--18 43-+/-19 65+/-_18 58_+/- 19 38 +/-13 58 +/- 23 42+/-19 75 +/-21 54+/- 20

<21

<28

<23 71 +/-15 101 +/-20 87+/-12 72+/- 20 64+/-17 102-+/-19 88_+/-18 67_+/-16 74+/-17

TABLEC-15 2001 CONCENTRATIONS. OF GAMMA EMITTERS*. INSURFACE WATER Results in Units. of pCi.L0 1-*/- 2-sigma SAMPLING GAMMA EMITTERS STATION !P.

DA' K,40 SA-SWA-1 F2 SA-SWA-7E1 SA-SWA-1 1 Al SA-SWA-i 2C1 (C)

SA-SWA-1 6F1 SA-SWA-1 F2 SA-SWA-7E1 SA-SWA-11 A1 SA-SWA-1 2C1 (C)

SA-SWA-1 6F1 SA-SWA-1 F2 SA-SWA-7E1 SA-SWA-11 A1 SA-SWA-i 2C1 (C)

SA-SWA-1 6F1 SA-SWA-1 F2 SA-SWA-7E 1 SA-SWA-11A 1 SA-SWA-i 2C1 (C)

SA-SWA-116F1 SA-SWA-1 F2 SA-SWA-7 E1 SA-SWA-11 A1 SA-SWA-1 2C1 (C)

SA-SWA-1 6F1 08/08/2001 08/08/2001 08/08/2001 08/08/2001 08/08/2001 09/03/2001 09/03/2001 09/03/2001 09/03/2001 09/03/2001 10/03/2001 10/03/2001 10/03/2001 10/03/2001 10/03/2001 11/13/2001 11/13/2001 11/13/2001 11/13/2001 11/13/2001 12/10/2001 12/10/2001 12/10/2001 12/10/2001 12/10/2001 AVERAGE

  • All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20.

C) Control Station 71 92+/-19 111+/-21 93+/-19 102+/-19 75+/-16 50+/-18 117+/-_22 162_+/-20 79_+/-14 74+/-22 112+/-20 101 +/-23 178 +/-28 107 +/-23

<14 79_+/-19 153 +/-18 101 +/-23 165 +/-25 124+/-_16 110+/-_21 176+/- 24 138_+/-20 164+/-32 144+/--29 91 +/-79

TABLE C-16 2001 CONCENTRATIONS OF TRITIUM IN QUARTERLY COMPOSITES OF SURFACE WATER Results in Units of pCi/L +/- 2 sigma STA TIO N ID ----------------------------------

SAMPLING SA-SWA-1 1A1 SA-SWA-12C1 SA-SWA-16F1 SA-SWA-1F2 SA-SWA-7E1 AVERAGE PERIOD (Control) 01 /08/2001 to

< 150

< 160

< 160

< 160

< 150 03/08/2001 04/06/2001 to

< 160

< 160

< 160

< 160

-<150 06/06/2001 07/03/2001 to

< 190

< 170

< 170

< 170

<170 09/03/2001 10/03/2001 to

<150

< 160

< 160

< 160

< 160 12/10/2001

TABLE C-17 2001 CONCENTRATIONS OF STRONTIUM-89, STRONTIUM-90*

AND GAMMA EMITTERS** IN EDIBLE FISH Results in Units of pCi/kg (wet) +/- 2 sigma (Strontium in bone is reported in pCi/kg (dry))

STRONTIUM GAMMA EMITTERS BONE -------

(FLESH)

SAMPLING STATION ID PERIOD Sr-89 Sr-90 K-40 SA-ESF-7E1 SA-ESF-11 A1 SA-ESF-1 2C1 (C) 5/14-16/2001 5/14-16/2001 5/14-16/2001

< 600

<130 AVERAGE SA-ESF-7E1 SA-ESF-11 Al SA-ESF-12C1 (C) 9/12-13/2001 9/12-13/2001 9/12-13/2001 AVERAGE GRAND AVERAGE 3390+/- 220 3240+/-190 3700+/-180 3440+/-470 3580+/-210 3910+/-100 3650+/-190 3710+/- 350

'3580+/-470

  • Strontium results for one location for the first semi annual collection are analyzed and reported by Duke Engineering & Services Environmental Laboratory as MDC.

This is done as a management audit sample.

    • All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20 (C) Control Station 73

TABLE C-18 2001 CONCENTRATIONS OF GAMMA EMITTERS* IN CRABS Results in Units of pCi/kg (wet) +1-2 sigma GAMMA EMITTER "SAMPLING (FLESH)

STATION ID PERIOD K-40 SA-ECH-1 1 A1 SA-ECH-12C1 (C) 07/16-19/2001 07/16-19/2001, AVERAGE SA-ECH-1 1A1 SA-ECH-12C1 (C) 09/11-13/2001 09/11-13/2001 AVERAGE 2590+/-210 GRAND AVERAGE 2790 +/- 510

  • All other gamnma emitters searched for were < LLD; Typical-LLDs are given in Table C-20.

(C) Control Station 74 2910+/-190 3080+/-200 3000+/-240 2510+/- 220 2660+/-160

-ý I I

TABLE C-19 2001 CONCENTRATIONS OF GAMMA EMITTERS* IN SEDIMENT Results in Units of pCi/kg (dry) +/- 2 sigma SAMPLING GAMMA EMITTERS STATION ID DATE Be-7 K-40 Co-60 Cs-134 Cs-1 37 RA NAT Th-232 SA-ESS-6S2 SA-ESS-11A1 SA-ESS-15A1 SA-ESS-16A1 SA-ESS-1 2C1 (C)

SA-ESS-7E1 SA-ESS-16F1 07/02/2001 06/27/2001 06/27/2001 06/27/2001 06/27/2001 06/27/2001 06/27/2001

<110 870 +/- 150

< 250 220 +/- 100

<78

<80 820 +/- 120 1020 +/- 140 15600+/-400 9310 +/- 300 15100+/-410 15600 +/- 440 12600 +/- 330 15100 +/- 350 12000+/-10700 45+/-81 540+/-420 780+/-360 SA-ESS-6S2 SA-ESS-11 A1 SA-ESS-1 5A1 SA-ESS-16A1 SA-ESS-1 2C1 (C)

SA-ESS-7E1 SA-ESS-16F1 AVERAGE 10/22/2001 10/10/2001 10/10/2001 10/10/2001 10/10/2001 10/10/2001 10/10/2001

<40

<76 370 +/- 120 480+/-160 350 +/- 63

<55

<79 1570+/- 94 13800 +/- 350 11200+/-410 15900+/-430 15600 +/- 220 12000 +/- 290 15400 +/- 470

<2.8

<22

<11

<15

<11

<13

<14

<1.8

<5.7

<6.4

<5.4

<7.2

<3.9

<6.4 12200 +/-10100 12100 +/-10000 GRAND AVERAGE

<3.7 50+/-14 38+/-12 76 +/-16 58+/-9.2 19+/-7.1 67+/- 21 96 +/- 6.8 660+/- 19 580+/-20 630+/-26 820 +/- 13 570+/-14 660 +/- 32 45+/-52

-570+/-450 92+/-18 S790 +/-41 750::+/- 58

-880+/-.54 1100: 30 620 +/-:37 1130+/-72 880+/-400 45 +/- 66 560+/-420 830+/-380

  • All other gamma emitters searched for were <LLD; typical LLDs are given in Table C-20 (C) Control Station AVERAGE

<2

<8

<10

<10

<11

<9

<20

<2.2 19 +/-6.9

<4.9

<5.9

<4.8 27+/- 8.2

<6.8

<4.1 72+/-11 44+/-11 120+/-16

<7.6

<23 46 +/- 9.6 98+/-9.2 630+/-17 530 +/- 20 620+/-23 550+/- 19 760+/-19 570+/-1,6 82 +/- 20 840 +/- 49 660 +/-49 990 +/- 60 480 +/- 89 840 +/- 60 860 +/-49

TABLE C-20 2001 MAPLXWOOD TESTING SERVICES LLDs, FOR GAMMO.

"SPECTROMETRY SAMPLE TYPE:

< ---------- AIR

I R-WATER ----------

MILK-......... >

IODINE PARTICULATES GAMMA SCAN IODINE GAMMA SCAN IODINE ACTIVITY:

10-3 pCi/m3 10-3 pCi/m3 pCi pCi/L pCi/L pCi/L GEOMETRY:

47 ML 13 FILTERS 3.5 LITER 100 ML 3.5 LITER 100 ML COUNT TIME:

120 MINS 500 MINS 1000 MIN 1000 MINS 500 MINS 1000 MINS DELAY TO COUNT:

2 DAYS 5 DAYS

.7 DAYS-3 DAYS 2 DAYS 2 DAYS NUCLIDES BE-7 7.2 7.8 18 NA-22 1.2 8

6.7 K-40 7.0 30 50 CR-51 1.8 9.1 14 MN-54 0.22 1.2 3.6 CO-58 0.30 1.3 2.8 FE-59 0.80 1.6 10.3 CO-60 0.39 1.3 5.6 ZN-65 0.70 2.1 12 ZRNB-95 0.57 2.0 4.5 MO-99 27 60 27 RU-103 0.30 1.2 1.9 RU-106 3.0 9.5 18 AG-II1M 0.45 2.3 3.3 SB-125 0.66 2.7 5.1 TE-129M 8.0 47 81 1-131.

9.5 0.52 2.5 0.3 2.0 0.4 TE-132 0.6 4.3 1.7 BA-133 0.29 1.6 1.8 CS-134 0.34 1.3 1.6 CS-136 0.54 1.9 3.0 CS-137 0.44 2.4 3.7 BALA-140 1.3 3.8 7.5 CE-141 0.25 1.3 2.5 CE-144 0.65 7.5 9.8 RA-NAT 0.57 2.9 5.4 TH-232 5 5.0 11 37 76

TABLE C-2 0 (-Cont ' d) 2001 MAPLEWOOD ' TEETIN

'SERVICES L.LDe FOR GOAMA;,S3PECTROMETRY SAMPLE TYPE:

FOOD PRODUCTS VEGETATION GAME FISH & SHELLFISH SEDIMENT & SOIL ACTIVITY:

pCi/kg WET pCi/kg WET pCi/kg WET pCi/kg WET pCi/kg DRY GEOMETRY:

500 ml 3.5 LITER 500 ml 500 ml 500 ml COUNT TIME:

500 MINS 500 MINS 500 MINS 500 MINS 500 MINS DELAY TO COUNT:

3 DAYS 7 DAYS 5 DAYS 5 DAYS 30 DAYS NUCLIDES 50 13 70 32 10 6.6 27 17.5 17 11 104 5.2 114 BE-7 NA-22 K-40 CR-51 MN-54 CO-58 FE-59 CO-60 ZN-65 ZRNB-95 MO-99 RU-103 RU-106 AG-IlOM SB-125 TE-129M 1-131 TE-132 BA-133 CS-134 CS-136 CS-137 BALA-140 CE-141 CE-144 RA-NAT TH-232 14 11 225 5.8 7.0 5.4 4.9 8.6 9.1 26 6.1 20 15 34 35 13 70 28 6.0 5.0 16 7.8 13 11.0 49 5.0 36 7.0 9.9 286 4.0 3.9 4.0 4.2 4.2 7.9 12.6 5.0 16 14 35 32 14.4 70 28 5.8 5.0 14.1 5.5 12.0 8.0 20 3.2 35 7.5 II 157 6.2 9.0 3.7 4.2 6.1 6.1 20 5.0 19.6 8.0 40.0 82 12 70 32 5.0 6.0 10 12 10 8.1 272 5.5 36 8.9 6.4 207 6.4 5.1 6.4 6.4 6.1 7.2 13.4 4.4 14.0 8.2 41 80 14 70 127 30 19 49 22 22 34 166000 14 81 39 29 470 108 5600 12 27 70 33 143 21 5o 45 50 77

APPENDIX D

SUMMARY

OF RESULTS FROM ANALYTICS AND ENVIRONMENTAL RESOURCE ASSOCIATES INTERLABORATORY COMPARISON PROGRAMS 79

APPENDIX D

SUMMARY

OF RESULTS FOR ANALYTICS AND ENVIRONMENTAL RESOURCE ASSOCIATES INTERLABORATORY COMPARISON PROGRAM Appendix D presents a summary of the analytical results for the 2001 Analytics and Environmental Resource Associates (ERA)

Interlaboratory Comparison Program.

TABLE OF CONTENTS TABLE NO.

D-1 D-2 D-3 D-4 TABLE DESCRIPTION Gross Alpha and Gross Beta Emitters in Water....

Gamma Emitters in Water and Milk.................

Gamma Emitters in Air and Soil...................

Tritium Analysis in Water and Iodine in Air......

PAGE 82 83 84 85 81

TABLE D-1 RESULTS FOR ANALYTICS AND ERA INTERLABORATORY COMPARISON PROGRAM Gross Alpha and Gross Beta Emitters In Water (pCi/L)

DATE MM-YY 06-2001 PSEG SAMPLE CODE ANL-WAT-AB529 07-2001 ERA-WAT-AB528 12-2001 ANL-WAT-AB539 MEDIUM Water Water Water ANALYSIS Alpha Beta Alpha Beta Alpha Beta PSEG Mean +/- s.d.

33+/-2 321+4 29+/-1.2 60+/-2.9 51+/-3 269+/-9 ANALYTICS ERA Known 35 248 18 53 72 214 ANALYTICS/ERA Acceptance Criteria Lower & Upper Limit Limit 25 45 176 320 9.3 26.7 35.7 70.3 48 96 148 280

  • s.d.

one standard deviation of three individual analytical results 83

TABLE D-2 RESULTS FOR ANALYTICS AND ERA INTERLABORATORY COMPARISON PROGRAM Gamma Emitters In Water and Milk (pCi/L)

ANALYTICS/ERA Acceptance ANALYTICS Criteria DATE PSEG PSEG ERA Lower & Upper MM-YY SAMPLE CODE MEDIUM ANALYSIS Mean +/- s.d.

Known Limit Limit 0J-0uul ANL-WAT-G524 Water 03-2001 ANL-MLK-G526 Milk 06-2001 ERA-WAT-G528 12-2001 ANL-WAT-G541 Water Water Cr-51 Mn-54 Fe-59 Co-60 Zn-65 1-131 Cs-137 Ce-141 Cr-51 Mn-54 Fe-59 Co-60 Zn-65

.1-131 Cs-134 Cs-137 Ce-141 Ba-133 Co-60 Cs-134 Cs-137 Zn-65 Cr-51 Mn-54 Fe-59 Co-60 Zn-65 1-131 Cs-134 Cs-137 Ce-141 270+19 112+/-2 100+2 162+6 211+6 98+/-2 112+2 105+2 436+/-19 186+/-6 162+7 256+7 346+/-10 79+5 195+/-6 181+1 165+/-3 36+/-1.2 48+/-1.5 16+/-0.6 203+/-1 37+/-1.5 284+5 89+/-3 71+/-3 2 06+/-6 127+14 97+5 101+/-7 196+/-6 227+8 242

.101 84 147 186 90 102 94 418 175 146 254 322 77 223 176 162 36 47 16 197 36 293 88 60 209 122 93 117 188 224 170 71 60 105 132 60 72 64 292 121 104 176 226 53 157 63 114 27.3 38.3 7.3 160 27.3 203 64 42 149 86 63 81 134 158 314 131 108 189 240 120 132 124 544 229 188 332 418 101 289 230 210 44.7 55.7 24.7 214 44.7 383 112 78 269 158 123 153 242 290

  • s.d. -

one standard deviation of three individual analytical results 84

TABLE D-3 RESULTS OF ANALYTICS AND ERA. INTERLA1ORATORY COMPARISON PROGRAM Gamma Emitters In-Soil-(pCi/Kg-dry) and Air Particulate Samples (pCi/m3 )

ANALYTICS/ERA Acceptance ANALYTICS Criteria DATE PSEG PSEG ERA Lower & Upper MM-YY SAMPLE CODE MEDIUM ANALYSIS Mean + s.d.

Known Limit Limit 03-2001 ANL-SOL-G525 06-2001 ANL-APT-G531 09-2001 ANL-SOL-G536 Soil APT Soil Cr-51 Mn-54 Fe-59 Co-60 Zn-65 Cs-137 Ce-141 Cr-51 Mn-54 Co-60 Fe-59 Zn-65 Cs-134 Cs-137 Co-58 Ce-141 Cr-51 Mn-54 Co-60 Fe-59 Zn-65 Cs-134 Cs-137 Ce-141 470+24 208+/-9 180+/-4 284+4 353+11 316+/-9 172+7 237+10 156+/-7 132+4 99+6 193+10 108+3 128+4 192+/-4 175+/-12 439+/-13

.237+4 292+2 113+/-5 271+/-16 172+5 437+59 135+/-14 479 201 167 291 369 328 186 210 141 127 82 170 125 114 90 153 404 226 294 95 281 177 480 134 335 141 119 201 261 232 132 144 99 91 58 116 89 78 60 105 284 160 198 65 197 123 336 92 623 261 215 381 477 424 240 276 183 163 106 224 161 150 120 201 524 292 390 125 365 231 624 176

  • s.d.

- one standard deviation of three individual analytical results 85

TABLE D-4 RESULTS OF ANALYTICS AND ERA INTERLABORATORY COMPARISON PROGRAM Tritium Analysis In Water (pCi/L)

And Iodine In Air Samples (pCi/m3 )

AV...... P"*,

-A Acceptance Criteria Lower & Upper Limit Limit 2178 4050 60 120 56 104 5244 9744 50 86 2113 3347

-6.6 21.9 62 122 9842 18278 PSEG SAMPLE CODE ANL-WAT-H523*

ANL-AIO-I527 ANL-AIO-I530 ANL-WAT-H532 ANL-AIO-I535 ERA-WAT-H534 ERA-WAT-1538 ANL-AIO-I540 ANL-WAT-H542 MEDIUM Water AIO AIO Water AIO Water Water AIO Water ANALYSIS H-3.

1-131 1-131 H-3 1-131 H-3 1-131 1-131 H-3 PSEG Mean +

s.d.

3,145+/-~171' 90+/-0 77+1 7890+/-85 64+4 2719+/-36 6.6+0.4 96+5 14950+417 ANALYTICS ERA Known 3114 90 80 7494 68 2730 7.7 92 14060

  • s.d. -

one standard deviation of three individual analytical results 86 DATE MM-YY 03-2001 03-2001 06-2001 06-2001 09-2001 08-2001 10-2001 12 -2001 12-2001

APPENDIX E SYNOPSIS OF LAND USE CENSUS 87

APPENDIX E SYNOPSIS OF 2001 LAND USE CENSUS A land use census was conducted 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 50m2 (500ft 2) producing broad leaf vegetation, in each of the 16 meteorological sectors.

Tabulated below are the results of these surveys:

Meteorological Sector Milk Animal July, 2001 km (miles)

Nearest Residence July, 2001 km (miles)

Vegetable Garden July, 2001 km (miles)

None None None None None None None None None None None None 7.8 (4.9)

None None None None None 6.4 (4.0) 5.8 (3.6) 5.4 (3.4)

None None None None 5.5 (3.4) 6.9 (4.3) 7.1 (4.4) 6.5 (4.0) 5.5 (3.4) 5.9 (3.7) 6.8 (4.2) 89 N

NNE NE ENE E

ESE SE SSE S

SSW SW WSW W

WNW NW NNW None None None None None None None None None None None None None None None None

Retrieved from "https://kanterella.com/w/index.php?title=ML021330145&oldid=5438936"