ML093340219
| ML093340219 | |
| Person / Time | |
|---|---|
| Site: | Susquehanna, Bell Bend  |
| Issue date: | 05/07/2004 |
| From: | Shriver B PPL Bell Bend, Susquehanna |
| To: | Office of New Reactors |
| Shared Package | |
| ML093270273 | List: |
| References | |
| BNP-2009-356 | |
| Download: ML093340219 (182) | |
Text
Bryce L Bryce Shriver L Shriver PPL Susquehanna, PPL Susquehanna, LLC LLC Senior Vice President Senior Vice President and and 769 Salem 769 Salem Boulevard Boulevard Chief Nuclear Chief Nuclear Officer Officer Berwick, PA Berwick, PA 18603 18603 Tel. 570.542.3120 Tel. 570.542.3120 Fax Fax 570.542.1504 570.542.1504 blshriver@pplweb.com blshriver@pplweb.com MAY 07 MAY 07 2004 2004 U. S. Nuclear U. S. Nuclear Regulatory Regulatory Commission Commission Attn: Document Attn: Document Control Control Desk Desk Mail Station Mail OPI-I7 Station OPI-I7 Washington, DC Washington, DC 20555 20555 SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRICELECTRIC STATIONSTATION ANNUAL RADIOLOGICAL ENVIRONMENTAL ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT OPERATING REPORT Docket Nos.
Docket Nos. 50-387 50-387 PLA-5748 PLA-5748 and 50-388 and 50-388 The Susquehanna SES The Susquehanna SES Annual Annual Radiological Radiological Environmental Environmental Operating Operating Report Report is is hereby submitted hereby submitted for for the the calendar calendar yearyear 2003 2003 in in accordance accordance with with Technical Technical Specification Section Specification Section 5.6.2.
5.6.2.
If you If you have have any any questions, questions, please please contact contact Mr.
Mr. Rocco Rocco R. R. Sgarro Sgarro at at (610)
(610) 774-7552.
774-7552.
Sincerely, Sincerely, Attachments Attachments copy: NRC copy: Region II NRC Region Mr. R.
Mr. R. V.
V. Guzman, Guzman, NRC NRC Project Project Manager Manager Mr. S.
Mr. S. Hansell, Hansell, NRC NRC Sr. Sr. Resident Resident Inspector Inspector Mr. R.
Mr. R. Janati, Janati, DEPIBRP DEPIBRP
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'Electric Station Units 1 & 2 2003 ANNUAL 2003 ANNUAL REPORT, REPORT, Annual Annual Radiological
.Radiological Environmental Environmental
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SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION STATION ANNUAL RADIOLOGICAL ANNUAL ENVIRONMENTAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT OPERATING REPORT REPORT PERIOD:
REPORT 12/30/02 -1/30/04 PERIOD: 12/30/02 -1/30/04 Prepared by:
Prepared by:
F.~£~~
Health Physicist Health Physicist II Reviewed by:
Reviewed by:
R.E.
R.E. Doebler Doebler Chemistry Chemistry Support Support Supervisor Supervisor -- SSES SSES Approved by:
Approved by: (I r4&..$3 B.~~l Manager -- Plant Manager Plant Chemistry Chemistry PPL Susquehanna, LLC PPL Susquehanna, LLC 769 Salem 769 Salem Boulevard Boulevard Berwick, Pennsylvania Berwick, Pennsylvania 18603 18603
TABLE OF TABLE OF CONTENTS CONTENTS
SUMMARY
AND
SUMMARY
AND CONCLUSIONS CONCLUSIONS ........................................................................................
........................................................................................ 1 1
INTRODUCTION ......................................................................................................................
INTRODUCTION ...................................................................................................................... 5 5
AMBIENT RADIATION AMBIENT RADIATION MONITORINGMONITORING ..............................................................................
.............................................................................. 16 16 AQUATIC PATHWAY AQUATIC PATHWAY MONITORINGMONITORING ................................................................................
................................................................................ 20 20 ATMOSPHERIC PATHWAY ATMOSPHERIC PATHWAY MONITORING MONITORING ......................................................................
...................................................................... 33 33 TERRESTRIAL PATHWAY TERRESTRIAL PATHWAY MONITORING MONITORING .......................................................................
....................................................................... 37 37 GROUND WATER GROUND WATER MONITORING MONITORING .......................................................................................
.......................................................................................42 42 REFERENCES ........................................................................................................................
REFERENCES ........................................................................................................................44 44 APPENDICES APPENDICES A.
A. 2003 REMP 2003 REMP CHANGES CHANGES A-I A-I B.
B. 2003 REMP 2003 REMP MONITORING MONITORING SCHEDULE SCHEDULE (SAMPLING (SAMPLING AND AND ANALYSIS)
ANALYSIS) B-1 B-1 C.
C. 2003 REMP 2003 REMP MONITORING MONITORING LOCA LOCAnON nON DESCRIPTIONS DESCRIPTIONS C-l C-l I
D.
D. 2003 LAND 2003 LAND USE USE CENSUS CENSUS RESULTS RESULTS D-I D-I E.
E.
SUMMARY
DESCRIPTION
SUMMARY
DESCRIPTION OF OF SSES SSES REMP REMP ANALYTICAL ANALYTICAL E-I E-I METHODS METHODS F.
F. 2003 EXCEPTIONS TO 2003 EXCEPTIONS TO THE THE SSES SSES TECHNICAL TECHNICAL F-I F-I REQUIREMENTS SAMPLE REQUIREMENTS SAMPLE SCHEDULE, SCHEDULE, METHODS METHODS AND ANALYSIS AND ANALYSIS SENSITIVITIES SENSITIVITIES G.
G. 2003 SSES 2003 SSES REMP REMP
SUMMARY
SUMMARY
OF OF DATA DATA G-l G-l H.
H. COMPARISON COMPARISON OF OF INDICATOR INDICATOR AND AND CONTROL CONTROL 2003 2003 H-l H-l REMP ANNUAL REMP ANNUAL MEANS MEANS FOR FOR SELECTED SELECTED MEDIA MEDIA ANALYSIS RESULTS ANALYSIS RESULTS WITH WITH MEANS MEANS FROM FROM PREOPERATIONAL AND PREOPERATIONAL AND PRIOR PRIOR OPERATIONAL OPERATIONAL PERIODS PERIODS 1.
- 1. SPECIFIC ANALYSIS RESULTS SPECIFIC ANALYSIS RESULTS TABULATED TABULATED BY BY MEDIA MEDIA I-I I-I AND SAMPLING AND SAMPLING PERIOD PERIOD J.
J. PERFORMANCE
SUMMARY
PERFORMANCE
SUMMARY
FOR FOR THE THE RADIOANALYSES RADIOANALYSES OF OF J-l J-l SPIKED ENVIRONMENTAL SAMPLE SPIKED ENVIRONMENTAL SAMPLE MEDIA MEDIA -- 2003 2003
LIST OF LIST OF FIGURES FIGURES Figure Figure Numbers Numbers Title Title Page Page 1.
- 1. Exposure Pathways Exposure Pathways toto Humans Humans 99 2.
- 2. 2003 TLD 2003 TLD Monitoring Monitoring Locations Locations within within One One Mile of the Mile of the SSES SSES 10 10 3.
- 3. 2003 TLD Monitoring 2003 TLD Monitoring Locations Locations fromfrom One One to to Five Five Miles Miles of of the the 11 11 SSES SSES 4.
- 4. 2003 TLD 2003 TLD Monitoring Monitoring Locations Locations Greater Greater than than Five Five Miles Miles from from the the 12 12 SSES SSES 5.
- 5. 2003 Environmental Sampling 2003 Environmental Sampling Locations Locations within within One One Mile Mile of of the the 13 13 SSES SSES 6.
- 6. 2003 Environmental Sampling 2003 Environmental Sampling Locations Locations from from One One to to Five Five Miles Miles of of 14 14 the SSES the SSES
.\.J 7.
- 7. 2003 Environmental Sampling 2003 Environmental Sampling Locations Locations Greater than Five Greater than Five Miles Miles 15 15 from the from the SSES SSES 8.
- 8. Ambient Radiation Ambient Radiation Levels Based on Levels Based on TLD TLD Data Data 19 19 9.
- 9. Gross Beta Gross Beta Activity Activity in in Surface Surface Water Water 30 30 10.
- 11. Gross Beta Gross Beta Activity Activity in in Drinking Drinking Water Water 32 32 12.
- 12. Gross Beta Gross Beta Activity Activity in in Air Air Particulates Particulates 36 36 13.
- 13. Iodine-I31 Activity Iodine-I31 Activity in in Milk Milk 41 41 iiii
SUMMARY
AND
SUMMARY
AND CONCLUSIONS CONCLUSIONS Radiological Dose Radiological Dose Impact Impact The extent of The extent of the the 2003 2003 Radiological Radiological The amounts The amounts of of the the radionuclides radionuclides Environmental Monitoring Environmental Monitoring Program Program detected detected in environmental samples in environmental samples (REMP) sampling (REMP) sampling met met oror exceeded exceeded the the during during 2003 2003 werewere very very small, small, asas in in past past requirements of requirements of the the Susquehanna Susquehanna Steam Steam years.
years. Based Based on on the the radionuclide radionuclide levels levels Electric Station Electric Station (SSES)
(SSES) Technical Technical measured measured by by the the REMP, REMP, the the maximum maximum Requirements. The Requirements. The types types of of analyses analyses whole whole bodybody dose dose or or maximum maximum organ organ that were that were performed performed on on these these samples samples dose dose to to aa member member of of the the public public from from for the for the identification identification and and quantification quantification SSES operation SSES operation is is estimated estimated to to be be less less of radioactivity of radioactivity also also metmet oror exceeded exceeded than one-tenth than one-tenth of of one one percent percent of of the the per per the SSES the SSES Technical Technical Requirements.
Requirements. The The unit dose unit dose guidelines guidelines established established by by the the of this result of result this effort effort waswas thethe verification verification Nuclear Regulatory Nuclear Regulatory Commission Commission (NRC) (NRC) of the of the SSES SSES Effluent Effluent Monitoring Monitoring as stated as stated in in 10 10 CFR CFR 50, 50, Appendix Appendix I. I.
Program Program data data that that indicate indicate thatthat the the The maximum The maximum hypothetical hypothetical off-site off-site SSES SSES operation operation has has no no deleterious deleterious whole body whole body andand organ organ doses doses from from effect on the effect on the health health and and safety safety of of the the radionuclides detected radionuclides detected by by the the REMP REMP public or public or the the environment.
environment. and attributable and attributable to to the the SSES SSES operations operations were calculated were calculated to to be be approximately approximately 0.0015 mrem/year.
0.0015 mremlyear.
By contrast, By contrast, potassium-40, potassium-40, aa very very long-long-COMPARISON COMPARISON OF OF PERCENT PERCENT OF OF AVERAGE AVERAGE ANNUAL PUBLIC ANNUAL PUBLIC EFFECTIVE EFFECTIVE DOSE-EQUIVALENT DOSE-EQUIVALENT FROM OTHER FROM OTHER SOURCES SOURCES WITH WITH THAT THAT FROM FROM THE THE SSES SSES Natural Background 81%
<0.01 % Consumer Products 5%
Medical 14%
Sources for Sources for the the values values provided, provided, with with the the exception exception of of Susquehanna, Susquehanna, are are the the foUowing foUowing from from NCRP NCRP Report #93 (1987):
Report #93 (1987): Tables Tables 2.4 2.4 (Natural (Natural Background),
Background), 5.1 5.1 (Consumer (Consumer Products),
Products), and and 7.4 7.4 (Medical).
(Medical).
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report 11
II II SlImmarv and SlImmarv and Conclllsions Conclllsions lived, naturally occurring lived, naturally occurring radionuclide radionuclide radium-226 were radium-226 were reported reported in in sediment.
sediment.
found in found in the the human human body, body, is is estimated estimated These radiomiclides are These radiomiclides are notnot related related to to to deliver to deliver an an average average annual annual dose dose toto the the the operation the operation of of the the SSES.
SSES. Doses Doses from from blood forming blood forming organs organs of of individuals individuals in in the presence the presence of of these these radiomiclides radiomiclides were were the United the United States States of of about about 27 27 millirem.
millirem. not included not included in in the the estimate estimate of of the the dose dose While aa small While small portion portion ofthe ofthe background background from SSES from SSES attributable attributable radionuclides.
radionuclides.
dose from dose from natural natural radiation radiation sources, sources, the'.
potassium-40 potassium-40 dose dose is is still still 18,000 18,000 times times Man-made Radionllc/ides Man-made Radionllc/ides the estimated the estimated maximum maximum whole whole bodybody Although Although not not allall due due to to SSES SSES operation, operation, and organ and organ doses doses to to aa hypothetical hypothetical the following the following man-made man-made radionucIides radionucIides member of member of the the public public fromfrom ingestion ingestion of of were reported were reported at at levels levels in in the the radionuclides attributable radionuclides attributable to to the the SSES.
SSES. environment in environment in excess excess of of the the MDCs MDCs for for their respective their respective analyses:
analyses: tritium,tritium, The maximum direct The maximum direct radiation radiation dosedose iodine-131 andcesium-137.
iodine-131 andcesium-137. These These from SSES from SSES operation operation to to aa member member of of radionuclides, with radionuclides, with the the exception exception of' of' the public the public waswas determined determined to to be be cesium-I 37, cesium-I 37, were were identified identified in in surface, surface, approximately 0.0314 approximately 0.0314 milliremlyear.
milliremlyear. ground and ground and drinking drinking water.water. Tritium Tritium The total The total whole whole body body dose from both dose from both was measured was measured above above minimum minimum ingested radionuclides ingested radionuclides and and direct direct detectable concentrations detectable concentrations in in some some radiation is radiation is negligible negligible compared compared to to the the surface water, surface water, drinking drinking water, water, and and public's exposure public's exposure from from natural natural ground water ground water samples.
samples. Iodine-13l Iodine-13l was was background radiation, background radiation, medical medical identified in identified in surface surface waterwater and and drinking drinking irradiation, and irradiation, and radiation radiation fromfrom water. Cesium-I37 water. Cesium-I37 was was observed observed in in consumer products consumer products of of more more thanthan 300 300 sediment and sediment and soil.
soil.
milliremlyear effective milliremlyear effective dose-equivalent.
dose-equivalent.
Tritium Tritium is is the the only only man-made man-made Identified Radionuclides Identified Radionuclides radionucIide attributed radionucIide attributed to to SSES SSES operation. Tritium operation. Tritium in in media media otherother than than and Their and Their Dose* the Susquehanna the Susquehanna River River waterwater Contributions Contributions downstream of downstream of the the SSES SSES was was attributed attributed to both to both natural natural production production by by the the Naturally OcclIrring interaction of interaction of cosmic cosmic radiation radiation with with the the Radionllc/ides upper atmosphere upper atmosphere and and previous previous In 2003, the In 2003, the SSES SSES REMP REMP reported reported the the atmospheric testing atmospheric testing of of nuclear nuclear weapons.
weapons.
naturally occurring naturally occurring radionuclides radionuclides The presence The presence of of cesium-I cesium-I 3 377 was was beryllium-7, potassium-40, beryllium-7, potassium-40, radium-226, radium-226, attributed to attributed to non-SSES non-SSES sources. sources.
and thorium-228 and thorium-228 in in the the environment environment at at Cesium-137 was Cesium-137 was considered considered to to bebe levels exceeding levels exceeding the the minimum minimum present only present only as as residual residual falloutfallout fromfrom detectable concentrations detectable concentrations (MDCs) (MDCs) for for atmospheric weapons atmospheric weapons testing.testing. Iodine-Iodine-their respective their respective gammagamma spectroscopic spectroscopic 131 was 131 was found found in in the the aquatic aquatic pathway.
pathway.
analyses.
analyses. Beryllium-7 Beryllium-7 was was identified identified in in Evidence indicates Evidence indicates that that it it is is there there only only air and air and sediment.
sediment. Potassium-40 Potassium-40 was was as the as the result result of of the the discharge discharge of of medical medical observed in observed in fish, fish, sediment, sediment, surface surface ..waste waste toto the the Susquehanna Susquehanna or or water, ground water, ground water, water, milk, milk, soil, soil, and and fruit fruit Lackawanna Rivers Lackawanna Rivers through through sewagesewage and vegetables.
and vegetables. Thorium-228 Thorium-228 and and treatment plants treatment plants upstream upstream of of the the SSES.
SSES.
1 1 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
Summary Summary and and Conclusions Conclusions AQUATIC AQUATIC PATHWAY PATHWAY All of the man-made radionuclides mentioned above were not analyzed for PERCENT PERCENT TOTAL TOTAL in all media.
media. For example, no analyses GAMMA GAMMA ACTIVITY ACTIVITY were perfonned performed in an effort to determine iodine-I3I iodine-I 3 I levels in ground SEDIMENT water. When selecting the types of analyses that would be perfonned, performed, consideration was given to the potential importance of different radionuclides in the pathways to man and the regulatory analysis requirements for various environmental media.
media.
Relative Radionuclide Activity Levels in Selected Media Some media monitored in the environment are significant for the numbers of gamma-emitting radionuclides routinely measured at TERRESTRIAL TERRESTRIAL PATHWAY PATHWAY levels exceeding analysis MDCs.
Sediment in the aquatic pathway and PERCENT PERCENT TOTAL TOTAL soil in the terrestrial pathway are two GAMMA ACTIVITY GAMMA ACTIVITY such media.
SOIL The following pie graphs show the relative activity contributions for the types of gamma-emitting radionuclides reported at levels above the analysis MDCs in sediment and soil at indicator locations during 2003.
Naturally occurring Naturally occurring radionuclides radionuclides accounted for accounted for 99.5 99.5 % and 99.4
% and 99.4 % ofthe
% ofthe gamma-emitting activity gamma-emitting activity in in sediment sediment and in and in soil, soil, respectively, respectively, in in 2003.
2003. Man-Man-made radionuclides made radionuclides of of SSES SSES origin origin accounted for accounted for 0.1 0.1%% of of the the gamma-gamma-emitting activity emitting activity in in sediment sediment during during 2003 Radiological Environmental Monitoring Report 33 co-z...
CO"Z-
II II Summary and Conclusions 2003. Man-made radionuclides 2003. Man-made radionuclides of of non-non-SSES origin SSES origin account account for for the the rest rest of of the the gamma-emitting activity gamma-emitting activity in in sediment sediment and soil and soil during during 2003.2003. Generally, Generally, the the activity for activity for naturally naturally occurring occurring radionuclides reported in radionuclides reported in sediment sediment and and soil dwarfs soil dwarfs the the activity activity of of thethe man-made man-made radio nuclides radio nuclides also also reported.
reported.
Radionuclides.
Radionuclides. ContriblltingContribllting to to fron, SSES Dose fron, Dose SSES Operation Operation Of the three Of the three man-made man-made radionuclides radionuclides reported in reported in the the environment environment by by the the SSES REMP, SSES REMP, tritiumtritium is is the the only only radionuclide attributable radionuclide attributable to to SSES SSES operation.
operation.
The dose to The dose to members members of of the the public public attributable to attributable the identified to the identified Tritium Tritium was 0.0015 was 0.0015 mrem.mrem.
Tritium Tritium was was included included in in the the dose dose calculation because calculation because it was identified it was identified in in \.J
\.J the REMP the REMP samples samples of of water water being being discharged to discharged to the the river.
river. The The concentration of concentration of tritium tritium in in the the water water andand the volume the volume of of water water discharged discharged were were used to used to determine determine the the amount amount of of tritium tritium released. The released. The presumed presumed exposureexposure pathways to pathways to the the public public fromfrom thisthis radionuclide were radionuclide were drinking drinking water water taken taken from the from the Susquehanna Susquehanna River River at at Danville, P Danville, PA,A, andand eating eating fish fish caught caught the SSES near the near SSES discharge discharge to to the the river.
river.
This assumption This assumption is is based based on on the the fact fact that tritium that tritium does does not not emit emit gammagamma radiation and radiation and the the beta beta radiation radiation emitted emitted by tritium by tritium is is not not sufficiently sufficiently penetrating penetrating to reach to reach an an individual individual on on thethe shore.
shore.
2003 Radiological 2003 Radiological En'vlronmentalMonitoring En'vlronmentalMonitoring Report Report
PPL has PPL maintained a has maintained aRadiological Radiological .
Environmeritru Monitoring Program Program Radiological Environme~~1 Environmeritru Monitoring Radiological <
(REMP) in (REMP) in the the vicinity vicinity ofof the the existing existing Monitoring ' "
Monitoring Susquehanna Stearn Susquehanna Stearn Electric'Station Electric'Station Units 1 Units 1 and and 22 sirice sirice April, April, 1972, 1972, prior prior to to '
The enclosed information The enclosed information is is consistent consistent ,', construction of construction of both both units units and and ten ten years years with with the the objectives objectives outlined outlined in in the the SSES SSES prior to prior to the the initial initial operation operation of of Unit Unit 1 1 in in ODCM ODCM and in10CFR50 Appendix and in10CFR50 Appendix I, I, ' September, 1982.
September, 1982. The The SSES SSES is is located located ..
Section IV.B.2, Section IV.B.2, IV.B.3 IV.B.3 and and IV.C.
IV.C. on an on an approximately approximately 1500 1500 acre acre tract' tract' along the along the Susquehanna Susquehanna River, River, five five miles miles In addition to In addition to the the steps steps taken taken to to control,',' ; northeast of northeast of Berwick Berwick in in Salem Salem :
and to and to monitor monitor radioactive radioactive effluents effluents ' " Township, Luzerne Township, County, '
Luzerne County, from the from the SSES, SSES, the the SSES SSES Technical Technical ' ,.,', Pennsylvania. The Pennsylvania. The area area around around the the site site Specifications also Specifications also require require aa program program ,,: is primarily is primarily rural, rural, consisting consisting for the for the radiological radiological monitoring monitoring of of the the :; <' ' predominately of predominately of forest forest and and agricultural agricultural environment in environment in the the vicinity vicinity ofof the the SSES:
SSES: :.: lands. (More lands. (More specific specific information information on on The objectives The objectives of of the the SSES SSES REMP REMP are are ":' the demography, the demography, hydrology, hydrology, as as follows:
follows: meteorology, and meteorology, and land land use use characteristics of characteristics of the the area area inin the the vicinity vicinity
environmental surveillance environmental surveillance . <,:: ' the Final the Final Safety Safety Analysis Analysis Report Report obligations; obligations; (Reference 2),
(Reference 2), and and the the Final Final
Environmental Statement Environmental Statement (Reference (Reference 3) 3)
- Verification Verification of of no no detrimental detrimental for the for the SSES.)
SSES.) TheThe purpose purpose of of the the effects on public effects on public health health andand safety safety ~' preoperational REMP preoperational REMP (April, (April, 1972 1972 toto and the and the environment environment from from SSESSSES ., September, 1982)
September, 1982) waswas toto establish establish aa operations, operations, baseline for baseline for radioactivity radioactivity in in the the local local environment that environment that could could be be compared compared
- Assessment Assessment of of dose dose impacts impacts to to the' the' ' with the with the radioactivity radioactivity levels levels observed observed in in public, if any, public, if any, various environmental various environmental media media throughout the throughout the operational operational lifetime lifetime of of
- Verification Verification of of adequate adequate SSESSSES ' .): I.',':' : the SSES.
the SSES. :: This assessments of This comparison comparison facilitates of the the radiological facilitates radiological impact impact radiological radiological effluent controls, and<~" '.I:
effluent controls, assessments
,'.i,)~." ~ ',I.~~\;~~.
of the of the SSES SSES operation.
operation.
" ~ ...
- Identification: measurement, Identification:
measurement, :'
- trending, trending, and and evaluation' evaluation' of" of"
. j . ' .....
The SSES ~MP was The SSES was designed designed on on the the radionuclides' radionuclides' and and their their " . : basis of basis of the the NRC's NRC's Radiological Radiological concentrations concentrations in in critical critical Assessment Branch Assessment Branch Technical Technical Position Position environmental environmental pathways pathways near the near the on radiological on radiological ,environmental
,environmental < <
SSES.
SSES. , ' , '.,:;' monitoring, as monitoring, as described described in in Revision,!,
Revision,!, ,
November 1979.(Reference November 1979.(Reference 4) 4)
- ,;1 ...
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report ss
II II In trodllction In trodllction However, However, the the REMP REMP conducted conducted by by PPL PPL the impact of the impact of the the station station operation.
operation.
for the for the SSES SSES exceeds exceeds the the monitoring monitoring Control locations Control locations have have been been situated situated at at suggested by suggested by the the NRC's NRC's branchbranch sites where sites where it it is is considered considered unlikely unlikely thatthat technical position, technical position, as as well well asas the the SSES SSES radiation or radiation or radioactive radioactive material material fromfrom Technical Req~irements in Technical in terms terms of of the the normal station normal station operation operation would would be be number of number of monitoring monitoring locations, locations, the the detected. Indicator detected. Indicator locations locations are are sited sited frequency of frequency of certain certain monitoring, monitoring, the the where where it is expected it is expected that that radiation radiation and and types of types of analyses analyses required required for for the the material that radio~ctive material that might might originate originate samples, and samples, and thethe achievable achievable analysis analysis from the from the station station would would be be most most readily readily sensitivities.
sensitivities. detectable.
detectable.
Potelltial Exposure Pat~ways Control locations for Control locations for the the atmospheric atmospheric The three pathways The three pathways through through ,which
,which and terrestrial and terrestrial pathways pathways are are more than more than radioactive material radioactive material may may reach reach thethe 10 miles 10 miles fromfrom the the station.
station. Preferably, Preferably, pubJic from pubJic from nuclear nuclear power power plants plants areare the the the controls the controls alsoalso are are in in directions directions fromfrom atmospheric, terrestrial, atmospheric, terrestrial, and and aquatic aquatic the station the station less less likely likely toto be be exposed exposed to to pathways. (Figure pathways. (Figure 11 depicts depicts thesethese wind blowing wind blowing from from thethe station station than than are are pathways for pathways for the the intake intake of of radioactive radioactive the indicator the indicator locations.
locations. Control Control materials.) Comprehensive materials.) Comprehensive radiological radiological locations for:
locations for: the the aquatic aquatic pathway, pathway, the the environmental monitoring environmental monitoring must must sample sample Susquehanna River, Susquehanna River, are are upstream upstream of of the the media from media from all of these all of these pathways.
pathways. station's discharge station's discharge to to the the river.
river.
Mechanisms Mechanisms by by which which people people may may be be Indicator locations are Indicator locations are selected selected exposed to exposed to radioactivity radioactivity and and radiation radiation in in primarily on primarily on the the basis basis ofof prox.imity prox.imity to to the environment the environment vary vary with with thethe pathway.
pathway. the station, the station, although although factors factors such such as as Three mechanisms Three mechanisms by by which which aa member member meteorology, topography, meteorology, topography, and and sampling sampling of the of the public public hashas the the potential potential to to be be practicality also practicality also areare considered.
considered.
exposed to exposed to radioactivity radioactivity or or radiation radiation Indicator locations Indicator locations for for the the atmospheric atmospheric from nuclear from nuclear power power plants plants such such as as the the and terrestrial and terrestrial pathways pathways are are typically typically SSES are SSES are as as follows:
follows: less than less than 10 10 miles miles fromfrom thethe station.
station.
Most often, Most often, they they are are within within 5 5 miles miles ofof
- inhalation (breathing) inhalation (breathing) the station.
the station. Indicator Indicator locations locations in in the the Susquehanna River Susquehanna River are are downstream downstream of of
- ingestion (eating ingestion (eating andand drinking).
drinking). and and the station's the station's discharge.
discharge. Monitoring Monitoring results from results from indicator indicator locations locations are are
- whole body irradiation whole body irradiation directly directly compared with compared with results results from from control control from aa plant from plant or or from from immersion immersion in in locations. These locations. These comparisons comparisons are are made made the radioactive the radioactive effluents.
effluents. to discern to discern any any differences differences in in the the levels levels andlor types andlor types of of radioactive radioactive material material andlor radiation andlor radiation that that might might exist exist REiYPScope between indicators between indicators and and controls controls and and that that During During the the operational operational period period of of the the could be could be attributable attributable to to the the station.
station.
SSES, it SSES, it has has been been important'to important'to establish establish two different two different categories categories of of monitoring monitoring In 2003, the In 2003, the SSES SSES REMP REMP collected collected locations, called locations, called control control and and indicator indicator more than more than 850850 samples samples at at more more thanthan 40 40 locations, to locations, to further further assist assist in in assessing assessing 6
6 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring ReportReport
lntrodtiction lntrodtiction more than
',{ J ~,; .! ..
locatio~s and peffonned more and peffonned than supporting supporting the, the, (!ff1,uent
(!ff1,uent and and ,
1,500 analyses.
1,500 analyses. In In additio~~ ih~ RE~',~ environmental monitoring environmental monitoring for for the the SSES.
SSES.
monitors ambient radiation)evels, monitors ambient radiation)evels, using. using. , ,; ,
thennoIiiminescent dosimeters thennoIiiminescent dosimeters CfI.Ds) CfI.Ds) :':' REMP Monitoring REMP Monitoring Sensitivity Sensitivity at 84 at 84 indicator indicator and and control control locations; locations; ,,', ,,', The sensitivity The sensitivity of of the the SSES SSES REMP REMP was was ':
making as making as manya~ 33~ radiation,radiation, level,level, "" ,f
,f demonstrated in demonstrated in 1986, 1986, following following the the measurements each measurements each year.
year. The The media media "" problem with with the the Chemobyl Chemobyl reactor reactor in in ,,
aare' re';;
problem monitored and monitored and analyses analyses performed performed the fonner the fonner Soviet Soviet Union. Union. When When the the summarized in summarized in the the table table below.
below. -'
-' Chemobyl incident Chemobyl incident occurred, occurred, the the SSESSSES Figures 2 Figures 2 through through ,7 ,7 di~play the the REf>4P REf>4P (( REMP was REMP was able able to to detect detect aa relatively relatively TLDs and TLDs and sampJing sampJing locations locations in in the the ,,',,',
,,',,', small increase small increase in in the the level level of of gross gross beta beta vicinity or'the vicinity or'the SSES:,;Appendix SSES:,;Appendix C C ,,':,',
,,':,', activity in activity in air air samples samples at at ,both
,both control control
provides directions; provides directions; distances, distances, and ,a,',,', ,,'
and ,a,',,', ,,' and indicator and indicator locations; locations; as as well well asJhe asJhe brief description brief description of of each each ofof the the l,ocations l,ocations presence of presence of some some specific specific radioactive radioactive in Figures in Figures 2 2 through through 7. 7. .. .. materials that materials that are are not not normaJIy.normaJIy.
observed.
observed.
Regulatory agencies also Regulatory agencies also participate participate in in ,,
monitoring the monitoring the SSES SSES environment environment and. and. "" Detection Detection of of radiation radiation and and radioactive radioactive also oversee also PPL's monitoring oversee PPL's monitoring efforts~, "" material from material from the the SSES SSES in in the, the, ' , , '. , '
The Stat~.ofJ>ennsy]vania*s Department The Department environment environment is is complicated complicated by by thethe '. ,~
of Environmental of Environmental Protection Protection (PADEP)
(PADEP) "" presence of presence of naturally naturally occurring occurring radiation radiation monitors air monitors air "for radioactive particulat~s'
"for radioactive and radioactive and radioactive materials materials from from both both ',,'
and radioactive and radioactive iodine.
iodine. It It also also monitors' monitors' ,, terrestrial and terrestrial and cosmic cosmic sources. sources. Man- Man- .
milk, fruits milk, fruits and and vegetables, vegetables, surface surface and and made radiation made radiation and and radioactive radioactive materiai materiai drinking water, drinking water, fish, fish, river river sediments, sediments, from non-SSES from non-SSES sources, sources, such such as as nuclear, nuclear, ,
and ambient and ambient radiation radiation levels.
levels. P P ADEP ADEP fanout from fanout from previous previous nuclear nuclear weapons weapons makes this makes this data data available available to to the the NRC.
NRC. tests and tests and medical medical wastes, wastes, also also can can makemake , ~
Inspectors from Inspectors from the the NRC NRC regularly regularly visit visit identification of identification of SSES,radiation SSES,radiation and and the SSES the SSES to to review review procedures procedures and and radioactive material radioactive material difficult. difficult. Together, Together, J '
SSESREMP SSESREMP , ,
- . , . ' ~: ~ ~'".' .......
T"pe T"pe of of Monitorine Monitorine Media Media Monitored. Monitored. :
Gross Alpha Gross Alpha Activitv Activitv Drinkine: Water Drinkine: Water ' , ,
Gross Beta Gross Beta Activity Activity All Waters.
All Waters. except except Ground Ground Water, Water, and and Air Air Particulates Particulates . '
Radionuclide Gamma-Emittin~ Radionuclide Activities Activities All Media All Media .'
Tritium Activity Tritium Activity All Waters All Waters lodine-131 Activity lodine-131 Activity Surface Water.
Surface Water. Drinking Drinking Water. Water. 'Air 'Air & & Milk' Milk' Exposure Rates Exposure Rates Ambient Radiation Ambient Radiation Levels Levels !' ~ .
(byTLD)
(byTLD) ~ . ,,:: 1:..1 . :
records, conduct personnel records, conduct personnel interviews, interviews, this radiation and this radiation and radioactive radioactive material, material, observe activities observe activities first-hand, first-hand, and and present backgr?l;lnd present backgr?l;lnd levels levels fro~ which which generally examine generally examine the the programs programs an attempt an attempt is is mademade to to distinguish distinguish 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report 7 7
I I 11ltrodllction relatively small relatively small contributions contributions from from thethe PPL's contracted PPL's contracted REMP REMP radioanalytical radioanalytical SSES.
SSES. This This effort effort isis further' further' . laboratories are capable laboratories are capable of of meeting meeting the the complicated complicated by by the the natural natural variations variations analysis sensitivity analysis sensitivity requirements requirements foundfound that typically that typically occur occur from from both both in the in the SSES SSES Technical Technical Requirements.
Requirements.
monitoring location monitoring location to to location location and and with with SummarY descriptions SummarY descriptions of of the the analytical analytical time at time at the the same same locations.
locations. procedures and procedures and the the accompanying accompanying calculational methods calculational methods usedused by by the the The naturally occurring The naturally occurring radionucJides radionucJides laboratories can laboratories can bebe found found in in Appendix Appendix potassium-40, berylJium-7, potassium-40, berylJium-7, radium-226, radium-226, E.
E.
and thorium-228 and thorium-228 are are routinely routinely observed observed in certain in certain environmental environmental media. media. Additional terrestrial and Additional terrestrial and aquatic aquatic Potassium-40 has Potassium-40 has been been observed observed in in all all environmental monitoring environmental monitoring is is perfonned perfonned monitored media monitored media andand isis routinely routinely seen seen independent of independent of the the SSES SSES REMPREMP by by the the at readily at readily detectable detectable levels levels in in such such Academy of Academy of Natuml*Sciences of of media as media as milk.
milk. fish, fish, fruits fruits andand PhiIadelphia~ Pennsylvania.
Pennsylvania. The The vegetables. Seasonal vegetables. Seasonal variations variations in in monitoring program monitoring program is is titled titled "Safety "Safety beryllium-7 in beryllium-7 in air air samples samples are are regularly regularly Net" and Net" and an an annual annual report report is is provided provided to to observed. Man-made observed. Man-made radionuclides, radionuclides, PPL Susquehanna, LLe.
PPL Susquehanna, LLe. Although Although the the such as such as cesium-1371eft cesium-1371eft over over from from Safety Net' Safety Net' program program is is not not part of the part of the nuclear weapons nuclear weapons testing testing are are often often SSES REMP, SSES REMP, the the data data has has provided provided observed as observed as well.
well. .. In In addition~ the the additional infonnation additional infonnation relative relative toto the the radionuclide tritium, radionuclide tritium, produced produced by by both both environmental impact environmental impact of of the the operation operation cosmic radiation radiation interactions interactions in in the* of the the SSES.
SSES.
cosmic upper atmosphere upper atmosphere as as well well as as man-made man-made of
,J (nuclear weapons),
(nuclear weapons), is is another another radionuclide typically radionuclide typically observed.
observed.
Radioactivity levels Radioactivity levels inin environmental environmental media are media are usually usually soso low low thatthat their their measurements, even measurements, even with with state-of-the-art measurement art measurement methods,methods, typically typically have significant have significant degrees degrees of of uncertainty uncertainty associated with associated with ihem:(Reference5)* As As aa resuH, resuH, expressions expressions are are often often used used when when referring referring to to these these meas.urements meas.urements that that convey convey infonnation infonnation about about thethe levels levels being being measured measured relative relative to to the the measurement measurement sensitivities.
sensitivities. Tenns Tenns such such as "minimum as "minimum detectable detectable concentration" concentration" (MDC) are (MDC) are used used for for this this purpose.
purpose. The The fonnulas used fonnulas used toto calculate calculate MDCs MDCs may may be fo*und in be Appen(fix E.
in Appen(fix E.
The methods of The methods of measurement measurement for for sample radioactivity sample radioactivity levels levels usedused by by 88 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
\ Uquid
~ EfHuent Direct Irradiation I
- 1
. \
\......J Fuel Transport Figure 1 Figure 1
FIGURE 2 2003 TLD MONITORING LOCATIONS WITHIN ONE MILE OF THE SSES
~
FIGURE 33 FIGURE 2003 TLD MONITORING LOCATIONS FROM ONE TO FIVE MILES FROM THE SSES
FIGURE 44 FIGURE TlO MONITORING 2003 TLD 2003 MONITORING LOCATIONS lOCATIONS GREATER THAN GREATER THAN FIVE FIVE MILES MilES FROM FROM THE THE SSES SSES cos
FIGURE 5 FIGURE 5 2003 ENVIRONMENTAL 2003 ENVIRONMENTAL SAMPLING SAMPLING LOCATIONS LOCATIONS WITHIN ONE WITHIN ONE MILE MILE OF OF THE THE SSES SSES 1'MILE .
coc.
FIGURE 6 2003 ENVIRONMENTAL SAMPLING LOCATIONS FROM ONE TO FIVE MILES FROM THE SSES co col
FIGURE 7 2003 ENVIRONMENTAL SAMPLING LOCATIONS GREATER THAN FIVE MILES FROM THE SSES
Ambient Radiation Ambient Radiation Monitoring Monitoring
.- ~ ", .,'
'oi.';
- INTRODUCTION INTRODUCTION due due to to loeational loeational differences'in differences'in such such "
The principal or The principal or .primary,method primary,method for forthe the factors .8S soil factors soil characteristics characteristics (amounts (amounts .
SSES SSES REMP's REMP's measurement measurement of of ambient, ambient, of organic of organic matter, matter, particle particle size, size, 'etc.),
'etc.),
radiation levels radiation levels is is thethe use use of of ~ *.',' :. ~';:.. drnitiage opporturiities~ and drnitiage and exposure exposure 'to 'to '
thennoluminescent dosimeters thennoluminescent dosimeters (TLDs).:' sunlight. 'Environmental sunlight. 'Environmental TLDs TLDs can can also also The TLDs The TLDs are are crystals crystals (calcium(calcium sulfate) sulfate) ;' be affected be affected by by direcfradiation direcfradiation (shine) (shine) :
capable of capable of detecting detecting and and measuring measuring lo~ ~ from from the ?SSES turbine the ?SSES turbine buildings buildings during:during:
levels of levels of radiation radiation by by absorbing absorbing a . .:,,: ,! operation,*radivaste transfer transfer and and storage, storage, portion portion ofof the the radiation's radiation's energy energy tha,t~s'. and radioactive and radioactive gaSeousgaSeous effluents effluents from from '
incident upon incident upon them them and and storing storing .the .the ~.;., ; the SSES.
the SSES. . ' .
captured energy captured energy until until the the TLDs TLDs are are ':', d processed processed (read).
(read). Processing Processing involves involves ~':{ Unfortunately, Unfortunately, 'fLDs 'fLDs do do n~t havehave any any ..
heating the heating the TLDs TLDs to to release release their their stored.
stored. . inherent ability inherent ability to to indicate indicate the the source source of of energy in energy in the the fonn fonn of of light light and.,': "',,: the radiatio~ to the to which'theYareexposed.
which'theYareexposed.
measuring measuring the the intensity intensity of of the the light light that that . The placement The placement of of nu~erous TLDs'in TLDs'in '. '
emit. Th~ intensity they emit.
they intensity of of the the emitted.,.:' the the environment environment can can facilitate facilitate decision-'
decision-' ,
light is light is proportional proportional to to the.amountof the amountof i:,' :' making making ~bo~,t the the possible possible radiation, radiation, ,
radiation radiation to to which which they they werewere exposed.
exposed. ' soiirces'to which soiirces'to which TLDsTLDs are are exposed.':* ' '
Calibration Calibration of of the the TLD TLD processors processors ' ;.;! r However~ aa method method for for evalu*atiiigTLD TLD .
pennits pennits aa reliable reliable relationship relationship to to bebe , ; 1 \:. data data is is still still required required:'The TheSSESSSES *.REMP :
established between established between the the light light emitted emitted :," I: relies relies on on 'a
'a statistically statistically based based approach approach ;.
and and the the amount amount of of radiation radiation dose dose .... ! . ' . to to simultaD(!ously simultaD(!ously compare compare indicator indicator ::.:
received by received by the TLDs; t~e result the ;fLDs; pennits i result pennits TLD TLD data data with with control TLDdata and control TLDdata and accurate accurate measurements measurements of of the the ambient, ambient, operntionafTLIidata With':";:, "
operntionafTLIidata radiation in radiation in the the environment.
environment. 'i';~ :' ~ preoperational TLD'data.'
preoperational TLD'data.' This This ' . .
,. ~ ~ [ ; 1 ~ approach peririits approach peririits the the .flagging
.flagging of of ',.
Environm'ental Environm'ental TLDs TLDs ,are"continually** ",. ; environmental environmental TLD TLD doses doses that that might might exposed to exposed to natural natural radiation radiation from from the,:.,,; have have !been
!been produced produced by'both by'both man-made man-made ground (terrestrial ground (terrestrial radiation) radiation) and and fromfrom ,i .. sources sources ofradiaiion; ofradiaiion; as as well well as'natUral as'natUral ,.
the sky the sky (cosmic)
(cosmic) radiation.
radiation. In In addition,.
addition,. : radiation radiation sources; sources; It It also also provfde'sa' provfde'sa' they also they also may may be be exposed exposed to to man-made:: means means for for attributing attributing aa portion portion of of the the '.
radiation. Most radiation. ofthe environmental Most ofthe environmental ::: total total TLD TLD dosedose to to SSES SSES operation operation if if TLD's natural TLD's natural radiation radiation exposure exposure comes, comes, appropriate. Appendix appropriate. Appendix E, E, pages.
pages. ~-~ :
from sources from sources in in the the groundground .. .'Thesei'l::~;): ': through E-IO~ provides through provides a adescription*of terrestrial sources terrestrial sources vary vary naturally' naturally' wiih wiih :J..:: j' tb.e process tb.e process for for evaluating the the results results of of time time due due to to changes changes 'in 'in soil soil moisture;, ::.. i TLD measurements.
TLD measurements. .
t ;
snow snow cover, cover, etc. etc. The The natural-radiation natural-radiation ,, ~ . \
picture is picture is complicated complicated because because the the factors affecting factors affecting radiation radiation reachingreaching the the TLDs from TLDs from the the ground ground vary vary differently differently with with time time fromfrom oneone locationlocation to to another another 2003 Environmental 2003 Environmental Radiological Radiological Monitoring Monitoring Report Report 16 16
Ainhiimt Radiatiijn l~fonitoring Scope sho~ in the bar ~phon the following page. Refer to Figure 8 whIch trends both indicator and control data quarterly TLDs from 1973 through 2003.
The area around the SSES was divided for monitoring purPoses into sixteen The 2003 arimial average exposures sectors radiating outwards, from the an plant site, each en'compaSsing area indicator and' control locations were 20.2 mR/std. qtr. and 19.0 mR/std. qtr.,
described by an ar~ 2~.~
respectively. The 2003 exposures are TLDs were placed in all 16 sectors at within the ranges of annual averages for varying distances from the plant. the prior operational 'periods at each Monitoring locations ~ere chosen.
type of monitoring location. Refer according to the criteria presented in the Figure 8 at the end of this section which NRC Branch Technical Position on trends quarterly TLD results for both Radiological Monitoring (Revision 1, preoperational and operational periods November, 1979). The locations for the at the SSES. Refer to Appendix H, TLDs were selected by considering Table HI, page H 3 for acomparison of factors such as loc~l meteorological, topographical, and population' the 2003 mean indicator and control' TLD results with the means for the' distribution characteristics.
preoperational and prior operational periods at the SSES.
During 2003, the SSES REMP had 76 indi,cator TLD' l~cations and ei~t Indicator environmental TLD results for controlTLD locations. This 'level of 2003 were examined quarterly on an monitoring exceeds that which IS individual location basis and compared required by th~ Nuclear Regula'tory ,
with both current contiollocation Commission. The indicator TLDs, ,
results and preoperational data. Very nearest the SSES are positioned at the small SSES exposure contributions secu~ity or ~e?met~rfe~ces su~ounding were suggested during 2003 at the the SIte. This ]s the closest that a' following onsite locations: IS2, 6S4, member of the public would be abi~ to 6S9, 7S6,8S2~9S2, 10S2, 11S3, 12S4, approach the station ..The co'ntrol TLDs 13S2, 13S4, 13S5, 16SI~ and 16S2.
are the most distant from the SSES '
Thus; there' were 10 monitored locations ranging from 10 to 20 miles from the site. in 2003 where a SSES dose contribution is considered to have been discernible.
Refer to Appendix E, page E-6, for'a Monitoring Results discussion of4'TLD Data Interpretation.'" TLD results for all TLDs locations for each quarter of 2003 may TLDs were retrieved and be found in Appendix I, Table I-I, quarterly in 2003. Average ambient beginning at page 1-2.
radiation levels measured by environmental TLDs generally remained constant throughout 2003, as 17 2003 Environmental Radiologic:alMonitoring Report
Ambient Ambient Radiation Monitoring Radiation Monitoring 2003 REMP Quarterly TLD Averages 25.0
..: 20.0 tT 15.0
-c
~
III E
10.0 5.0 0.0 2 3 4 Calendar Quarters The estimated quarterly The estimated quarterly exposure exposure contributions were contributions were summed summed by by location location for the for the entire entire year.
year. The The largest largest dose dose suggested was suggested was approximately approximately 0.0314 rnrem 0.0314 rnrem at at an an on on site site monitoring monitoring location, 9S2, location, 9S2, 0.2 0.2 mile mile south south of of the the SSES. This SSES. This dose dose was was used used forfor determining compliance determining compliance with with SSES SSES Technical Requirement Technical Requirement Limit Limit 3.11.3 for 3.11.3 for annual effluent annual effluent reporting reporting purposes.
purposes.
This dose This dose amounts amounts to to only only 0.13%
0.13% of of the the 25 rnrem 25 rnrem whole-body whole-body dosedose limit of of SSES Technical SSES Technical Requirement Requirement 3.11.3. 3.11.3.
2003 Environmental 2003 Environmental Radiological Radiological Monitoring Monitoring Report Report 18 18 c.O~
FIGURE 8 FIGURE 8 -- AMBIENT AMBIENT RADIATION RADIATION LEVELS LEVELS Exposure Rate (mRlSTD Qtr) BASED ON BASED ON TLD TLD DATA DATA 50 , --------------------------,, --------------------------------------------------------,
PREOPERATIONAL OPERATIONAL 45 40 35 Unit 2 30 Criticality 25 20 15 10 5
0 r--- r---
~
r---
0\
l£l r---
0\
r---
0\
0\
r---
0\
""'at)"
0\
~
at) 0\
l£l at) 0\
at) 0\
0\
at) 0\
0\
0\
~
0\
0\
l£l 0\
0\
t-0\
0\
0\
0\
0\ =
=
M
=
~
=
M
- Indicator - Control CJQ
Aquatic Patlrwaj; Monitoring v E:t'~Uj!l0~QY.At~p:~~r~l\¥;M_QNi:rPRiNG.;C:::Q:*:;~;c~7 INTRODUCTION INTRODUCTION data data for for comparison comparison with with downstream downstream The fol1owing media The fol1owing media werewere monitored monitored in in monitoring results.
monitoring The poteniial results. The poteniial exists exists 2003 by 2003 by th~ SSES SSES REMPREMP in in the the aquatic' for radioactive for radioactive material material that that might might be be surface water~ drinking pathway: surface pathway: drinking water," present in present in SSES SSES airborne airborne releases releases to to fish, and fish, and sediment.
sediment. Some Some of of the' the' media media : eJiter the eJiter the Susquehanna Susquehanna River River upstream upstream (e.g., drinking (e.g., drinking waterwater and and fish) fish) provide,r:' of the of the plant plant through through either either direct direct infonnation that infonnation that can can bebe especially especially useful useful deposition (e.g.,
deposition (e.g., settling settling or'washout) or'washout) or' to the to the estimation estimation of of possible possible dosedose to to the the by way by way of of runoff runoff from from deposition deposition on on public from public from potentially potentially ingested' ingested' ", land land adjacent adjacent to to the the river.
river. However However
radioactivity, if radioactivity, if detected.
detected. Other Other media, media, :. direct deposition direct deposition and and runoff runoff are are such as' such as' sediment, sediment, can can bebe useful useful forfor '. considered to considered to be be insignificant insignificant as as means means trending radioactivity trending radioactivity levels levels in in the' the' of entry of entry forfor SSES SSES radioactivity radioactivity into into thethe aquatic pathway, aquatic pathway, primanJytJecause primanJytJecause of' of' Susquehanna River Susquehanna River when when compared compared to to their tendency their tendency to to assimilate assimilate certain certain Jiquid discharges Jiquid discharges underunder nOrnlal nOrnlal materials that materials that might might enter enter the the surface surface ' conditions.
conditions.
water to water to wh~c~ they they areare exposed.
exposed. The The results from results from monitoring monitoring all all of of these' ' Lake Took-a-While Lake Took-a-While (LTAW). (LTAW). which which is is .
media provide media provide aa p,icture of of the the aquatic!
aquatic! r . located located in PPL's Riverlands in PPL's Riverlands Recreation Recreation pathway that pathway that is clearer th~m that is clearer that 'which"; ! Area adjacent Area adjacent to to the the Susquehanna Susquehanna could could be be obtained obtained if if one one oror more more were:
were: ',' River, is River, is a]so a]so considered considered to be part to be part ofof not not included included in in the the REMP.
REMP. " i f , the aquatic the aquatic pathway pathway for for monitoring monitoring ,
" ' purposes. Although purposes. Although it it is is not not in in a' Fruits or Fruits or vegetables vegetables that that are are grown grown in' ," pos~tion to to receive receive water water discharged discharged to to .
fields fields irrigated irrigated with with surface surface water water would would the river the river from from the'SSES, the'SSES, it it can can receive receive also also be inthe aquatic be inthe aquatic pathway.
pathway. The The .'; stonn runoff stonn runoff from from theSSES.
theSSES. Stonn' Stonn' land use land use census census (Reference (Reference 11) 11) runoff from runoff from thethe SSESsite SSESsite sho'uldsho'uld not not conducted in conducted in 2003 2003 looked looked at at fanns fanns nonnally contain nonnally contain anyany measurable measurable within 10 within 10 miles miles downstream downstream of of the the '" radioactivity from radioactivity from thethe plant.
plant. However, However, SSES.
SSES. Two Two fannfann fields fields were were found found to to the SSES the SSES REMP, REMP, consistent consistent with with other' other' have been have been irrigated irrigated during during thethe 2003'* " aspects of aspects of aquatic aquatic monitoring monitoring and and thethe growing season.
growing season.
..,: REMP. ingfmeral~ goes REMP. goes beyond beyond its its requirements by requirements by monitoringLTAW.
monitoringLTAW.
The The aquatic aquatic pathway pathway in in the the vicinity vicinity of,of, f' the SSES the SSES is is the the Susquehanna Susquehanna Rjver~ ,'" , Scope Scope Monitoring Monitoring of of al1 al1 'of
'of the the aquatic aquatic media;'-'
except drinking except drinking water, water, is is conducted' conducted' 'j ;
- Surface Water both both downstream' downstream' arid arid upstream upstream of of the;;' Surface water Surface water waswas routinely routinely sampled sampled location from location from which which occasional occasional SSES' SSES' -',' from from the the Susquehanna Susquehanna River River at at one one low-level radioactive low-level radioactive discharges' discharges' enterenter ,';" I indicator ]o~ation (6S5) indicator (6S5) andand oneone con'lro]
con'lro] .
the river/The upstream the river/The upstream monitoring monitoring .,j ;. <"
location (6S6)'iitthe location (6S6)'iitthe SSESSSES River River Water Water locations serve locations serve as as controls controls to to provide' provide' '.' : Intake during Intake during 2003.
2003. Sampling Sampling also also took took 2003 Radiological 2003 Radiological Environmental Monitoring Report Environmental Monitoring Report 20 20
II II Aqllatic Pathway Aqllatic Pathway Monitoring Monitoring place place atat the the fol1owing fol1owing additional additional the Susquehanna River.
the Susquehanna River. In In addition, addition, indicator locations:'
indicator locations:' the the SSES SSES discharge, discharge, sediment' was sediment' was also also obtained obtained fromfrom line to line to the the river river (2S7/6S7)
(2S7/6S7) and and Lake Lake location LTAW.
location LTAW.
Took-A-Whi1e (LTAW).
Took-A-Whi1e (LTAW).
Sampling Sampling Drinking Water Drinking Water Drinking water Drinking water samples samples were were collected collected Surface Water Surface Water at location 12H2, at location 12H2, thethe Danville Danville Weekly Weekly grabgrab sampling sampling was was performed performed at at Municipal Water Municipal Water Authoriiy's Authoriiy's treatment treatment the indicator the indicator location location 6S5.6S5. Weekly Weekly grab grab facility on facility on the the Susquehanna Susquehanna River, River, in in samples were samples were composited composited both both monthly monthly 2003. Treated 2003. Treated water water is is collected collected from from and biweekly and biweekly at at this this location.
location. Location Location the end the end ofof the the processing processing fjowpath,fjowpath, 6S5 was 6S5 was considered considered aa backup backup for for representing finished representing finished wat~r that that isis locations 2S7 locations 2S7 and and 6S7 6S7 in in the the event event that that suitable for suitable for drinking.
drinking. This This is is the the nearest nearest water could water could not not be be obtained obtained fromfrom thethe point downstream point downstream of of the the SSES SSES automatic samplers automatic samplers at at these these locations.
locations.
discharge to discharge to the the River River at at which which drinking drinking Nevertheless, 6S5.was Nevertheless, 6S5.was sampled sampled water is water is obtained.
obtained. No No drinking drinking waterwater routinely throughout routinely throughout 2003, 2003, since since itit is is control location control location is is sampled.
sampled. For For allall ' the closest the closest downstream downstream sampling sampling pointpoint intents and intents and purposes, purposes, controlcontrol surface surface to the to the SSES SSES discharge.
discharge.
water sampling water sampling locations locations would would be be suitable for suitable for comparison.
comparison. Indicator locations 2S7 Indicator locations 2S7 andand 6S7, 6S7, the the SSES Cooling SSES Cooling Tower Tower Blowdown Blowdown Fish Fish were sampled Fish were sampled from from the the Discharge (CTBD)
Discharge location 6S6, location (CTBD) line, 6S6, the the SSES line, and SSES River and control control River Water Water
.J Susquehanna River Susquehanna River in in the the spring spring and and Intake structure, Intake structure, were were sampled sampled timetime fall of fall of 2003 2003 at at one one indicator, indicator, location, location, proportionally using proportionally using automatic automatic IND, downstream IND, downstream of of the the SSES liquid SSES liquid continuous samplers.
continuous samplers. The The samplers samplers discharge to discharge to the the River River and and oneone control control were typically were typically set set to to obtain obtain 30-60 30-60 ml ml location, 2H, location, 2H, sufficiently sufficiently upstreamupstream to to aliquots every aliquots every 20-25 20-25 minutes.
minutes. Weekly, Weekly, essentially preclude essentially preclude the the likelihood likelihood that that the water the water obtained obtained by by these these samplers samplers the fish the fish caught caught there there would would spend spend any any was retrieved was retrieved for for both both biweekly biweekly and and time below time below the the SSES discharge. In SSES discharge. In monthly compositing.
monthly compositing.
addition, fish addition, fish we~e also also sampled sampled in in the the fall from fall from PPVs PPVs Lake Lake Took-a-While, Took-a-While, The other surface The other surface water water monitoring monitoring location LTAW.
location LTAW. This This location location is is not not location, LTAW, location, LTAW, was was grab grab sampled sampled downstream of downstream of the the SSES SSES discharge.
discharge. It It once each once each month.
month.
is sampled is sampled because because of of its its potential potential for for receiving runoff receiving runoff fromfrom the the SSES.
SSES. Drinking Water Drinking Water LTAW is LTAW is considered considered an an indicator indicator Treated water was Treated water was sampled sampled time time location.
location. proportionally by proportionally by an an automatic automatic sampler.
sampler.
The sampler The sampler waswas typically typically setset to to obtain obtain Sediment Sediment three 12-ml three 12-ml aliquots aliquots every every twenty twenty Sediment sampling was Sediment sampling was performed performed in in minutes. Weekly, minutes. Weekly, the the water water obtained obtained by by the spring the spring andand fail atat fail i'ndicator i'ndicator locations locations this sampler this sampler waswas retrieved retrieved for for both both 7B and 7B and 12F12F andand control control location location 2B 2B on on biweekly and biweekly and monthly monthly compositing.
compositing. J 21 21 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
Aquatic Patlnvar Aquatic Patlnvar Monitoring Monitoring Fish , ),' Monitoring Results Monitoring Results Fish were obtained Fish were obtained by by electrofishi~g. ~ ?*
Electrofishing stuns Electrofishing stuns the the fishfish and and allowsallows Surface JVater them to them to float float to to the the surface surface so so that that tho~~ Results Results fromfrom specific specific sample sample analyses analyses ofthe desired ofthe desired species species and and sufficient sufficient si~e of surface of surface water water may may be be found found in in can be can be sampled.
sampled. Sampled Sampled fish fish include, include, Tables 1-2 Tables 1-2 and and 1.;3 1.;3 of of Appendix Appendix I. I. A A recreationally important recreationally important species, species, such such as as summary of summary of the the 2003 2003 surface surface waterwater data data smallmouth bass, smallmouth bass, and and also also channel channel i may be may be located located in in Table Table G G ofof catfish catfish and and shorthead shorthead redhorse. redhorse. The The " Appendix G.
Appendix Comparisons of G. Comparisons of 2003 2003 , ,
fish fish are are filleted filleted and and the the edibleedible portions portions , monitoring results monitoring results with with those those of of past past are are kept kept for for analysis.
analysis. years may years may be be found found in in Tables Tables H H 22
- ' ~.
through H through H 44 of of Appendix Appendix H H ..
Sediment Sediment Shoreline sediment was Shoreline sediment was collected collected to to The Nuclear Regulatory The Nuclear Regulatory Commission Commission depths of depths of four four feet feet of of water.
water. (NRC) requires (NRC) requires that that averages averages ofthe ofthe
..... ' activity levels activity levels forfor indicator; indicator; Sample Preservation Sample Preservation environmental monitoring environmental monitoring locationslocations and and and Analysis' and Analysis' for control for control environmental environmental monitoring'monitoring' locations of locations of surface surface water, water, as as well well as as other monitored other monitored media, media, be be reported reported to to Sllrface and,Drinking Sllrface and,Drinking Water Water the NRC the NRC annually.
annually. Data Data fromfrom the the '
Surface and Surface drinking water and drinking water samplessamples ,. following three following three surface surface water water ,
were analYzed monthly were analYzed monthly for for ~eta monitoring locations were monitoring locations were averaged averaged activities, the activities, the activities activities of of gamma-gamma- together together as as indicators indicators for for reporting, reporting, ;
emitting radion~clides, and emitting and tritium tritium '\' purposes: one purposes: one location location (6S5) (6S5) on on the the acti~ities. Biweekly Biweekly composite composite samp'l~s . Susquehanna River Susquehanna River doWnstream doWnstream 'of 'of the the were anaIYzcdforI-13'1.
were anaIYzcdforI-13'1. In In addition, addition, SSES, Lake*Took*a While SSES, While (LTA (LTAW) W) drinking water samples drinking water samples were were analyZed, analyZed, '. adjacent to adjacent to the the river, river, and and thethe SSES SSES '
for gross for gross alpha alpha activity.
activity. ;/;1 cooling tower,blowdown cooling tower,blowdown discharge" discharge" r* I ~" * , ' ..
(CTBD) line (CTBD) line toto the the river river (2S7).
(2S7).
The The useuse of~tri~~cid and and sodium." ~. "i bisulfite bisulfite as as presen;atives presen;atives in ,surface an'~ , ,
in ,surface Technically; the Technically; CTBD line the CTBD line is is not not part part drinking water drinking water samples samples ~\Y~ j 1 ; ** ,t:;,:,:
of the environment of the environment.. .. The The CTBDCTBD line line isis aa discontinued in discontinued in _~003 (at (at d.t d.tee req~es.t ~f..:: below ground below ground pipe pipe to to which which the the public public '
thevendorlabora!ory), .: ,::' "';'1.1'-
thevendorlabora!ory), has no has no access; access; contrary contrary to' to' the the other-:
- ~ environmental monitoringmonitoring locationslocations on on
, ~ ," .. . .1 t ,'"jj environmental Sedi;lIent and Fish' ,;, ;;::. the Susquehanna the Susquehanna River River to to which which the the .; .
Fish are frozen Fish are frozen untiluntil shipment.
shipment. All All " ..' public does public does havehave access.
access. However,:
samples are samples are analyzed analyzed by by gamma, gamma, . . . , currently there currently there is is no no automatic automatic .. ' '
spectroscopy spectroscopy for for the activities of the activities of any any composite sampling composite sampling of of an an indicator indicator gamma emitting gamma emitting radignuclides radignuclides that that mi:\y mi:\y ,, location on location on the the Susquehanna Susquehanna River, River, so so .'
be present.
be present. . ". . the CTBD the CTBD line line from from the the SSES SSES is is I , . ,~. " . included as included as an an indicator indicator monitoring monitoring 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report 22 22
II II Aquatic PatltwavMonitoring Aquatic PatltwavMonitoring location location in in the the radiological radiological as the discharged as the discharged water water mixes mixes with with thethe envirorunental monitoring envirorunental monitoring program.
program. '
much larger much larger flow flow of of river river water.
water. The The mean flow mean flow rate rate of of the the Susquehanna Susquehanna Most of Most of the the water water entering entering the the River in River in 2003 2003 was was approxhllately approxhllately Susquehanna River Susquehanna River through through the the SSES SSES 9,910,000 gpm:
9,910,000 gpm: This This is is more more than than CTBO line CTBO line isis simply simply water water that that was was 1,900 1,900 tim~s the the required required minimum minimum flow flow taken from taken from the the river river upstream upstream of of the the rate through rate through the the CTBO CTBO for for discharges discharges to to SSES, used SSES, used for for cooling cooling purposes purposes be permitted.
be permitted.
without being without being radioactively!
radioactively! :'
contaminated by contaminated by SSES SSES operation, operation, and and The amounts of The amounts of radioactively radioactively returned to returned to the the river.
river. Nevertheless, Nevertheless, contaminated water contaminated water beingbeing discharged discharged batch discharges batch discharges of of relatively relatively small small are small.
are small. Nevertheless, Nevertheless, sensitivesensitive volumes of volumes of slightly slightly radioactively radioactively analyses of analyses of the the water water samples samples can can often often contaminated water contaminated water are are mademade to to the the detect the detect the low low levels levels of of certain certain types types of of river through river through the the SSES SSES CTBO CTBO at at times times radioactivity in radioactivity in the the CTBO CTBO water water throughout each throughout each year.
year. The The water water is is following dilution.
following dilution. ThoughThough the the levels levels released from released from tankstanks of of radioactively radioactively of radioactivity of radioactivity measured measured in in the the CTBOCTBO
,, contaminated contaminated water water on on sitesite to to the the CTBO CTBO water are water are generally generally quite quite low, low, theythey tend tend and mixes and mixes with,the with,the noncontaminated noncontaminated to be to be higher higher than than those those in in the the river river water already water already present present in in the the CTBO.
CTBO. downstream of downstream of the the SSES.
SSES. Most Most Flow rates Flow rates from from the the tanks tanks containing containing radionuclides discharged radionuclides discharged from from the the SSES SSES radioactively contaminated radioactively contaminated water water beingbeing CTBO are CTBO are atat such such low low levels levels in in the the discharged to discharged to the the CTBO CTBO vary vary based based on on downstream river downstream river water water that, that, even even withwith the radioactivity the radioactivity level level of of the the batch batch the sensitive the sensitive analyses analyses performed, performed, they they release. In release. In addition, addition, the the minimum minimum flow flow cannot be cannot be detected.
detected.
rate for rate the returning for the returning water water in in the the CTBO CTBO is maintained is maintained at at aa flow flow raterate ofof 5,000 5,000 When When the the radioactivity radioactivity levels levels fromfrom the the gpm or gpm or higher.
higher. These These requirements requirements are are CTBO samples CTBO samples throughout throughout the the yearyear areare in place in place to' to' ensure ensure adequate adequate dilution dilution of of averaged with averaged with those those obtained obtained from from radioactively contaminated radioactively contaminated water water by by thethe actual downstream actual downstream monitoringmonitoring returning noncontaminated returning noncontaminated water water in in thethe locations, the locations, the result result is is an an overall overall CTBO prior CTBO prior to to entering entering the the river.
river. indicator location indicator location average average that that is is too too high to high be 'representative' to be 'representative' of of the the actual actual At the point At the point thatthat CTBO CTBO water water enters enters the the average radioactivity average radioactivity levels levels of of thethe river, additional, river, additional, rapid rapid dilution dilution of of the the downstream river downstream river water.
water. As As thethe discharged water discharged water by by the the river river is is following discussions following discussions are are reviewed, reviewed, promoted by promoted by releasing releasing it it through through aa consideration should consideration should be be given given to to this this diffuser. The diffuser. The diffuser diffuser is is aa large large pipe pipe inflation of inflation of average average radioactivity radioactivity levels levels with numerous with numerous holes holes in in it it that that isis from the from the inclusion inclusion of of CtBO CtBO (location (location positioned near positioned near the the bottom bottom of of the the river.
river. 2S7/6S7) results 2S7/6S7) results in in the the indicator indicator data data CTBO discharges CTBO discharges exit exit the the diffuser diffuser that is that is averaged.
averaged.
through the through the many many holes,holes, enhancing enhancing the the mixing ofthe mixing ofthe discharge discharge and and river river The 2003 The 2003 datadata for gross beta for gross beta activity activity waters. The waters. The concentrations concentrations of of analyses analyses of of surface surface water water indicator indicator contaminants are contaminants are reduced reduced significantly significantly locations is locations is higher higher than than those those of of 2002.
2002.
23 23 2003 Radiological, 2003 Radiological, Environmental Environmental Monitoring Monitoring Report Report
Aqilatic Patllway Aqilatic Monitoring Patllway Monitoring The The 2003 2003 !mean !mean gross gross beta beta 'aativity of of ',: ' periods periods of of thethe SSES. SSES. The The 2003 2003 control control 6.1 pCilliter 6.1 pCilliter for for indicator indicator locations' is' .', ~ i mean activity mean activity is is less less thanthan thethe averages averages greater greater than than the the 2002 2002 indicatorindicator mean mean , of the of the annual annual means' means' for for control control gross beta gross beta activityactivity of of 5.4 5.4 pCilliter.
pCilliter. The", locations for locations for the the prior prior operational operational and and 2003 indicator 2003 indicator mean mean activityactivity is is within" ,r , preoperational preoperational period period of of the the SSES.-
SSES.-
the range the range of of thethe annual annual means means for for the the ~ ,
previous operational previous operational period period of of the the ' ' ,,; , Throughout the Throughout the course course of of aa year, year, iodine-iodine-SSES. The SSES. The 2003 2003 mean mean gross gross betabeta ,,;,-; 131 is 131 is typically typically measured measured at at levels levels in in activity of activity of 2.4,pCilliter 2.4,pCilliter for control for control "1 excess of excess of analysis analysis MDCs MDCs in in some some locations is locations is 'Jess
'Jess than than the the 2.9 2.9 pCi/liter pCi/liter ; " samples obtained samples obtained from from control control surface surface forthe forthe 2002 2002 control control mean mean grossgross beta' ;: :-' water monitoring water monitoring locations locations on on thethe activity.
activity. 'The 'The 2003 2003 controlcontrol mean mean ",' Susquehanna River Susquehanna River upstream upstream of of the' activity is activity is within within the the rangerange of of thethe annual annual
- SSES as SSES as well well as as indicator indicator locations locations means for means for previous previous operationaloperational periods~' : downstream of downstream of thethe SSES.':
SSES.': As As The 2003 The 2003 control control mean mean is is bel'ow bel'ow the' the' ':;:: determined by determined by measurements measurements of of range of of annualannual means means for" for" range , samples obtained samples obtained by by the the 'SSES
'SSES REMP, REMP, p~eoperati~nal periods. periods. 'Refer 'Refer to to , -, thernean iodine-i31 thernean iodine-i31 activity activity levellevel from from Figure 9 Figure 9 which which trends trends gross gross betabeta ' , " , the CTBD the CTBD forall forall of of 2003 2003 was was :, '
activitie~ separately separately for for surface surface water',
water', i'" approximately'0.78 approximately'0.78 pCilliter. pCilliter. This ni"ay This ni"ay indjc~to~. and control ,lo~ations quarter~y and control be compared be compared to to thethe activity activity levellevel of of from 1975 from 1975 thro'ughthro'ugh 2 0 0 3 . ' :;
0.26 pCi/liter pCi/liter for for control control surface surface water water monitoring locations monitoring locations in in 2003.
2003.
Comparison of thethe 2003 2003 indicator indicator mean' mean' ,,
~ , t' 1 Comparison of (6.1 pCill)to (6.1 pCill)to the the 2003 2003 control control mean mean , Iodine-131 Iodine-131 from from the the discharge discharge 'of 'of (2.4 pCi/l)
(2.4 pCi/l) suggests suggests aa contributioncontribution of of :,': I, medical wastes medical wastes into into the the Susqueh,anna Susqueh,anna beta activity beta activity from from the the SSES.SSES. The The 2003 2003 ': 'J River upstream River upstream of of thethe SSES SSES is is drawn drawn '
data is data is similar similar in in this this regard regard to to the the ",', into the into the SSES SSES cooling cooling tower tower basin's'*
averages of averages of annual' annual' means means for for indicator indicator ' through the through the SSESSSES River River Water Water Intake:
Intake:
and control and control locations locations for for the' prior' :', ~
the' prior' Stn.fcture. It Stn.fcture. It is is reasonable reasonable to to assume' assume' operational period.
operational period. 'During 'During the the prior prior '.":" that concentration that concentration of of the the already already ':
operatj~naI~nod, the the averageaverage of of ,', existing iodine-131 existing iodine-131 in in the the cooling cooling towertower annmll iridic'ator annmll iridic'ator means means exceeds exceeds the the ' , basins occiiis basins occiiis as as itit does does forfor other" other" ,
average of average of annual annual controlcontrol m'eans m'eans for for " '::,~': substances found substances inin found the'river. the'river. For For gross beta gross beta activity.
activity. . ' , : I " ",.: example, the example, the SSES SSES routhielyassumes routhielyassumes concen'trati'on factors concen'trati'on factors in in the the basin basin for for The 2003 The ;
2003 means ,\ '
means foi foi iridin~~131'activityi ~;
- . ~ I' . * , .... "(
calcium offouT'to calcium offouT'to five five times times the the at indicator at indicator and and control control surface surface water water ' concentrations in'th;e concentrations in'th;e ri'ver' ri'ver' water water {
monitoring monitoring location's location's ~~re 0.~6'pci/i!t~V' ent~ri'rlg thethe basins, basins, based based 'on 'on past past and ~)'26 pCillitei~ 'respectively.,
and 'respectively., The',' .," measurements. :This measurements. :This concentrating, concentrating, '
2003 indicator 2003 indicator and and control control means means 'are:':' ,.'. effect occurS effect occurS because because of of the the evaporation evaporation less than less than the the corresponding corresponding 2002 2002 means.
I, 1 means. '
." '-J '
of the of the water water :the inin :the basins, basins, ieavin'g' ieavin'g' ""
The 2003;ipdic,at?r m~a~ ~ctivity is The 2003;ipdic,at?r is :, " 1 ' behind most behind most dissoiv~~f and and suspended suspended ,
greater than greater than the the averages averages of of the the annual, annual, ,', materials in' materials in' the the unevapornted unevapornted water water '
means for means for indicator.1ocations indicator.1ocations for for the',
the', "-' remaining in remaining in the the basins~ If a '
prior operational prior operational and and preoperational preoperational "f I' concentration concentration factor factor of of four four forfor iodine-iodine-2003 RadiologicaJ 2003 RadiologicaJ Environmental Environmental Monitoring Monitoring Report Report 24 24
II II Aquatic Pat/nvav llfonitoring 131 were to 131 were to be be applied applied to to the the 2003 2003 from the SSES from the SSES to to the the Susquehanna Susquehanna mean iodine-I31 acti~ity level mean iodine-I31 level forfor the the River during River during 2003. 2003.
control samples control samples from from the the Susquehanna Susquehanna River, aa mean River, mean concentration concentration of of ' . The 2003 mean The 2003 mean tritium tritium activity activity for for 1.04 pCilliter 1.04 pCilliter for iodine-13 ii itl for iodine-13 itl the the basin basin indicator locations indicator locations is more than is more than the the water and water and thethe water water being being discharged discharged corresponding,2002 mean.
corresponding,2002 mean. The The 2003 2003 from the from the basi~ woul~ b~ expected expected.. The The means for means for tritium tritium activity activity at at indicator indicator actual 2003 actual 2003 meanmean of of 0.78 0.78 pCilliter pCilliter for for and contr-ollocations and contr-ollocations were were the CTBD the CTBD iodine-I31 iodine-I31 activity activity levellevel waswas 1,567 pCilliter 1,567 pCilliter and and 31.8 31.8 pCi/liter, less than less than this.
this. respectively,',The2003 indicator respectively,',The2003 indicator mean mean is greater is greater thanthan the the annual annual average average mean mean Because iodine-131 Because iodine-131 is is radioactive, radioactive, for prior for prior operational operational and and preoperational preoperational unlike unlike thethe calcium calcium that that hasheen hasheen periods of periods of the the SSES.
SSES. Note Note thatthat the the 2003 2003 iodine-131 is measured, iodine-131 measured, is removed removed from from mean tritium mean tritium activity activity at at indicator indicator the water the water while while it it is is in in the the baSins baSins locations i~ higher locations higher thanthan thethe range range for for through the through the radioactive radioactive decay decay process, process, both operational both operational and and preoperational preoperational Thus, it Thus, it might might be be expected expected ihat ihat thethe net net periods. The periods. The control control meanmean is is within within thethe concentration factor concentration factor for for iodine-131 iodine-131 range of range of the the corresponding corresponding annual annual mean mean would be would be somewhat somewhat less less than than that that forfor reported for reported for thethe prior prior operational operational period period calcium, considering'this calcium, considering'this additional additional of the of the SSES.
SSES. Refer Refer to to Figure Figure 10 10 which which removal process.
removal process. The The extent extent to to which which trends tritium trends tritium activity activity levels levels separately separately the iodine-I31 the iodine-I31 concentration concentration factor factor is is for surface for surface waterwater indicator indicator and and control control less than less than that that for for calcium calcium would would depend depend locations from locations from 1972 1972 through through 2003. 2003.
the mean on the on mean residence residence time time for for the the "
~
II water in water in the the basins basins compared compared to to iodine-iodine- The 2003 indicator The 2003 indicator mean mean tritium tritium levellevel 131 's 131 's radioactive radioactive hat'f-life hat'f-life -- thethe greater greater for all for all surface surface water water locations locations can can be be the ratio the of the ratio of the mean mean residence residence time time to to misleading for misleading for those those interested interested in in the the the half-life, the half-life, thethe smaller smaller the the mean tritium mean tritium l<:vel l<:vel in in the the Susquehanna Susquehanna concentration factor.
concentration factor. A A mean mean residence residence River downstream River downstream of of the the SSES SSES for for time for time for water water in in the the basins basins is is expected expected 2003. The 2003. The muchmuch higherhigher levels levels of of tritium tritium to be to be about about twotwo days, days, ThisThis is is only only about about observed in observed the CTBD in the CTBD line line (location (location one-fourth of one-fourth of the the approximately approximately eight- eight- 2S7/6S7), when 2S7/6S7), when averaged averaged with with the the low low day half-life day half-life of of iodine-13l,"
iodine-13l," Thus, Thus, levels from levels from the the downstream downstream location location radioactive decay radioactive wO,uld ri~~ be decay wO,uld be :: 6S5 sample 6S5 sample analysis analysis results results distort distort thethe expected to expected to reduce reduce the the concentration concentration real environmental real environmental picture. picture. The The meanmean factor for factor for iodine-I3I iodine-I3I by by aa large large amount.
amount. tritium activity tritium activity level level from from indicator indicator Therefore, the Therefore, the difference difference betweenbetween the the location 6S5 location 6S5 for for 2003 2003 was was 140 140 pCilliter, pCilliter, 2003 mean jodine~ 131 2003 mean 131 activity activity of of about about which is which is greater greater than than the mean tritium the mean tritium 0,78 pCi/liter 0,78 pCi/liter in the CTBD in the CTBD and and thethe 2003 2003 activity, 31.8 activity, 31.8 pCiIliter, pCiIliter, for the control for the control mean iodiIie-131 mean iodiIie-131 activity activity for for the the control control location, but location, but is is within within the the range range of of prior prior location of location of 0.26' 0.26' pCilliter pCilliter sliould sliould be be the the operational' and operational' and preoperational preoperational periods. periods.
result of result of concentration concentration in the basins.
in the basins. '
Iodine-I31 Iodine-I31 was was "not "not reported reported to to have have In spite of In spite of the the fact fact that that thethe tritium tritium been discharged been discharged with with water water released released activity levels activity levels reported reported for for 2S7/6S7 2S7/6S7 are are from the from the discharge discharge line line prior prior to to dilution dilution 2S 2S 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
-- Aquatic PathlVa)~ Monitoring
, . : ' . , . ' , : - .I ~ .' r, ~
in the river, in the river, the the highest highest quarterly quarterly Susquehanha Susquehanha ruver ruver upstream upstream of of the the average tritium average tritium actiVity'reported actiVity'reported at at " ! ' SSES .and SSES .and th~iefore n~ drinking drinking waterwater 2S7/6S7 during 2S7/6S7 during 20032003 was' was' control monitoring control monitoring locations. locations. Danville' Danville' approximately 6,990 approximately 6,990 pCilliter pCilliter for for the, the, ' drinking water drinking water analysis analysis resultsresults may may be be first quarter, first quarter, well well below below the the NRC NRC non-non- ' compared to compared to thethe results results for for surface surface I' routine reporting levels routine reporting levels for for quarterly quarterly '- - .. water water control monitoring control monitoring locations.locations.
average activityactivity levels levels of of '
average : i'; ,
20,000' pCiIliter 20,000' pCiIliter when when aa dnnkingdnnking water water ' Results from Results from specific specific samplesample analyses analyses pathway' exists pathway' exists or or 30,000 30,000 pCiniterpCiniter wh'en wh'en of drinking of drinking water water may may pe pe found found in in no drinking no drinking water water pathway pathway exists: exists: .' ' Table 1-4 Table 1-4 of of Appendix Appendix I. I. AA summary summary of of the 2003 the 2003 drinking drinking water water data data niay niay be be ,"
The The tritium tritium activityactivity reported reported in in the the located in located in Table Table G G ofof AppendixG~ ,
CTBD CTBD line line from from location location 2S'7/6S72S'7/6S7 is,'*; Co~parisons of of 2003 2003 'f!lonitoririg
'f!lonitoririg results results attributable to attributable to the the SSES.
SSES. Refer Refer to to the the with those, with those, of of past past years years may may be be found found inin "Dose from "Dose from the the Aquatic Aquatic Pathway" Pathway" , 'r: j Tables HS Tables HS through through H H7 of Ap~~~dix H.'
7 of discussion at discussion at the the end end of of this this section section for'for' additional iriformation' additional iriformation' on on the the projected" Gross alpha Gross alpha activity activity has been monitor~d has been dose 'to dose 'to 'the
'the population population from from tritiumtritium 'and'
'and' in'drinking in'drinking water water since since 1980.
1980. 'Gross
'Gross '
other radionuclides other radionuclides in in thethe aquatic aquatic ::', alpha activity alpha activity has has ~een ob~erved at at ",
pathway attributableto'the pathway attributableto'the SSES. SSES. !' levels above levels above the the analysis'MDCs analysis'MDCs in in aa
' ; "I small minority small minority of of the the samples samples duringduring With the With the following following exceptions, exceptions, no no .,, most years most years sincesince 1980. 1980. The The 2003 2003 'mean
'mean '
gamina-errutting radion~clides were' gamina-errutting were' " gross alpha gross alpha activity activity level level for for ,drlnldng
,drlnldng " ,
measured in measured in surface surface water water primary primary : water was water was 0.18 0.18 pCiniter.
pCiniter. The The 20032003 ..
samples at samples at an an activity activity level level exceeding exceeding " mean alpha mean alpha activity activity level level is is within within the the an analysis an analysis MDC MDC in in 2003:
2003: potassium-potassium- range of range of the the corresponding corresponding annual annual 40 and 40 and iodine-I3l.
iodine-I3l. means fo'r means fo'r the the prior prior operational operational years. years.
.*.. t;.
No gross No gross alpha alpha activity'in activity'in dnnking dnnking ,
Drinlf,i~g' Water Water water during water during '2003 '2003 is is attributed attributed to to liquid liquid Drinking' water Drinking' water was was monitored monitored during during ,: discharges from discharges from theSSEStheSSES to'the' to'the' , ,"
2003 at 2003 at the'the' Danville Danville Water Water CompanY'sCompanY's ilil Susquehanna'River', .,
facility '26 facility miles'WSW ofth~ SSES
'26 miles'WSW SSES on'~'
the SusquehaiUia the SusquehaiUia River. River. From From 1977:;-:' Gross Gross beta beta activity activity has has been been monitored' monitored' (when dritlking'water (when dritlking'water samples'\vere samples'\vere first' first' in in diinking diinking water water since since ii 977.
977. 'Gross
'Gross '
thi-oughJ 984;driIild~g collected) thi-oughJ collected) water' water' beta activity beta activity is' is' typically ineasurc'd at typically ineasurc'd at '
samples were' samples were' also also obtained obtained from from the':' ': levels exceeding levels exceeding the the MDCs MDCs in'drinking in'drinking :
BerWickWater Companyatlocation':' J' BerWickWater water samples~ The water The 2003 2003 mean mean grossgross 12F3; s;i'riiiies 12F3; s;i'riiiies WSW WSW 'Of 'Of the' the' SSES.'!'.' ," beta activityievel beta activityievel for'driflkingfor'driflking water" water" The The drinking drinking water water supply supply for for the:the: ' :~ .. (! was 2J3 was 2J3 'pcilliter~ The The 2003 2003 mean'is' mean'is' BeiwickWater Company BeiwickWater Company is is not," " " ,. i' belO\y the belO\y the 20022002 'mean
'mean gross gross beta beta activity activity however, :wilierfroiftihe however, :wilierfroiftihe Susquehanna:
Susquehanna: :", level for level for drinking drinking water water but\viihin but\viihin the': ,
River; River; it it is is actually actually well well water," ":-:r,l' water,"
',':ttur range of range of thethe corresponding:
corresponding: annual annual ' ','
t~.~ ~.~.
- means for means for prior prior operational operational periods. periods.
There are'noknow~ drinking There drinking water water <" ." , The 2003 The 2003 mean mean below isis below the the range range of of supplies in supplies in Pennsylvania Pennsylvania on on the' the' , ',,; : ~I' the 'corresponding the 'corresponding annual annual 'means for' 2003 Radiologieal 2003 Radiologieal Environmental Environmental Monitoring Monitoring Report Report 26 26
Aqllatic PatltHJayMonitoring preoperational peJiods. ~efer to preoperational peJiods. to above the above the analysis analysis MDCs MDCs for for gamma gamma Figure II, Figure II, w~ich trerds trerds gross gross beta beta spectroscopic spectroscopic analysesanalyses of of drinking drinking waterwater activity levels activity levels separately separately for for drinking drinking samples during samples during 2003.2003.
water indicator water indicator arid arid coritrollocations coritrollocations .
from 1977 from through '2003~ No 1977 through No gross gross beta beta Fish activity in activity in drinking drinking waterwater during during 2003 2003 is is Results from specific Results from specific sampJe sampJe analyses analyses attributed to attributed to liquid liquid discharges discharges from from the the of fish of fish may may be be found found in in Table Table II 55 of of SSES to SSES to the the Susquehanna Susquehanna River. River. Appendix I.
Appendix I. A A summary summary of of the the 2003 2003 fish data fish data may may be be located located in in Table Table G of G of Iodine-I31 was Iodine-I31 was measured measured in in excess excess of of Appendix G Appendix G.... AA comparison comparison of2003 of2003 analysis analysis MDCsMDCs in in 22 out out of26~rinking monitoring results monitoring results withwith those those of of past past water samples water samples in in 2003.
2003. This This compares compares years may years may be be found found in in Table Table H H 88 ofof with results with results from from 6 6 samples samples for for which which Appendix H. H.
analysis MDCs analysis MDCs ~ere ex'ceeded inin ex'ceeded 2002. 2002.
Appendix The 2003 The 2003 mean mean iodine-I31 iodine-I31 activity activity levellevel Three species of Three species of fish fish wer,?
wer,? sampled sampled at at in drinking in drinking water water samples samples was was each of each of one one indicator indicator location location and and one one 0.18 pCiIliter.
0.18 pCiIliter. ThisThis isJess isJess than than the the control location control location on on the the Susquehanna Susquehanna 2002 mean 2002 mean drinking drinking waterwater activity activity levellevel River in River in May May 2003 2003 andand again again in in October October of 0.22 of 0.22 pCilJiter.
pCilJiter. Also,Also, itit is is less less than than 2003. The 2003. The species species included included the the the 2003 the 2003 mean mean of of 0.26 0.26 pCiJliter pCiJliter for for the the following: smallmouth following: smallmouth bass, bass, channel channel surface water surface water control control location.
location. No No catfish, shorthead catfish, shorthead redhorse, redhorse, 'and 'and white white iodine-I3l activity iodine-I3l activity in in drinking drinking water water sucker. In sucker. In addition, addition, one one largemouth largemouth during 2003 during 2003 isis attributed attributed to to liquid liquid bass was bass was sampled sampled from from PPL's PPL's LTAW. LTAW.
discharges from'the discharges from'the SSES SSES to to the the A total A of 13 total of 13 fish fish were were collected collected and and Susquehanna River.
Susquehanna River. analyzed.
analyzed.
Tritium Tritium was was measured measured in in excess excess of of The only gamma-emitting The only gamma-emitting radionuclideradionuclide analysis MDC~ twice analysis twice in 2003 in, in 2003 in, reported in reported in excess excess of of analysis analysis MDCs MDCs in in drinking water.,
drinking water., The The 2003 2003 mean mean tritium tritium fish during fish during 2003 2003 was was naturally naturally activity level activity level for'drinking for'drinking waterwater was was occurring potassium-40.
occurring potassium-40. The The 2003 2003 62 pCiJliter.
62 pCiJliter. TheThe 20032003 me~ is is equal equal to to indicator and indicator and control control means means for for the the the averages the averages of of the the corresponding corresponding activity levels activity levels of of potassium-40 potassium-40 in in fish fish annual means annual means for for both both the the prior prior were 3.57 were 3.57 pCiJgram pCiJgram and and 3.16 3.16 pCi/gram, pCi/gram, operational and operational and preoperational periods preoperational periods respectively. The respectively. The 2003 2003 indicator indicator and and of the of the SSES.
SSES. The The 2003 2003 mean mean tritium tritium control means control means were were less less than than thethe 2002 2002 activity level activity level for for driIlking driIlking water water is is means. Both means. Both the the 2003 2003 indicator indicator and and higher than higher than the the 2003 2003 meanmean tri~ium control me~ns are control are within within the the ranges ranges of of activity level activity level for for the the surface surface w~ter their corresponding their corresponding annual annual means means for for control location.
control location. Tritium Tritium activity activity in in prior operational prior operational years. years. The The 2003 2003 drinking water drinking water can can bebe attributed attributed to to indicator mean indicator mean is is greater, greater, than than the the range range liquid liquid discharges discharges from from thethe SSES SSES to to the the of corresponding of corresponding anIlUal anIlUal means means for for Susquehanna Susquehanna River. River. preoperational periods.
preoperational periods. !he !he 20032003 control mean control mean is is within within the the range range of of With With thethe exception exception ofI~13.I, no no gamma-gamma- corresponding annual corresponding annual means means for for emitting radionudides emitting radionudides were, were, measured measured preoperational periods.
preoperational periods. Naturally Naturally 27 27 2003 Radiological 2003 Radiological. Envir~nmental ,
Monitoring Report Monitoring Report
Aquatic Pathway Aquatic Pathway Afonitoring Afonitoring occuning 'p~tassium-40 in occuning fish is in fish is not,* . 2002 meari.... The 2002 meari The 2003 2003 controf controf mean mean attributable to attributable to the the liquid liquid discharges discharges ,,;. radium-226 activity radium-226 activity is is lower lower than than thethe from the from the SSES SSES to to the the Susquehanna' Susquehanna' . corresponding 2002 corresponding 2002 means.
means. The The 2003 2003 River. .
River radium":226 mean radium":226 mean was was above above the the range range of corresponding of corresponding annual annual means means for for all all Sedilllellt Sedilllellt prior operational prior operational years.
years. The The 2003 2003
" control mean control mean was was within within thethe range range of of Shoreline sediment was Shoreline sediment was sampled sampled in in May May 2003 and 2003 and again again in in October October 2003. 2003. .' ,!
corresponding annual corresponding annual means means forfor all all Results from Results from specific specific sample sample analyses analyses prior operational prior operational years.
years.
of sediment of sediment may may be be found found in in Table Table 1-6 1-6 ~.
of Appendix of Appendix 1. 1. AA summary summary of of the the 2003 2003 The 2003 indicator The 2003 indicator and and control control means means sediment data sediment data isis located located in in Table Table G G or, . for thorium-228 for thorium-228 activity activity levels levels in in Appendix G.
Appendix G. Comparisons Comparisons of of 2003 2003 .,; shoreline sediment shoreline sediment were were 3.23.2 and and monitoring monitoring results results withwith those those of of past past 3.0 pCi/gram, 3.0 pCi/gram, respectively.
respectively. The The 2003 2003 years may years may be be found found in in Tables Tables H H 99 indicator and indicator and control control means means are are higher higher through H through H 12 12 ofof Appendix Appendix H. H. " I ;
than the than the corresponding corresponding 2002 2002 means.
means.
The 2003 The 2003 indicator indicator and and control control means means Naturally occuning Naturally occuning potassium-40, potassium-40, are greater are greater than than the the range range of of radium-226, and radium-226, and thorium-228 thorium-228 were were . corresponding means corresponding means for for prior prior measured at measured at activity activity levels levels above above " operational years.
operational years. TheThe naturally naturally analysis MDCs analysis MDCs in in aUaU shoreline shoreline sediment sediment occuning radionuclides occuning radionuclides in in sediment sediment samples in samples in 2003.
2003. discussed above discussed above are are not not attributable attributable to to the liquid the liquid discharges discharges from from thethe SSES SSES to to ..
The 2003 indicator The 2003 indicator and and control control meansmeans the Susquehanna the Susquehanna River River.. ..
for potassium-40 for potassium-40 activity activity levels.levels. in in
.. shoreline shoreline sediment sediment were were 12.3 12.3 pCi/gram pCi/gram Cesium-137 was Cesium-137 was measured measured at at activity activity and 12.9 and 12.9 pCilgram,.
pCilgram,. respectively.
respectively. :The :The levels levels in in shoreline shoreline sediment sediment exceeding exceeding 2003 indicator 2003 indicator mean mean for for potassium-40 potassium-40 analysis MDCs analysis MDCs in of 66 analyses in 55 of analyses during during activity is activity is less less than than the the corresponding corresponding 2003. The 2003. The 2003 2003 indicator indicator and and control control 2002 mean.
2002 mean. The The 2003 2003 control control mean mean is is means for means for cesium-137 cesium-137 activity activity levels levels in in greater than greater than the the corresponding' corresponding' 2002 2002 sediment were sediment 0.07 pCi/gram were 0.07 pCi/gram and and mean. The mean. The 2003 2003 indicator indicator and and control control 0.08 pCi/gram, 0.08 pCi/gram, respectively.
respectively. The The 20032003 means were means were withinwithin the the ranges ranges of of indicator mean indicator mean is is greater greater than than thethe corresponding annual corresponding annual means means for for all all corresponding 2002 corresponding 2002 mean mean .. .. The The 2003 2003 prior operational prior operational years. years. The 2003 The 2003 control mean control mean is is less less 'than
'than the the indicator and indicator and control control means means were were corresponding 2002 corresponding 2002 mean.
mean. The The 2003 2003 greater than greater than the the ranges ranges of of corresponding corresponding indicator and indicator and control control means means are are Jess Jess means for means for preoperational preoperational periods. periods. than the than the average average of of corresponding corresponding annual means annual means for for both both prior prior operational operational The 2003 indicator The 2003 indicator and and control control means means as well as well asas preoperational preoperational years. 'The' years. 'The' for radium-226 for radium-226 activity activity levels levels inin cesium-137 in cesium-137 in sediment sediment is is attributed attributed to to shoreline sediment shoreline sediment were were 2.382.38 pCi/gram pCi/gram residual fa110ut residual fa110ut from from past past atmospheric atmospheric and 1.6 and 1.6 pCi/gram, pCi/gram, respectively.
respectively. The The nuclear weapons nuclear weapons tests.
tests.
2003 indicator 2003 indicator meanmean radium-226 radium-226 activity is activity is higher higher thanthan thethe corresponding corresponding 2003 Radiological 2003 Radiological EnYironmental EnYironmental Monitoring Monitoring Report Report 28 28
II **
Aquatic Pathway Aquatic Pathway Monitoring Monitoring Dose Dose from from the the Aquatic Aquatic This estimate is This estimate is 33 curies curies less less than than the the amount of amount of tritium tritium determined determined by by Pathway Pathway effluent monitoring effluent monitoring to to have have been been released to released to the the river river by by the the SSES SSES in in Tritium Tritium was was thethe only only radionuclide radionuclide 2003. This 2003. This agreement agreement between between the the identified in identified in 2003 2003 by by the the SSES SSES REMP REMP estimate based estimate based on on environmental environmental in the in the aquatic aquatic pathway pathway that that waswas monitoring and monitoring and thethe amount amount reported reported by by attributable to attributable to SSES SSES operation operation and and also also effluent monitoring effluent monitoring is is consistent consistent withwith included in included in the the pathway pathway to to man.
man. previous years previous years comparisons.
comparisons.
The total tritium The total tritium activity activity released released from from Given the total Given the total tritium tritium activity activity released, released, the SSES the SSES for for thethe year year was was estimated estimated the maximum the maximum whole-body whole-body and and organ organ based on based on REMP REMP monitoring monitoring results results forfor doses to doses to hypothetical hypothetical exposed exposed use in use in projecting projecting maximummaximum doses doses to to the the individuals in individuals in four four age age groups groups (adult, (adult, public. This public. This estimate estimate assumed assumed that that the the teenager, child, teenager, child, and and infant) infant) were were tritium was tritium was present present continuously continuously in in the the determined according determined according to to the the CTBD line CTBD throughout 2003 line throughout 2003 at at aa level level methodology of methodology of the the Offsite Offsite Dose Dose equivalent to equivalent to ,the
,the annual annual meanmean activity activity Calculation' manual Calculation' manual using using thethe RETDAS RETDAS level of level of tritium.
tritium. It was also It was also assumed assumed computer program.
computer program. This This is is in in that the that the annual annual average average activity activity levellevel ofof accordance with accordance with SSESSSES Technical Technical tritium being tritium being contributed contributed to to the the Requirement 3.11.4.1.3.
Requirement 3.11.4.1.3.
Susquehanna River Susquehanna River water water couldcould be be represented by represented by the the difference difference between between The maximum dose The maximum dose obtained obtained fromfrom thethe the annual the annual meanmean activity activity levels levels of of ingestion of ingestion of tritium tritium waswas estimated estimated at at the the tritium in tritium in the the CTBD CTBD line line (without (without nearest downriver nearest downriver municipal municipal waterwater correction for correction for cooling cooling tower tower basinbasin supplier via supplier via the the drinking drinking water water pathway pathway reconcentration) and reconcentration) and inin the the river river and near and near the the outfall outfall ofof the the SSES SSES upstream of upstream of the the SSES.
SSES. discharge to discharge to the the Susquehanna Susquehanna River River viavia the fish the fish pathway.
pathway. The The maximum maximum whole whole The annual mean The annual mean activity activity level level of of body and body and organ doses were organ doses were each each tritium in tritium in the the CTBD CTBD line (monitoring line (monitoring estimated to estimated to bebe approximately approximately location 2S7\6S7) location 2S7\6S7) for for 2003 2003 was was 0.0015 mrem.
0.0015 mrem.
4,416 pCiIl.
4,416 pCiIl. The The annual annual meanmean activity activity level for level for the the river river upstream upstream of of the the SSES SSES (monitoring location (monitoring location 6S6)6S6) was was approximately 32 approximately 32 pCill.
pCill. Thus, Thus, the the difference in difference in the the mean mean activity activity levels levels for for these two these two locations locations was was about about 4,384 pCi/I.
4,384 pCi/I. The The annual annual mean mean flow flow rate rate for the for the CTBD CTBD line line was was 7,703 7,703 gpm. gpm.
Using the Using the proper proper unit unit conversions conversions and and mUltiplying 7,703 mUltiplying 7,703 gpm gpm times times 4,384 pCiIl 4,384 pCiIl yields yields aa value value ,of ,of 67.2 67.2 curies curies for the for the estimate estimate of of tritium tritium released released during 2003 during 2003 based based on radiological environmental radiological on the the results results of environmental monitoring.
of monitoring. ,.J
,.J 29 29 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
FIGURE 9 FIGURE 9 -- GROSS GROSS BETA BETA ACTIVITY ACTIVITY IN IN SURFACE WATER SURFACE WATER pCi/Liter pCi/Liter 20 ~----------------------------------------------------------------~
18 18 PRE OPERA PRE OPERATIONAL TIONAL OPERATIONAL OPERATIONAL 16 14 14 12 12 10 10 88 66 4
4 22 o+-----------------~--------------------------------------~------~
-2
-2
-4 +-~~~~--~~~_r~~--~~~~~--~~~~~~--~~~~~~--~
~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~
~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~
-- Indicator --
Indicator Control Control G l, Gl,
))
FIGURE 10 FIGURE 10 -- TRITIUM TRITIUM ACTIVITY ACTIVITY IN IN SURFACE SURFACE WATER WATER pCi/Liter pCilLiter 3000 ~----------------------~--------------------------------~------------.
PREOPERATIONAL PREOPERATIONAL OPERATIONAL OPERATIONAL 2500 2500 2000 2000 1500 1500 Unit2 Unit2 1000 1000 Criticality Criticality
~
500 500
-500 +-~~~~~~--~~~~-r~~~~~~~~~~~~~--~~~~~~~~~
~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~
~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~
-- Indicator Indicator -- Control Control
cc cc cc FIGURE 11 FIGURE 11 -- GROSS GROSS BETA BETA ACTIVITY ACTIVITY IN IN DRINKING WATER DRINKING WATER pCilLitcr pCilLitcr 10~------------~~--------------------------------------------------~
9 9
PREOPERATIONAL PREOPERATIONAL OPERATIONAL OPERATIONAL 88 77 6
6 55 Unltl Unltl 44 33 2
2 1
1 O+-~~--~~-r~~~~-r~--~~-T--~~~~--~~~~--~~-T~~~~
f\'\
f\'\
~
Atmospheric Pathway Atmospheric Pathway Monitoring Monitoring Samplintfand 'Analysis Samplintfand 'Analysis INTRODUCTION INTRODUCTION t '!'
'if Air' Air' .
Atmospheric.
Atmospheric. monitoring monitoring by by th.e SSES" ~ "
th.e SSES" The 'SSES The 'SSES REMP REMP monitored monitored the the air air at at . ,
REMP involves REMP involves the the sampling sampling and, and, !ji:, fo~r indicator indicator locations locations and and twotwo control control analysis of analysis of air.
air. Because Because ihe ihe air air isis the the locations during' locations during' 2003.
2003. The The SSES SSES first medium first medium that that SSES SSES vent vent releases releases {" I Tech~ic~i ~equirements require require ..
enter enter inin thethe pathway pathway to to man, man, it it is is .;~ . i monitoring afonly monitoring afonly aa total total ofof five five site~. ,
fundamenta1 that fundamenta1 that it it be be monitored.
monitored. , .' : Monitoring is' Monitoring is' require~. at at three three locations, locations, Mechanisms Mechanisms do do exist exist forfor the the transport transport i.," at the at the SSES'site'boundaryin SSES'site'boundaryin different different '
of airborne of airborne contaminants contaminants to to other other media' media' sectorS sectorS 'with greatest pre~icted .
'the greatest
'with 'the and their and their concentration concentration in in them.
them. For' .. :. sensitivities for sensitivities for the'detection the'detection of of SSES SSES examp1e, examp1e, airborne airborne contaminants contaminants may,':,'; releases. M~nitoring must releases. must bepefforI,ned bepefforI,ned move toto the'terrestrial environment move the'terrestrial environment and,. at the at the community'in community'in the the 'vicinity
'vicinity of of the the concentrate concentrate in in milk.
milk. Concentrations Concentrations of'. .. ,
d, SSES with SSES with the the greatest greatest pre,dicted pre,dicted '
radionuclides can radionuclides can make make the the sampling, sampling, sensitivity. A sensitivity. A controllocati0!l controllocati0!l that that is is and analysis:ofmedi,a and analysis:ofmedi,a like like ~lkmore' .;;' , expected to expected to bebe umiffe~ted by by a~yroutine(
sensitive approaches sensitive approaches for for the the detection detection o~. SSES releases SSES releases must must be be mon~tored.
radionuclides, such radionuclides, such asas iodine-131:
iodine-131: in in the the pathway t<?
pathway t<? man man than than the the monitoring monitoring ~fiA', Airborne parti~uhites ~ere~~llected on Airborne on air directly.
air directly. ::(PPL (PPL also also samples samples milk; milk; ,;., . glass fiber glass fiber filters' filters' using using low low volume, volume, '
refer refer toto the Terrestrial Pathway the Terrestrial Pathway ,, (typically 2.0 (typically 2.0 to to 2.5 2.5 cfm cfm 'sampling
'sampling rates) rates)
Monitoring Monitoring section section of of this this report~) ,.,:} , air ~amplers that air that run run continuously.
continuously. Air Air Nevertheless, the Nevertheless, the sensitivity sensitivity of of air air iodine samples iodine samples were were collected collected on' on' monitoring can monitoring can bebe optimized optimized by by the the , ' charcoa1 cartridges, charcoa1 cartridges, placedplaced downstream downstream proper proper selection selection of of sampling sampling te~hnique~ ',:' of the of the particulate particulate filters:filters: . .
and the and the choice choice of of the the proper proper typestypes of,. .:, .,
analyses analyses for for the the collected collected samples.
samples. ,
" ' Particulate Particulate filters filters andand charcoal charcoal cartridges were cartridges were exchanged exchanged weekly weekly at at the, the, Scope Scope air monitoring sites.
air monitoring sites. SampHng SampHng times', '
'j were reco~ded 'o~\elapsed-tirrie meters.
were meters. '
Air samples were Air samples were col1ected col1ected on on '" , Air sample :v,?lti~es fo~ p~i~ul~te ",' "
Air sample particulate filters particulate filters and and charcoa1 charcoa1 ,, filters and filters and charcoal charcoal cartridges cartridges wer~
cartridges at cartridges at indicator indicator locations locations 3S2, 3S2, measured measured
- ~. ,
with with dry-gas dry-gas meterS. '
meterS.
12S1, 13S6 12S1, 13S6 and and 12El.
12El. and and control' control' ':,.., I locations 6Gl locations 6Gl and and 8Gl.* , .-- -," 'r: ;,' Air fillers~ere anhlyzed Air anhlyzed weekly'for weekly'for '
gross beta gross beta 'activity.,
'activity., then then composi,ted composi,ted quarter1y and quarter1y and ~mi,lyzed for the ~cti~ities for the of g'amma-einitthlg'radionuclide~. The, of The, charcoal cartridges charcoal cartridges were were analyz(!d analyz(!d weekly for weekly for iodine-131.
iodine-131. '
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report 33 33
I I Atmospheric Pathway Atmospheric Pathway Monitoring Monitoring Monitoring Results Monitoring Results on the higher on the higher mean mean activity activity reported reported for for indicator location.
indicator location.
Air Particulates Air Particulates The SSES Technical The SSES Technical Requirements Requirements Gross Gross beta beta activity activity is is always always measured measured Manual requires Manual requires radionuclide radionuclide analysis if analysis if at levels at levels in in excess excess of of the the analysis analysis MDCs MDCs any weekly any weekly gross gross beta beta result result was was greater greater on the on the fiber fiber fi)ters.
fi)ters. The The highest highest gross gross than ten than ten times times the the yearly yearly mean mean ofof beta activity beta activity levels levels that that have have been been control sample control sample results.
results. This This condition condition measured during measured during the the operational operational period period did not did not oc~ur during during 2003.
2003.
of the of the SSES SSES were were obtained obtained in' in' i986 i986 following the following the Chemobyl Chemobyl accident accident in in the the Quarterly Quarterly gamma gamma spectroscopic spectroscopic former Soviet former Soviet Union.
Union. FigureFigure 12 12 trends trends measurements of measurements of composited composited filters filters the quarterly the quarterly mean mean grossgross beta' beta' activities activities often show often show the the naturally naturally occurring occurring for the for the indicator indicator and and control control locations locations radionuclide beryHium-7.
radionuclide beryHium-7. Occasionally.
Occasionally.
separately from separately from 1~14 throutihthroutih 2003.
2003.
other naturally naturally occurring occurring radionuclides Note that Note that prior prior toto SSES SSES operation, operation, other potasstum-40 and potasstum-40
.. radionuclides and radtum-226, radtum-226, are are also also before 1982, before 1982, thethe unusually unusually high high gross gross observed. ~ery1lium-7 is observed. is cosmogenic cosmogenic in in beta activities beta activities were were generally generally origin, being origin, being produced produced by by the the attributable to attributable to faJlout faJlout fromfrom atmospheric atmospheric interaction of interaction of cosmic cosmic radiation radiation with with the the nuclear weapons nuclear weapons tests.tests. Typical Typical gross gross earth's atmosphere.
earth's atmosphere. The The other other two two beta activities beta activities measured measured on on air air gamma-emitting radionucIides gamma-emitting radionucIides originate originate particulate filters particulate filters are are the the result result ofof from soil from soil and and rock.
rock.
naturally occurring naturally occurring radionucHdes radionucHdes associated with associated with dust dust particles particles suspended suspended BeryHium-7 BeryHium-7 was was measured measured aboveabove in the in the sampled sampled air. air. They They areare thus thus analysis MDCs analysis MDCs fO,rfO,r all all quarterly quarterly terrestrial in terrestrial in origin.
origin.
composite samples composite samples in in 2003.
2003. The The 2003 2003 indicator and indicator and control control means means forfor Particulate Particulate gross gross beta beta activity activity levels levels for for beryllium-7 activity beryllium-7 activity were were each monitoring each monitoring location location and and 9.IOE-2 pCi/m 9.IOE-2 pCi/m33,, and and 8.20E-2 pCi/m33,,
8.20E-2 pCi/m monitoring period monitoring period in in 2003 2003 areare presented presented respectively. The respectively. The 2003 2003 means means areare lower lower in Table in Table 1-8 1-8 of of Appendix Appendix I. I.
than the than the corresponding corresponding 2002 2002 means.
means.
Comparisons of Comparisons of 2003 2003 grossgross beta beta The 2003 The 2003 iridicator iridicator and and control control means means analysis results analysis results with with those those of of previous previous were lower were lower thanthan the the averages averages of of the the years may years may bebe found found in in Table Table H H 1313 ofof corresponding annual corresponding annual means means forfor the the Appendix H.
Appendix H. For For 2003, 2003, the the annu'al annu'al prior operational prior operational and and preoperational preoperational means for means for the the beta beta activities activities of of the the periods. BerylJium-7 periods. BerylJium-7 activity activity levels levels for for indicator and indicator and control control locations locations are are each 2003 each 2003 calendar calendar quarter quarter at at each each 1.47E-2 pCilm 1.47E-2 pCilm33 and and 1.34E-2 pCilm33,,
1.34E-2 pCilm monitoring location monitoring location areare presented presented inin respectively. These respectively. These are are near near the the low low end end Table 1-9 Table 1-9 of of Appendix Appendix I. I. Comparisons Comparisons of the of the corresponding corresponding ranges ranges of of previous previous of 2003 of 2003 beryIlium-7 beryIlium-7 analysis analysis results results operational yearly operational yearly av~rages. They They are are with previous with previous years m'ay be years m'ay be found found inin significantly below significantly below the the corresponding corresponding Table H Table H 14 14 of of Appendix Appendix H. H. Potassium-Potassium-lower ends lower ends ofof their their preoperational preoperational yearly yearly 40 was 40 was measured measured aboveabove analysis analysis MDCs MDCs averages. A averages. A contribution contribution of of radioactivity radioactivity for one for one quarterly quarterly composite composite sample sample from the from the SSES SSES may may be be suggested suggested from from during 2003 during 2003 (control (control location location 6Gl).
6Gl).
the 2003 the 2003 airborne airborne gross gross betabeta data data based based 34 34 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
Atmospheric Pathway Atmospheric Pathway Monitoring Monitoring
'-.J No other gamma-emitting No other gamma-emitting radionucHdes radionucHdes were reported were reported for for air air in in 2003.
2003.
Beryllium-7 and Beryllium-7 and potassium-40 potassium-40 areare not not attributable to attributable to SSES SSES operation.
operation.
.1
.1 Iodine-131 Iodine-131 hashas been been detected detected infrequently from infrequently from 1976, 1976, when when itit was was first monitored, first monitored, through through 2003.
2003. Since Since operation of operation of the the SSES SSES began began inin 1982, 1982, iodine-131 has iodine-131 has only only been been positively positively detected in detected in air air samples samples in in 1986 1986 due due to to the Chemobyl the Chemobyl accident.
accident. No No iodine-131 iodine-131 was reported was reported for for the the 2003 2003 air air monitoring results.
monitoring results.
2003 RadiologicaJ 2003 RadiologicaJ Environmental Environmental Monitoring Monitoring Report Report 3S 3S
FIGURE 12 FIGURE 12 -- GROSS GROSS BETA BETA ACTIVITY ACTIVITY IN IN AIR PARTICULATES AIR PARTICULATES E-03 pCi/M3 E-03 pCi/M3 500 ,---------------------~----------------------------------------------------~
CHINESE CHINESE WEAPONS WEAPONS TEST TEST 450 450 PREOPERA TIONAL PREOPERA TIONAL OPERA TIONAL OPERA TIONAL 06/17174 A -- 06/17174 A
09/26176 B -- 09/26176 B
400 400
+
A A C-11117176 C-11117176 350 350
+ 09/17177 D -- 09/17177 D
E -- 03/14178 E 03/14178 10/15/80 F -- 10/15/80 F
300 300 250 250 200 200 D E D E 150 150
~ CHERNOBYL CHERNOBYL 4/26/86 4/26/86 II UNIT2 UNIT2 100 100 CRITICALITY CRITJCALITY F
F 50 50 00 t\~
~
-- Indicator Indicator -- Control Control
T~"e~trial P~thway Monitoring Monitoring
. ~ .' ,
.... ~
.~:TERREs~fRiAi3PAt'HWAy~'MONiT*O*RiNG;.',:F;~!;ri
.-,. ___ ....... ,.. 'I.l.. _>~ ........ >.#...-. _ ** ......... ,_ .....,,_ ............ _...."' .. ""' ... *. ...-__ ..
~
_~~ ,.;..:_._~~
"\..I>:r;~' .... _~'.'~; _ _l~** " " ' - " .~ -. -. ~ ... , . , .......
tl :-1t......... 'c;.~ :;.~.,_,~ ..
INTRODUCTION INTRODUCTION . ;.: ,
either either medium. medium. Sampling Sampling is is performed performed ,,
The following media The following media ,were ,were monit9red monit9red in, in, at different at different depths depths near near the the surface surface to to ..
the Terrestrial the Terrestrial Pathway Pathway in in 2003: 2003: soil,*' *. , help provide help provide information information on on how how milk, ~ruits and milk, and vegetables.
vegetables. '.,: ":. recently certain
, recently certain radioactiveradioactive materials materials may have may have enieredihesoiL enieredihesoiL Sampling Sampling at at Soil can Soil can aa great be be great accumulator accumulator of of man~',' more than more than one one depth depth also also may may help help made radionuclides made radionuclides that that enter enter it. it. The', The', .' ensure the ensure the detection detection of of materials materials that that extent of extent of the the accumulationaccumulation in in the the soil' soil' move relatively move relatively quickly quickly through through the the soil. soil.
depends of depends of course course on on the the amount amount of of the, the, . Such quick-moving Such quick-moving materials materials may may have have radionuclides reaching radionuclides reaching it, it, but but it it also. also. ' already passed already passed through through the the topmost topmost depends on depends on the the chemical chemical nature nature of of those' those' , layer of layer of soil soil at at the the timetime of of sampling.
sampling.
radionucJides an4 radionucJides an4 the the particular particular characteristics of characteristics of the the soil. soil. For For example,: ;', Milk Milk was was sampledsampled at at four four locations locations and and the elemerlt the elemerlt cesium, cesium, and, and, therefore, therefore, ' :', ;', fruit and fruit and vegetable vegetable samples samples ~ere cesium-137 can cesium-137 can be be bound bound very very tightJ,fto tightJ,fto obtained at obtained at 210cations 210cations in in 2003~ SSES SSES clay in clay in soils.
soils. The The amount'of amount'of clay clay i!l i!l soil soil ,,' Technical Requirements Technical Requirements requi~e th~t. the the can vary can vary greatly greatly frorilone frorilone location location to to ',' SSES REMP'sample SSES REMP'sample milk milk at at the the three three
anoth'er. In anoth'er. In clay clay soils, soils, cesium-137 may may most sensitive most sensitive monitoring monitoring locations locations move very move very slowly slowly and and also also may may be be takeri" near the near the SSES SSES :and :and 'one 'one .coritrollocation
.coritrollocation up very up very slowly slowly in in plants plants as as they they absorb absorb '! distant from distant from the the SSES. SSES. SSES SSES Technical Technical soil moisture.
soil moisture. ' Rt:quirements only Rt:quirements only require require ~hat fruit fruit and and vegetables be vegetables be sampled sampled at at locations locations Any medium, such Any medium, such as as soil, soil, th~t ten~s tQ . irrigated by irrigated by Susquehanna Susquehanna River River water water accumulate radioactiVe accumulate radioactiVe mateiials mateiials cari,: cari,:__ from points from points downstream downstream of of the the SSES SSES ""
also provide also provide more more sensitivity sensitivity for for dischargeto the dischargeto the Riv~r. There There are are only only .-.-
radionuclide detection radionuclide detection in in the the : I ' , " : ' ,; : three 10catic)Jls'withiri three 10catic)Jls'withiri 10 10 miles' miles' "
environment environment than than those those media media thai' .~ ;l:('!' downstream downstream i:>fthe i:>fthe SSES SSES that that have have been been don't. Such don't. Such aa medium medium facilitates facilitates the the ::;;;:: known to known to irrig~te: ~ith water water from from the the ' ::
early early identification identification of of radionuclides radionuclides in in J!."; Susque~anna ;River ;River during during unusually unusually ,
the environment, the environment, as as well well as as a\vareness!
a\vareness! ;-;- i dry periods.
dry periods. These These locations locations do do ~ot, ",
of changesihat of changesihat 'subsequently 'subsequently may may occur occur ,-; irrigate eve.ry irrigate eve.ry year. year. Irrigation Irrigation was. was. ,:' I in the in the environmental environmental levels levels of of the':;*': : performed at performed at the the Chapin Chapin FarmsDrake FarmsDrake identified radionuclides.
identified radionuclides. ' ',' ;' d' :
Field" (l1F2)
Field" (l1F2) and and ,the ,the Lupln'i Lupln'i Farm Farm ::
,, "Route "Route 93 93 Nescopeck Nescopeck Field" Field" (11D2), (11D2),
The The SSESSSES REMP REMP sampfes sampfes 's~iI nead'o~r'-:: during 2003 during 2003 as as identified identified by by the the '2003 '2003 of the of the six six REMPair REMPair sampling sampling stations.'" : Land Use Land Use 'Census'Census (Refe.rence (Refe.rence ii 1)., 1)., ..
The The purpose purpose for for soil soil sampling sampling near near the' the' r:~.'
rl'~ t" t" t -
- ,*,* ~
air sampling sampling sites sites is is to to makemake it it easier easier to" to" No requirement exists exists for for the the SSES SSES
'" t I , " .
air No requirement correlate. air correlate. air samplfng samplfng results results with'soil with'soil ":', : REMP'to monitor'soil.
REMP'to monitor'soil. AlJ,monitqring AlJ,monitqring sampling sampling results results if if any any SSES SSES related"' related"' ' : of the of the terrestrial terrestrial pathway pathway that that is is radioactive material radioactive material were were found found ,in ,in "' _~<.?~d~~!ed ,:>y .~he SSES SSES REMP REMP in in 2003 Radiological 2003 Radiological Em'ironmental Em'ironmental Monitoring Monitoring Report Report 37 37
II II Terrestrial Pathway Terrestrial Pathway Monitoring Monitoring addition addition to to milk milk and and certain certain fruitfruit and and Fruits and Fruits and Vegetables Vegetables veoetables veoetables cc is voluntary is voluntary
,, and reflects and reflects Potatoes were sampJed Potatoes were sampJed during during thethe .. ,, -- ""II PPL's wi1Jingness PPL's wi1Jingness to to exceed exceed regulatory regulatory harvest season harvest season at at 2 2 locations locations requirements to requirements to ensure ensure thatthat thethe public public surrounding the surrounding the SSES.
SSES. A A total total ofof 22 and the and the environment environment are are protected.
protected. samples were samples were coJ1ected coJ1ected from from locations locations I1D2, and I1D2, and I1F2.
I1F2. --
Scope Scope Both locations were Both locations were identified identified as as having having Soil " irrigated with irrigated with Susquehanna Susquehanna River River water water Soil was sampled Soil was sampled in in September September 2003 2003 inin from downstream from downstream of of the the SSES SSES during during accordance with accordance with its its scheduled scheduled annual annual 2003. There 2003. There areare often often years years with with frequency, a~ the sampling frequency, sampling the f.0l1owing f.0l1owing adequate rainfall adequate rainfall whenwhen no no irrigation irrigation is is four REMP four REMP air air sampling sampling locations, locations, 3S2, 3S2, performed.
performed.
12S1, 13S6, 12S1, 13S6, andand 801.801. Location Location 801 801 was aa control was control sampling sampling location; location; the the Sample Preservation Sample Preservation remaining sampling remaining sampling sites sites wer~ indicator indicator and Analysis and Analysis locations.
locations.
AU media AU media in in the the terrestrial terrestrial pathway pathway are are Twelve Twelve soilsoil plugs plugs were were taken taken at at selected selected analyzed analyzed forfor the the activities activities of of garnma-garnma-spots at spots at each each monitoring monitoring location.
location. The The emitting radionuclides emitting radionuclides using using gamma gamma plugs were plugs were separated separated into into "top" "top" spectroscopy. The spectroscopy. The other other analysis analysis that that is is (0-2 inches)
(0-2 inches) andand "bottorr(
"bottorr( (2-6 (2-6 inches) inches) routinely performed routinely performed is is the the segments. Each segments. Each setset ofof top top and and bottom bottom radiochemical analysis radiochemical analysis for iodine-131 in for iodine-131 in segments was segments was comp6sited comp6sited to to -yield
-yield 22 soil soil milk. The milk. The useuse of of sodium sodium bisulfite bisulfite as as aa samples from samples from each each location location for for analysis.
analysis. preservative in preservative in milk milk samples samples was was Since there Since there are are four four monitoring monitoring discontinued in discontinued in 2003 2003 (at (at the the request request of of locations, aa total locations, total of of 88 soil soil samples samples were were the vendor the vendor laboratory).
laboratory).
analyzed in analyzed in 2003.
2003.
Milk Milk Monitoring Results Monitoring Results Milk Milk waswas sampled sampled at at least least monthly monthly at at The only man-made The only man-made radionuclides radionuclides the foUowing the foUowing four four locations locations in in 2003:
2003: normally ~xpected at normally at levels levels in in excess excess of of lOD-l, IOD2, lOD-l, IOD2, 12B212B2 and 1001:
and 1001: analysis MDC~ in analysis in the the terrestrial terrestrial pathway are pathway are strontium-90 strontium-90 and and cesium-cesium-Milk Milk waswas sampled sampled semi-monthly semi-monthly from from 137. Both 137. Both of of these these radionuclides radionuclides are are
April through April through Octobe~ when when cows cows were were present in present in the the environment environment as as aa residual residual more Hkely more Hkely to to be be on on pasture.
pasture. U?cations U?cations from previous from previous atmospheric atmospheric nuclear nuclear 10DI, lOD2.
10DI, lOD2. andand 12B2 12B2 areare believed believed to to weapons testing.
weapons testing.
be the be the most most sensitive sensitive indicator indicator sites sites avaiJable for avaiJable for the the detection detection of of Strontium-90 analyses Strontium-90 analyses are are not not now now radionucHdes released radionucHdes released from from the the SSES.
SSES. routinely performed for routinely performed for any any media media Location 1001 Location 1001 is is the the control control location.
location. A A samples in samples in the the terrestrial terrestrial pathway.
pathway.
of 76 total of total 76 milk milk samples samples from from bothboth Strontium-90 activity Strontium-90 activity wouldwould be be indicator and indicator and control control locations locations were were expected to expected to bebe found found in in milk.
milk. SSES SSES analyzed in analyzed in 2003.
2003. Technical Requirements Technical Requirements do do not not require require .. ii 2003 Radiological 2003 Radiological Environmental Environmental MonitoringMonitoring Report Report 38 38
Terrestrial Pathway Terrestrial Pathway MonitoringMonitoring that miik that miik be be analyzed analyzed fo,r.strontiun:t:-,99:
fo,r.strontiun:t:-,99: . results were simi1ar results were simi1ar to to those those for for Strontiu~-90 analys~s may may be' be' "" "" ."." previous years.
previous years. No No other other gamma-gamma-performed at performed at anytime anytime if if the the results results of, of, .... ' emitting radionuclides emitting radionuclides were were reported reported at at other milk other milk analyses analyses would would show. show. ~:, :.., above analysis le~els above analysis MDCs. MDCs.
detectable levels detectable levels of of fission fission 'product,
'product, activity which activity which might might suggest suggest the the ~S;t;S : The 2003 The 2003 meansmeans for indicator and for indicator and as the as the sourc,e.
sourc,e. ,, .. control location sample control location potassium40 sample potassium40 activitywere 14.4 activitywere 14.4 p'Ci/gram p'Ci/gram and and Cesium-137 nOrinally Cesium-137 nOrinally has has beenbeen , " ": 10.6 pCilgram.
10.6 pCilgram. respectively.
respectively. The The me~sured iti iti excess excess ,of ,of analysis analysis MDCs' MDCs' in in .. indicator and indicator and control control means means are are within within most s()il most s()il samples.
samples. AlthoughAlthough game game is is , ,", the range the range of of corresponding corresponding means means for for not cu~nily'~fng' Irionitored, not Irionitored, ces~um~ , both prio~ ~perational and both and 137 has 137 has also also been'seen been'seen often often at levels' at levels' preoperational years'.:
preoperational years'.: This This is is notnot the the above the ~~s iIi above the iIi 'game
'game :in :in thethe past.:
past.: ',:; , result of result SS'ES op~ration because of SS'ES because the the potassium40 is potassium40 is naturaIly naturaIly occurring. occurring. The The Certain natuiaiIy Certain natuiaiIy Occurring Occurring 2003 indicator 2003 indicator and and control control means means for for radioriuCiides are radioriuCiides are also also 'routinely
'routinely fourid fourid potassium40 were potassium40 were greatergreater than than the the above analysis above analysis MDCs MDCs in'terrestrial' in'terrestrial' corresponding 2002 corresponding 2002 means. means.
pathway media.
pathway media. Potassium40, Potassium40, aa
primordial and primordial and very very long-lived long-lived Ra-226 analysis of Ra-226 analysis of soi1 soi1 samples samples was was radionuc1ide, which radionuc1ide, which is is terrestrial terrestrial in' in' ,.,. ";"; deleted from deleted from the the SSESSSES REMP REMP iri iri 2002.
2002.
origin, is origin, is obse'rved obse'rved in in all all terrestrial' terrestrial' ,, )) Ra-226 was Ra-226 was not not performed performed on on any any soil soil pathway media.
pathway media. Other Other naturally naturally .*.~ ::
.*. samples in samples in 2003 2003 and and has has been been occurring'radionuc1ides often occurring'radionuc1ides often observed:'
observed:' discontinued from discontinued from the the SSES SSES REMP REMP soil soil are thorium~228 and are and radium-226 radium-226 in in soil,"
soil," sample analysis sample analysis library.
library.
bery11ium-7 in and bery11ium-7 and in fruits fruits and and vegetables.
vegetables. "" ""
The 2003 means The 2003 means for indicator and for indicator and The results of The results of the the 2003 2003 terrestrial terrestrial control location control location sample sample thorium~228 pathway monitoring pathway monitoring resemble resemble those those of of // II activity were activity were both both 0.8 0.8 pCi/gram.
pCi/gram. The The the past~ Results the Results for for specific specific sample sample :., 2003 indicator 2003 indicator mean mean is e.qual to is e.qual to the the analyses of analyses of terrestrial terrestrial pathwaypathway media, media, :. ,.: corresponding 2002 corresponding 2002 mean. mean. 'The 'The 2003 2003
may be may be found found in in Tables Tables 1-10 1-10 through* ': control mean control mean for for thorium-228 thorium-228 is is greater greater 1-12 1-12 ofof Appendix Appendix 1. 1. A A summary summary ofthe ofthe :-:- .J', than the than the corresponding corresponding 2002 2002 mean. mean. The The 2003 terrestrial 2003 terrestrial monitoring monitoring data data may may be be ," indicator and indicator and 'control
'control means means are are within within located located inin Appendix'G.
Appendix'G. Comparisons Comparisons of of ", the ranges the ranges of of the the corresponding corresponding means':. means':. ~
2003 monitoring 2003 monitoring results results with with those those of.of. ~ tt'r; , for both for both thethe previous previous operation operation a) a) and.
and.
past years past years may may be be found found in in Tables Tables H H 15 15 \~; preoperational 'periods, preoperational 'periods, as as applicable applicable tt of" of" through'H 19 through'H 19 of of Appendix Appendix H. H. ",' ::.:' the SSES.
the SSES. Thorium-228 Thorium-228 in in soil soil is not ':': ::
is not the result the result ofSSES ofSSES operation operation because because it, it, Soil Soil * .. l' ~ :
is naturaIJy is naturaIJy occurring.
occurring.
The following gamma-emitting The following gamma-emitting ) ':!;, t
- r ".
radionucHdes radionucHdes are are routinely routinely measuredmeasured in' in' ,: I The The 2003 2003 means means for for indicator indicator and and soil soil at at levels levels exceeding exceeding analysiS analysiS MDCs: MDCs: control control location location sample sample cesium-137 cesium-137 ,,
naturaHy naturaHy occurring potassium40 tt occurring potassium40 activity activity were were 0.04 0.04 pCi/g pCi/g and and 0.07 0.07 pCi/g, pCi/g, radium-226, and radium-226, and thorium-228 thorium-228 and man-and man- respectively.
respectively. The The 2003 2003 indicator indicator mean mean made cesium-137.
made cesium-137. The The 2003 2003 analysis analysis is is within within the the range range of of thethe corresponding corresponding 39 39 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
II II Terrestrial Pathway Monitoring annual means for annual means for prior prior operational operational With With thethe exception exception of of the the naturally naturally years. The years. The 20032003 indicator indicator mean mean is is below below occurring potassium-40, occurring potassium-40, no gamma-no gamma-the ranges the ranges of of the the corresponding corresponding means means emitting radionuclides emitting radionuclides were were measured measured for preoperational for preoperational years~ The The 20032003 in excess in excess of of analysis analysis l\1DCs l\1DCs in in 2003.
2003.
control mean control mean is is below below the the 'ranges
'ranges of of the* The 2003:
The 2003: means means for for indicator indicator and and corresponding. annual corresponding. annual means means for for both both control location control sample potassium-40 location sample potassium-40 prior operational prior operational and and preoperational preoperational activity were activity were 13831383 pCilliter pCilliter and and years. Cesium-137 years. Cesium-137 levels levels in in soil soil 1406 pCi/Hter, 1406 pCi/Hter, respectively.
respectively. The The 2003 2003 samples typically samples typically vary vary widely widely from from indicator mean indicator mean is is less less than than the the 2002 2002 sample to sample to sample.
sample. Levels Levels of of cesium-137 cesium-137 mean. The mean. The 2003 2003 control control meanmean is is greater greater activity in activity in 2003 2003 samples samples varied varied by by aa than the than the corresponding corresponding 2002 2002 mean.
mean. The The factor of factor of four four over over thethe entire entire range.
range. 2003 indicator 2003 indicator and and control control means means for for Cesium-137 in Cesium-137 in soil, soil, althoughmim-althoughmim- potassium-40 activity potassium-40 activity areare within within thethe made, is made, is not from the not from the operation operation of of the the corresponding ranges corresponding ranges of of annual annual means means SSES. It SSES. It is is residual residual faJIout faJIout from from for previous for previous operational operational and and previous atmospheric previous atmospheric nuclear nuclear weapons weapons preoperational years.
preoperational years. TheThe potassi potassi um-40 um-40 testing.
testing. activity in activity in milk milk is not attributable is not attributable to to the the SSES operation SSES operation because because it it is is naturally naturally Milk Milk occurring.
occurring.
Iodine-131 Iodine-131 has has been been chemically chemically separated in separated in milk milk samples samples and and counted counted Fruits alld Fruits alld Vegetables Vegetables routinely since routinely since 1977. Refer to 1977. Refer to Figure Figure 13 13 Naturally occurring potassium-40 Naturally occurring potassium-40 was was which trends which trends iodine-131 iodine-131 activityactivity in in milk milk the only the only gamma-emitting gamma-emitting radionuclideradionuclide for indicator for indicator and and control control locations locations measured in measured in fruits fruits andand vegetables vegetables at at anan separately from separately from 19771977 through through 2003. 2003. activity level activity level in in excess excess of of analysis analysis l\1DC l\1DC Typically, iodine-131 Typically, iodine-131 is not reported is not reported at at during 2003.
during 2003.
levels exceeding levels exceeding the the l\1DCs l\1DCs for for the the analyses in analyses in anyany milk milk samples samples during during aa Due Due toto excessive excessive rainfall rainfall during during thethe monitored year.
monitored The 2003 year. The 2003 monitoring monitoring 2003 growing 2003 growing season, season, fruits fruits andlor andlor year was year was no no exception; exception; no no iodine-131 iodine-131 vegetables were vegetables were onlyonly sampled sampled twice,twice, above the above the analysis analysis l\1DCs l\1DCs was was observed observed both from both from indicator indicator locations.
locations. The The 2003 2003 in either in either indicator indicator or or control control samples.
samples. indicator location indicator location sample sample potassium-40 potassium-40 activity mean activity mean was was 4.64.6 pCi/gram.
pCi/gram. The The The preoperational years The preoperational years 1976, 1976, 1978,1978, 2003 indicator 2003 indicator mean mean is is higher higher thanthan its its and 1980 and 1980 were were exceptional exceptional years years in in the the corresponding 2002 corresponding 2002 mean.
mean. The The 2003 2003 sense that sense that iodine-131 iodine-131 activity activity was was indicator mean indicator mean is is above above the the range range ofof the the observed in observed in excess excess of of l\1DCs l\1DCs due due toto corresponding annual corresponding annual meansmeans for for pre-pre-fallout from fallout from atmospheric atmospheric nuclear nuclear operational and operational and prior prior operational operational years.years.
weapons testing.
weapons testing. Iodine-131-Iodine-131- activityactivity Potassium-40 in Potassium-40 in fruits fruits and and vegetables vegetables is is was also was also measured measured at at levels levels exceeding exceeding not attributable not attributable to to SSES SSES operation operation l\1DCs in l\1DCs in milk milk samples samples in in 1986 1986 in in the the because it because it is is aa naturally naturally occurring occurring vicinity of vicinity of the the SSES SSES as as aa result result of of the the radionuclide.
radionuclide.
Chemobyl incident.
Chemobyl incident.
2003 Radiological 2003 Radiological Environmentall\'onitoring Environmentall\'onitoring Report Report 40 40
c* cc FIGURE 13 FIGURE 13 -- IODINE-131 IODINE-131 ACTIVITY ACTIVITY IN IN MILK MILK pCilLiter pCilLiter 100 100 CHINESE CHINESE WEAPONS WEAPONS TEST TEST 90 --
90 A -- 09/12177 A
PRE-PRE- B- 03/14178 B- 03/14178 OPERATIONAL OPERATIONAL OPERATIONAL OPERATIONAL -10/15/80 C -10/15/80 80 --
80 C 70 70 --
60 --
60 so so 40 40 -- A A
CIIERNOBYL CIIERNOBYL 30 30 4/26/86 20 20 UNIT2 UNIT2 CRITICALIT CRITICALIT 10 10
+
B B
o o D D
C C
1M 1M II
+ :..
121 Indicator 121 Indicator Control
[J Control
[J
,*GroundWater WaterMonitoring Monitoring "
\ I
'--" ~ > J".: !', : f , . I J, ..
INTRODUCTION INTRODUCTION ~. Scope**... '
- ' . " .: '_, i, ",
Nonnal operation of Nonnal operation of the the SSES SSES does does not',
not', Ground Ground water water inin thethe SSESSSES vicinityvicinity was was involve the involve the release release of of radioactive radioactive .: ", J\: sampled'monthlY' at sampled'monthlY' at 2 2indicator indicator ,, ))
material to material to ground ground water water directly directly 'or'or ," locations (2S2 arid 4S4) and locations and one one c'ontr01 c'ontr01 .
,, in'directly in'directly through' through' the the ground.
ground. As As aa ,"": " location (12F3) location (12F3) during during 2003. 2003.
result, there result, there are are no no effluent effluent monitoring' monitoring' ,,
data to data to compare compare with with REMP REMP ground ground ,":" With With the the exception exception of of location location 4S4 4S4 *. ,
water water monitoring monitoring results. results. Ground Ground water water untreated gro'und untreated gro'und waterwater was was sampled.
sampled.
could could conceivably conceivably become become Untreated means Untreated means that that thethe waterwater has'not has'not contaminated contaminated by by leakage leakage or or spills spills from from ,", undergone. any undergone. any processing processing such such as.,
as., '
the the plant plant or or by by thethe washout washout or'* .,' :.: ;. filtration,'chlorinaiio~: or or softening.
softening. At" At" deposition of deposition of radioactive radioactive material material thatthat ;; :-: location *4S4. the location the SSES SSES Training' Training' Center, might might be be airborne.
airborne. If If deposited deposited 'on 'on the the :;:': we)) water we)) water actually.is actually.is obtainedobtained frop} frop} on~
ground, ground, precipitation/soil precipitation/soil moisture moisture '", " .';'; site and site and piped piped to to the the ,Training
,Training Genter" Genter" .
could could aidaid in'in' the the movement movement of of .:,' ~! 'JJ " ! after treatment.
after treatment. This This samplingsampling is' is' radioactive materials radioactive materials through through the:" the:" , .. ! L:., performed as performed as aa check check toensuretoensure thai thai ground to ground to water water thatthat could could conceivably conceivably ;.(; water:has not' water:has been radioactiveh< ~ ,
not' been be pumped be pumped for for drinking drinking purposes.purposes. No \~: r'; , contaminated. Sampling contaminated. Sampling is is performed performed at at ,,
use of use of ground ground water water for for irrigation irrigation near near the Training Center the Training Center to facilitate the to facilitate the '.
the SSES the SSES has has been been identified.
identified. .. sample collec.tion process..,
sample collec.tion '
Because routine SSES Because routine SSES operation operation Sample Sample Preservation Preservation & &
releases primarily releases primarily tritium tritium and, and, toto aa Jesser extent, Jesser extent, isotopes isotopes of of xenon xenon and and Analysis Analysis krypton to krypton to the the air, air, nono radionuclides radionuclides attributable to SSES operation to SSES operation are are Ground water Ground water samples samples were were analyzed analyzed attributable expected to expected to be be observed observed in in ground ground ~or the the 'activities
'activities ofof gamma-emitting gamma-emitting water. Iodine water. Iodine and and particulate particulate releases releases to to radiolniclides'an4 tritium radiolniclides'an4 tritium activity.
activity.
the air the air are are negJigible.
negJigible. Gaseous Gaseous xenon xenon Gamma spectrometric Gamma spectrometric 'analyses 'analyses of of and krypton and krypton tend tend to to remain remain airborne; airborne; ground \vater ground \vater were were begilrdn begilrdn 1979 1979 and and ' ,
analyses in tritiuin analyses in 1972, b'oth prior prior to' to'
- C 1972, b'oth C
deposition or deposition or washout washout of of these these would would be be tritiuin expected to expected to be be very very minimal.
minimal. Tritium Tritium SSES operation.
SSES operation. 'The 'The use use ofnitrlc'acid ofnitrlc'acid ' '
would be would be thethe most most likeJylikeJy radionuc1ide radionuc1ide to to as aa preservative as preservative in in ground ground water'- water'-
reach the reach the ground ground with with precipitation precipitation and, and, samples was samples was discontinued discontinued in in 2003 2003 '(at'(at if not if not lost lost toto streams streams (surface (surface water)water) by by the request the request of of the the vendor vendor laboratory).
laboratory).
runoff, move runoff, move readily readily throughthrough the the soil soil toto __ 'f': !.'
the ground the ground water.water.
2003 Radiological 2003 Radiological EnYironmental EnYironmental Monitoring Monitoring Report Report 42 42
Ground Water iWonitoring Monitoring Results Monitoring Results indicator and control indicator and control means means areare lower lower -.-.
than those than those for for 2002.
2002. Both Both the the 2003 2003 ..._-....../
._-....../II indicator and indicator and control control mean mean tritium tritium Tritium activity levels Tritium activity levels in in ground ground waterwater activity levels activity levels are are withi~:.!he range range of of have typically have been observed typically been observed to to _be
_be corresponding averages corresponding averages of of annual annual lower than lower than inin surface surface water.water. A A means for means for prior prior operational operational years.
years. The The
.. noticeable noticeable decline decline 'occurred
'occurred between between 2003 indicator 2003 indicator mean mean tritium tritium activity activity is is 1992 and 1992 and 1993.
1993. Fewer Fewer measurements measurements lower than lower than the the corresponding corresponding meansmeans for for were above were above thethe analysis analysis sensitivities sensitivities in in preoperational years.
preoperational years. The The 2003 2003 control control 1993 than 1993 than inin 1992.
1992. mean is mean is within within the the range range ofof corresponding means corresponding means forfor preoperational preoperational Gamma-emitting radionucIides Gamma-emitting radionucIides in in years.
years.
excess ofMDCs have excess ofMDCs have beenbeen found found in in few samples only aa few only samples in' in' an an the the years years that that Natural1y occurring potassium-40 Natural1y occurring potassium-40 was was these analyses these analyses havehave been been performed.
performed. measured in measured in excess excess ofof analysis analysis MDCs MDCs in in natural1y occurring The natural1y The occurring radionuclides radionuclides 2 ground 2 ground water water samples samples during during 2003.
2003.
potassium-40 and potassium-40 and thorium-228 thorium-228 have have No man-made No man-made gamma-emitting gamma-emitting been measured been measured aboveabove their their MDCs MDCs radionuclides were radionuclides were determined determined to to be at be at occasionaUy in occasionaUy in ground ground water. water. .. levels in levels in excess excess ofof analysis analysis MDCs.
MDCs. No No Potassium-40 was Potassium-40 was reported reported in in 1979, 1979, radioactivity contributions radioactivity contributions to to ground ground 1981, 1985.
1981, 1985. 1991, 1991, 1992, 1992, 199~,and water from water from thethe SSES SSES were were identifiable identifiable 1997. Thorium-228 1997. Thorium-228 was was found found in in 1985 1985 in 2003.
in 2003.
and 1986.
and 1986. TheThe man-made man-made radionuclide radionuclide cesium-137 has cesium-137 has been, been, detected detected only only occasionally since occasionally since 1979.
1979. Its Its presence presence has always has always beenbeen attributed attributed to to residual residual from previous fallout from fallout previous atmospheric atmospheric nuclear weapons nuclear weapons tests.
tests.
The results of The results of the the 2003 2003 REMP REMP groundground survei1Iance resemble water survei1Iance water resemble those those of of the the past. Res~Its for past. for specific specific ground ground waterwater sample analyses sample analyses may may be be found found in in Table 1-7 Table 1-7 ofof Appendix Appendix I.I. A A summary summary of of the 2003 the 2003 ground ground water water monitoring monitoring data data may be may be located located inin Appendix Appendix G. G.
Comparisons of Comparisons of 2003 2003 monitoring monitoring resultsresults for tritium for with those tritium with those of of past past years years maymay be found be found ,in,in Table Table H H 20 20 ofof Appendix Appendix H. H.
During 2003, tritium During 2003, tritium was was measured measured in in excess of excess of analysis analysis MDCsMDCs on on 44 occasions. The occasions. The 2003 2003 mean mean tritium tritium activity levels activity for indicator levels for indicator and and control control monitoring locations monitoring locations were were 5454 pCi/Jiter pCi/Jiter and 17 and 17 pCilliter, pCilliter, respectively.
respectively. The The 43 43 2003 Radiological 2003 Radiological Envjron~ental Monitoring Monitoring Report Report
References r7~:"~:~~';:~
- 1. Pennsylvania Power and Light Company, ffSusquehanna Steam Electric Station, Environmental Report, Operating License Stage,ff May
- 2. Pennsylvania Power and Light Company, "Susquehanna Steam Electric Station, Final Safety Analysis Report".
- 3. United States Nuclear Regulatory Commission, Office of Nuclear Reactor Regulation, "Final Environmental Statement Related to the Operation of Susquehanna Steam Electric Station, Units 1 and 2," Docket Nos. 50-387 and 50-388, June 1981.
- 4. United States Nuclear Regulatory Commission, "An Acceptable Radiological Environmental Monitoring Program," Radiological' Assessment Branch Technical Position, November 1979, Revision 1.
- 5. National Council on Radiation Protection and Measurements, ttEnvironmental Radiation Measurement:t NCRP Report No. 50, Washington, D.C.,
December 27, 1976. .
- 6. Oakley, D.C., tlNatural Radiation Exposure in the United States:' ORP/SID 72-1 Office of Radia"tion Programs, U.S. Environmental Protection Agency, Washington, D.C., June 1972.
- 7. Denham, D.H., Roberts, M.C., Novitsky, W.M., Testa, E.D., "Investigation of Elevated Cesium-137 Concentrations in Small Game in Luzerne County, PennsyJ vania." Proceedings of Papers presented at Health Physics Society Tenth Midyear Topical Symposium~ October 11-13, 1976, pgs. 271-279.
- 8. Cunie L.A., "Lower Limit of Detection: Definition and Elaboration of a Proposed Position for Radiological Effluent and Environmental Measurements,"
NUREG/CR-4007, September 1984.
- 9. PPL, "Susquehanna Steam Electric Station, 2002 Annual Radiological Environmental Operating Report." April 2003.
- 10. PPL, "Susquehanna Steam Electric Station, Radioactive Effluent Release Report,"
Data Period: January - December 2003; April 2004.
- 11. Ecology ill, "Susquehanna Steam Electric Station, 2003 Land Use Census,"
November 2003.
2003 Radiological Em'ironmental Monitoring Report 44
APPENDIX A APPENDIX A
"/ ;"
1",
r 17.'
r r:.
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report A*I
II II Appendix A Appendix A REMP Sample REMP Sample Analyses Analyses The fol1owing table The fol1owing table summarizes summarizes the the REMP REMP sample sample analyses analyses for for which which different different laboratories were laboratories were responsible responsible during during 2003.
2003. Note Note that that TBE TBE represents represents Teledyne Teledyne Brown Brown Engineering and Engineering and E-LAB E-LAB represents represents Framatome Framatome ANP.
ANP.
SOURCE OF SOURCE OF REMP REMP DADA TA TA FOR FOR MONITORING MONITORING YEAR YEAR 2003 2003 Sample Sample Analysis Analysis Sample/Analysis Sample/Analysis Medium Medium Type Type Frequency Frequency Data Period Data Period Lab Lab Air Air Gross Beta Gross Beta Weekly Weekly All Year All Year TBE TBE Air Air 1-131 1-131 Weekly Weekly All Year All Year TBE TBE Air Air Gamma Gamma Quarterly Quarterly All year All year TBE TBE Surface Surface Gross Beta Gross Beta Monthly Monthly All Year All Year TBE TBE Water Water Drinking Drinking Gross Beta &
Gross Beta & Monthly Monthly An Year An Year TBE TBE Water Water Gross Alpha Gross Alpha All Water All Water Tritium Tritium Monthly Monthly All Year All Year TBE TBE Surface Surface && Gamma Gamma Monthly Monthly All Year All Year E-LAB E-LAB Drinking Drinking Water Water Surface Surface 1-131 1-131 Monthly Monthly All Year All Year E-LAB E-LAB Water Water (LTAW)
(LTAW)
Ground Ground Gamma Gamma Monthly Monthly All Year All Year E-LAB E-LAB Water Water Surface &
Surface & 1-131 1-131 Bi/weekly Bi/weekly An Year An Year E-LAB E-LAB Drinking Drinking Water Water Milk Milk Gamma Gamma Monthly!
Monthly! All Year All Year E-LAB E-LAB Semi-Monthly Semi-Monthly Milk Milk 1-131 1-131 Monthly!
Monthly! All Year All Year E-LAB E-LAB Semi-Monthly Semi-Monthly Fish Fish Gamma Gamma Semi-Annually Semi-Annually Spring/Fall Spring/Fall TBE TBE Sediment Sediment Gamma Gamma Semi-Annually Semi-Annually Spring/Fall Spring/Fall TBE TBE 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
Appendix A Appendix A SOURCE OF SOURCE OF REMP REMP DATA DATA FOR FOR MONITORING MONITORING YEAR YEAR 20032003
.. (continued)
(continued)
Sample Sample Analysis Analysis Sample! Analysis Sample!Analysis Medium Medium Type Type Frequency Frequency Data Period Data Period Lab Lab Fruits &
Fruits & Gamma Gamma In Season In Season All Year All Year TBE TBE Vegetables Vegetables (when irritgated)
(when irritgated)
Soil Soil Gamma Gamma Annually Annually All Year All Year E-LAB E-LAB Direct Radiation Direct Radiation Monitoring Monitoring There were There were no no changes changes toto direct direct radiation radiation monitoring monitoring inin 2003.
2003.
Air Monitoring Air Monitoring There were There were no no changes changes toto the the air air monitoring monitoring program program during during 2003 2003 Milk Monitoring Milk Monitoring There were There were nono changes changes to to the the milk milk monitoring monitoring program program inin 2003.
2003.
Ground Water Ground Water Monitoring Monitoring There were There were nono changes changes to to the the ground ground water water monitoring monitoring program program during during 2003.
2003.
Fruits &
Fruits & Vegetables Vegetables Because Because of of the the milk milk monitoring monitoring that that is performed, there is performed, there is no requirement is no requirement to to sample sample from from gardens that gardens that have have aa potential potential forfor the the deposition deposition ofof activity activity by by way way of of the the airborne airborne pathway. Fruits pathway. Fruits and and vegetables vegetables areare sampled sampled from from locations locations that that irrigate irrigate with with water water taken taken from the from the Susquehanna Susquehanna River River downstream downstream from from the the SSES SSES diffuser.
diffuser. The The only only change change to to the the fruit and fruit and vegetable vegetable monitoring monitoring program program in in 2003 2003 was was the the addition addition ofof Contro]
Contro] Location Location 5S10. Location 5S10. Location 5S10 5S10 is is aa farm farm irrigated irrigated with with Susquehanna Susquehanna RiverRiver water water upstream upstream ofof the the SSES diffuser.
SSES diffuser. Due Due to to excessive excessive rainfall, rainfall, no no irrigation irrigation was was performed performed at at Location Location 5S10 5S10 during 2003.
during 2003.
A*3 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
,, "I
" I" APPENDIXB APPENDIXB
,, 1 1 ~ ,,
/",
/",
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report B*l
II AppendixB AppendixB TABLE TABLE 1 1 (Page 1 (Page 1 of2) of2)
Annual Analytical Annual Analytical Schedule Schedule for for the the PPL Susquehanna Steam PPL Susquehanna Steam Electric Electric Station Station Environmental 'Monitoring Radiological Environmental Radiological 'Monitoring Program Program -- 2003 2003 No. of No. of Sample Sample Analysis Analysis Media &
Media Code
& Code Locations Locations Freq.(a)
Freq.(a) Analyses Required Analyses Required Freq. (b)
Freq. (b)
Airborne Airborne 66 W W Gross Beta (c)
Gross Beta (c) W W
Particulates Particulates Gamma Spectrometry Gamma Spectrometry QC QC Airborne Iodine Airborne Iodine 66 W W 1-13 ))
1-13 W W
Sediment Sediment 4 4 SA SA Gamma Spectrometry Gamma Spectrometry SA SA Fish Fish 2 2 SA SA Gamma Spectrometry Gamma Spectrometry SA SA 1
1 A A (on edible portion)
(on edible portion)
Surface Water Surface Water (d)(d) 4 4 MC, M,or MC, M,or Gross Beta Gross Beta M M
BWe BWe 1-13 II 1-13 BW BW Gamma Spectroscopy Gamma Spectroscopy M M
Well (ground)
Well (ground) 33 M* Gamma Spectroscopy Gamma Spectroscopy M M
Water Water Tritium Tritium M M
Drinking Water Drinking Water (e)
(e) MC,Bwe MC,Bwe Gross Alpha Gross Alpha M M
Gross Beta Gross Beta M M
1-131 1-131 BW BW Gamma Spectrometry Gamma Spectrometry M M
Cow Milk Cow Milk 4(0 4(0 M. SM(!)
M. SM(!) 1-131 1-131 SM,M SM,M Gamma Spectrometry Gamma Spectrometry SM,M SM,M Food Products Food Products 2 2 A A Gamma Spectrometry Gamma Spectrometry A A
(Potatoes)
(Potatoes)
Soil Soil 4 4 A A Gamma Spectrometry Gamma Spectrometry A A
Direct Radiation Direct Radiation 84 84 Q Q TLD TLD Q Q
Note: See Note: See footnotes footnotes at at end end of of table.
table.
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report B-2
Appelldix B (a)
(a) W=
W weekly, BW
weekly,
=
BW biweekly, biweekly, BWC BWC = = biweekly biweekly composite, composite, M =
=
M monthly, monthly, SM SM =
=
semi-monthly, Q semi-monthly, =
=
Q quarterly, quarterly, QCQC =,quarterly
,quarterly composite, composite, SA SA == semi-annually, semi-annually, A
=
A annually, annually, MC =
=
MC monthly monthly composite.
composite.
(b)
(b) Codes are Codes are the the same same asas for for sample sample frequency.
frequency.
(c)
(c) If the gross If the gross beta beta activity activity were were greater greater than than 10 10 times times the the yearly yearly mean mean ofof the the control control sample, gamma sample, gamma analysis analysis would would bebe performed performed on on the the individual individual filter.
filter. Gross Gross beta beta analysis was analysis was performed performed 24 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br /> hours or or more more following following filter filter change change to to allow allow for for radon and radon and thoron thoron daughter daughter decay.
decay.
(d)
(d) Locations 6S6,657, and Locations 6S6,657, and 2S7 werewere checked checked at at least least weekly weekly to to ensure ensure that that the the automatic composite automatic composite samplers samplers were were operational.
operational. Time Time proportional proportional sampling sampling waswas performed at performed at locations locations 656, 656, 657 657 and and 2S7 the entire 2S7 the entire year.
year. Station Station 6S5 was grab 6S5 was grab sampled weekly.
sampled weekly. Individual Individual composites composites ofof the the weekly weekly samples samples werewere made made both both monthly (MC) monthly (MC) and and biweekly biweekly (BWC)
(BWC) for for analysis.
analysis.
(e)
(e) Water from location Water from location 12H2 12H2 waswas retrieved retrieved weekly.
weekly. Composite Composite samples samples of of the the weekly collections weekly collections at at this this location location were were made made both both monthly monthly (MC)
(MC) andand biweekly biweekly (BWC) for (BWC) for analysis.
analysis. Sampling Sampling at at 12H2 12H2 was was performed performed using using an an automatic automatic continuous sampler continuous sampler (ACS)
(ACS) that that was was operated operated inin the the time time proportional proportional mode.
mode.
(f)
(f) Locations lODI, IOD2, Locations lODI, IOD2, IOGl, IOGl, and and 12B2 12B2 were were sampled sampled semi-monthly semi-monthly from from April April through October.
through October.
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
APPENDIXC APPENDIXC
~ ..
.. r' r' .~
,1
,1
.~, .. JJ 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report C-l C-l
II II C
Appendix C Appendix TABLECI TABLECI (Page 11 of (Page of 5) 5)
TLD Locations for TLD Locations for the the SSES SSES Radiological Environmental Radiological Environmental Monitoring Monitoring Program Program -- 2003 2003 Less Than Less Than One One Mile Mile from from the SSES(a) -- See the SSES(a) See Fi2Ure Fi2Ure 2 2 Location Location Distance Distance Direction Direction Description Description Code(b}
Code(b} (miles)
(miles)
IS2 IS2 0.2 0.2 N N Perimeter Fence Perimeter Fence 2S2 2S2 0.9 0.9 NNE NNE Energy Infonnation Energy Infonnation Center Center 2S3 2S3 0.2 0.2 NNE NNE Perimeter Fence Perimeter Fence 3S2 3S2 0.5 0.5 NE NE SSES Backup SSES Backup MetMet Tower Tower 3S3 3S3 0.9 0.9 NE NE ANSP Riverlands ANSP Riverlands Garden Garden 3S4 3S4 0.3 0.3 NE NE Perimeter Fence Perimeter Fence 4S3 4S3 0.2 0.2 ENE ENE Post, West Post, West ofof SSES SSES APF APF 4S6 4S6 0.7 0.7 ENE.
ENE. Riverlands Riverlands 5S4 5S4 0.8 0.8 E E West of West of Environmental Environmental Laboratory Laboratory 5S7 5S7 0.3 0.3 E E Perimeter Fence Perimeter Fence 6S4 6S4 0.2 0.2 ESE ESE Perimeter Fence Perimeter Fence (north)
(north) 6S9 6S9 .0.2 ""
.0.2 ESE ESE Perimeter Fence (south)
Perimeter Fence (south) 7S6 7S6 0.2 0.2 SE SE Perimeter Fence Perimeter Fence 7S7 7S7 0.4 0.4 SE SE End ofK1ine's End ofK1ine's Road Road 8S2 8S2 0.2 0.2 SSE SSE Perimeter Fence Perimeter Fence 9S2 9S2 0.2 0.2 S S Security Fence Security Fence 10S1 10S1 0.4 0.4 SSW SSW Post -- south Post south of of switching switching station station 10S2 10S2 0.2 0.2 SSW SSW Security Fence Security Fence 10S3 10S3 0.6 0.6 SSW SSW Confer's Lane Confer's Lane -- east east of of Confer's Confer's Lane.
Lane.
south of south Towers Club of Towers Club l1S3 l1S3 0.3 0.3 SW SW Security Fence Security Fence l1S7 l1S7 0.4 0.4 SW SW SSES Access SSES Access Road Road Gate Gate #50
- 50 12S1 12S1 0.4 0.4 WSW WSW SSES West SSES West Building Building 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
Appendix C Appendix C TABLECI TABLECI (page'2 of (page'2 of sj sj
'Lo'catioris' for TLD 'Lo'catioris' TLD for 'the S'SES'
'the S'SES' Radio)o~dca) Enviromliental Enviromliental Monitoring Monitoring p~ogninf':"io03. ., ..
Less Than Less Than One One l\1i1e l\1i1e from from the SSES(a) -:
the SSES(a) -: See Fieure 22 See Fieure .
-'" . , ... ~
Location Location Distance'"
Distance'" Direction Direction .. 'Description
'Description
.Code (b)
.Code (b) ..(miles)
(miles) ,- . ,', '" ........ " .. ,,,.
.to ** '
' ., ....:...... '. ~"" .- .
....J2S3 J2S3 .. , ;; WSW.
WSW. : ... :Penmeter.Fence
- Penmeter.Fence ....... L...... .., ~., ** '
if
.... 1'-<< , . , - _.
.... 12S4 12S4 .0.4
.0.4 WSW '~ :Perimeter
.... WSW :Perimeter Fence' Fence' . : '
,12S5
,12S5 0.4 0.4 wsw ... ~Perimetei Fence.
wsw Fence. . .,. --
12S6 .
12S6 ,; 0.4* .': ..WSW WSW 'Perimeter Fence
'Perimeter Fence 'I J
.13S2
.13S2 0.4 0.4 '.' W W !IPerinieter.Fence*, _ .... .. ........ ' .. .., ::.:'"
13S4 13S4 '0.4
'0.4 :PerimeteiFence
" . , W*** : :PerimeteiFence " i "
13S5 13S5 0.4 0.4 ,, W W .'.' Perimeter Perimeter Fence'* ' , I < I
- 13S6 13S6 0.4 .:),.J :.:iW ,':" ..Former 0.4 Former Laydown Laydown Area-west Area-west of of Confer's Confer's Lane Lane .': r 14S5 14S5 0.5 0.5 Beach'Grove RoadlConfer's WNW .' Beach'Grove WNW RoadlConfer's Larie: Larie: : ~~ .
14S6 14S6 0.7 0.7 :WNW .ll ;Beach
- WNW ;Beach Grove Grove Road Road (pole)
(pole) ',! '
..* i
\J 15S5'. :,; ',;.:;,.0.4 "
15S5'.
16S1 16S1 0.3 0.3 NNW,;' ,,' PerimeteiFence NNW,;' PerimeteiFence (east), (east), r...
I6S2 I6S2 0.3 0.3 NNW NNW Perimeter Fence Perimeter Fence (west)
(west) ::.'
6A4 6A4 0.6 0.6 ESE. ;; ,Restaurant ESE. ,Restaurant (U.S. (U.S. Route Route 11) 11) ,
SA3 SA3 0.9 0.9 SSE.PPLWetlarids Sign SSE.PPLWetlarids Sign (U. (U. S. S. Route Route 11) 11) 15A3 15A3 0.9 0.9 NW "" Hosler NW Hosler Residence Residence .,.,
16A2 16A2 O.S O.S ... NNW
... ,,"BenldnneyResidence' :
NNW ,,"BenldnneyResidence' 11 ~ ':
': __ '~'!: >~L. :)L~~<.~ (i".. =c '// .
From One From to Five One to Five Miles Miles fromfrom theSSES(~):::Soo-Fi2Ure"3 -... :';
I2S7 I2S7 ... 1.1 1.1 -
- .. WSW 'Kisner Residence WSW 'Kisner Residence IBI IBI 1.4' 1.4' -.
-. I ,'** o*
2B3 1.3 NNE ........ Leggeff&'Platt Leggeff&'Platt 2B3 1.3 NNE 2B4 2B4 1.4 1.4 NNE NNE U.S. Route U.S. Route lllMingle lllMingle Inn Inn Road Road Intersection Intersection 5B3 5B3 1.6 1.6 E E PPL Switchyard PPL Switchyard 7B2 7B2 1.5 1.5 SE SE HeUer's Orchard HeUer's Orchard Store Store SB2 SB2 1.4 1.4 SSE SSE Lawall Residence Lawall Residence C-3 C-3 2003 Radiological 2003 Radiological Environmental Environmental Monitoring'Report Monitoring'Report
II ,,
Appendix C Appendix C
, .- .. ~ .. ' '.' .. , . . , ' . --
TABLE'CI (page ,3 (page ,3 of of 5) 5)
TLD TLD Locations Locations for for.. the the SSES SSES
Radiological Environmental Radiological Environmental Monitoring Monitoring Program Program -- 2003 2003
\~ ' , .
From One From One to to Five Five Miles Miles from from the the SSES(a) SSES(a) -- See See Fi~re 3 3 : ,
,, ,~,'- ,, " ,
Location Location Distance. ;;
Distance. Direction Direction \
~escription Code (b)
Code (b) (miles)'"
(miles)'"
'-'9Br i '-'9Br 1.3' .. ,.,.
1.3' .. ...... S S Transmission Line Transmission Line -'east -'east of of Route Route 11 11
.... 2.0 -- ---- .. ......
2.0 ...... SSW.~-,.* AIgatt
- lOB2 lOB2 AIgatt Re'siderice Re'siderice ..
1.7 ..
1.7 . Castek Inc; .. -- --
IOB3 IOB3 SSW SSW ..
.. . Castek Inc; :):) .... //
IOB4 IOB4 1.4 1.4
,-- .~
.---- SSW'
.---- SSW' "" "" u. u. S; S; Route Route lllRiver lllRiver Road Road Intersection Intersection 12B4 12B4 1.7 1.7
~
'*WSW'*,. ;; Berger. Berger. FannFann ...
13Bl 13Bl 1.3 1.3 W* .... ::Walker Walker Run Run Creek Creek (fele.PoIe(fele.PoIe #36) #36) 14B3 14B3 1.3 1.3 WNW*;' ,,Moskaluk Moskaluk Residence Residence ISBl:
ISBl: ,, ~'1.7;*. :.,. .NW .. ..Country Country Estates Estates Trailer Trailer Park Park I6B2 I6B2 h71'!' , \'.NNW*.'* Walton Walton Power Power Line"Line" .. '.
IDS IDS 4.0 4.0 N .
.ShickshinnylMoeanaqua ShickshinnylMoeanaqua Sewage Treatment Sewage Treatment PIt.
PIt.
6DI 6DI 3.S 3.S ESE.:
ESE.: St. Peters St. Church:: Hobbie Peters Church:: Hobbie 8D3 8D3 4.0 4.0 '.SSE "" Mowry
'.SSE Mowry Residence*'
'j 904 904 3.6 3.6 : '
' S',
S', J J '.'
'.' Country Folk Country Folk Store"':
Store"':
1001 1001 3.0:".:'*., .. SSW,:,:' SSW,:,:' :R~ & C. Ryman
& C. Ryman Farm Farm 12D2 12D2 3.7 3.7 WSW, WSW, Dagostin Residence Dagostin Residence ",",
1401 1401 3.6 3.6 WNW:, Moore's WNW:, Moore's HilllMingleInn HilllMingleInn Roads Roads Intersection Intersection 3EI 3EI 4.7 4.7 NE NE Webb Residence Webb Residence -- Lilly Lilly Lake Lake
' ___ 4E2 4E2 4.7 4.7 ENE ENE Ruckles HiIVPond Ruckles HiIVPond Hin Hin Roads Roads Intersection Intersection '.'.
.SE2 4.S E E "
" BlossFann
.SE2 4.S BlossFann .... .. ....
6EI 6EI 4.7 4.7 ESE; ESE; St.;Jarries Church St.;Jarries Church -- ..
Radiological Environmental 2093 Radiological 2093 Environmental Monitoring Monitoring Report Report C-4 C-4
APPelldix C C TABLECI TABLECI (page 44 of (page of 5) 5)
TLD TLD *LoCationS for for the SSEs the SSEs Radiological Environmentai Radiological Environmentai Monitoring Monitoring Program Program -2003 -2003 From One From One to to Five Five Miles Miles from from the SSEs(a) .:.: See the SSEs(a) See Figure Figure 3 3 ""
~ : ~.
Location Location Distance Distance DireCtion'-' ,
DireCtion'-' , ..;;
Descript~on Code(b) ,. , . '(miles)
Code(b) '(miles) ,, :
. ,'_I. , , ** JJ **
7EI 7EI 4.2 4.2 ""
SEt" SEt" "" Harwood Harwood Transmission Transmission Line Line PolePole #2 #2 4.7 llE1 llE1 4.7 SW SW Thomas Residence Thomas Residence 12EI 12EI 4.7 4.7 WSW" WSW" Berwick Hospital Berwick Hospital 13E4 13E4 4.1 4.1 W W Kessler Fann Kessler Fann Greater than Greater than Five Five Miles Miles from from the SSES(a) -- See the SSES(a) See Figure Figure 4. 4. ""
2Fl 2Fl 5.9 5.9 NNE NNE St. Adalberts St. Adalberts Cemetery.
Cemetery.
SF2 SF2 8.5 8.5 SSE SSE Huff Residence Huff Residence 12F2 12F2 5.2 5.2 WSW' WSW' II
'Beiwick Substation
'Beiwick Substation ,.1 '
'5.4 NW Z8watSki Fann Fann 15Fl ' '5.4 '
15Fl NW Z8watSki 16Fl 16Fl '7.S'
'7.S' 'NNW,
'NNW, Hidlay Residence Hidlay Residence 3G4 3G4 ,, 17 17 .. NE NE ,
, Wilkes Barre Wilkes Barre Service Service CenterCenter r ** ;
4GI,* .' 14 14 .ENE"
.: .ENE" ,Mountaintop -- Crestwood
,Mountaintop Crestwood Industrial Industrial Park Park 6G1.
6G1. ., .:13.5
.:13.5 ESE' ESE' Freeland Substation Freeland Substation ' , : .. ,, ,,
7Gl 7Gl 14 14 ,"SE
,"SE ","
"," HazletonPP&L HazletonPP&L Complex: ,.,.
Complex: . '-
7G2 7G2 12 12 SE SE Hazleton Cemetery Hazleton Cemetery -- 14th14th Street Street SG1 SG1 '12
'12 SSE' SSE' PPL'SFC ;;"HumboltIndustriaI PPL'SFC ;;"HumboltIndustriaI Park' Park'
12G1' 12G1' 15 15 '
.. 'WSW'
'WSW' ,,
PPL Service PPL Service Center.
Center. Bloomsburg Bloomsburg .. '. ' ~ .. '
12G4 10 WSW Naus ResidenceResidence 12G4 10 WSW Naus c-s c-s 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
II II Appendix C Appendix C TABLECI TABLECI (Page 55 of (Page of 5) 5)
TLD Locations for TLD Locations for the the SSES SSES Radiological Environmental Radiological Environmental Monitoring Monitoring Program Program -- 2003 2003 a) a) All distances from All distances from thethe SSES SSES ~o monitoring monitoring locations locations areare measured measured from from the the standby gas standby gas treatment treatment ventvent at at 442001N34117 442001N34117 (pa. (pa. Grid Grid System).
System). TheThe location location codes are codes are based based on on both both distance distance and and direction direction from from thethe SSES.
SSES. TheThe letters letters in in the the location codes location codes indicate indicate if if the the monitoring locations aare monitoring locations re on on site site (wfthin (wfthin the the site site boundary) or, boundary) if they or, if they are are notnot onon site, site, the the approximate approximate distances distances ofof the the locations locations from the from the SSES SSES as as described described below: below:
S -on S -on site site E-E- 4-5 miles 4-5 miles A-A- <1 <1 mile mile F --
F 5-10 miles 5-10 miles B -- 1-2 B 1-2 miles miles G --
G 10-20 miles 10-20 miles C -- 2-3 C 2-3 miles miles H-H- >20miles
>20miles 4 miles D 4 D miles The numbers preceding'the The numbers preceding'the letters'in letters'in rherhe location location codes codes provide provide the the directions directions of of the monitoring the monitoring locations locations from from the the SSES SSES by by indicating indicating thethe sectors sectors inin which which they they are are located. A located. A total total ofof 16 16 sectors sectors (numbered (numbered 1 1 through through 16) 16) equally equally divide divide an an imaginary circle imaginary circle onon aa map map of of the the SSES SSES and and its its vicinity.
vicinity. with with the the SSES SSES at at the the center center of the of the circle.
circle. The The middle middle of sector ii is of sector is directed directed due due north north (N).
(N). Moving Moving clockwise clockwise from sector from sector 1,1, the the sector sector immediately immediately adjacent adjacent toto sector sector 11 is is sector sector 2,2, the the middle middle of of which is which is directed directed duedue ~orth, northeast (NNE). Continuing northeast (NNE). Continuing to to move move clockwise, clockwise, the the sector numbers sector numbers increase increase to which is to I~, which is the the north, north, northwest northwest sector.
sector.
The numbers following The numbers following the the letters letters in the in the location location codes codes are are used used to to differentiate differentiate sampling locations sampling locations found found in in the the same same sectors sectors atat approximately approximately the the same same distances distances from the from the SSES.
SSES. ..
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report C-6 C-6
Atmendix C TABLEC2 (pagelof4)
Sampling LOCations for the SSES Radiological Environmentill Monitoring Program ~ 2003 Less Than One Mile from the SSES(a) See Figure 5 Location Code Distance Direction Description (miles)
- ,<~~;~*t~.-',:;*c* It;*.~,.:~.':;:., :~ ~':'>,:'i"'SURFACE:WATER'" :;.'B~:,.~:~~(~;: J(:~ ,~:{:'~~:
2S7 OJ NNE; Cooling Tower BIowdown Line' 6S5 0.9 .ESE Outfall Area 6S6 0.8 ESE Water Intake Line 6S7 0.4 ESE Cooling Tower Blowdown Line (alternate for 2S7)
LTAW NE;.ESE Lake Took.:A-While (on site)
'~::*:.:~*::~~t~:~>":~*:~*:~~~:~;~'~~~j:*~:' ;¢~;'~ ~~~<:;'.~::~~~ ~:~ ~;:-~,~~.~~ ~:~~.r~:~:\:~,;~::t~1~*~~*;~;)FISH ,;t:!:~*~':~f*~*~).~*;~.~'~~::~ .~. ~:; :.:~: ~"'-,"',.
LTAW NE-ESE,. Lake Took.!A-While (on site)
~~**>'~?>2:*::L~: ':'~~
'2.'*:"f~,,;:-:;,.r;*;'>';;SEDIMENT(c)':";* :.~[;.("
.~"~~ ,."(~:-:>;)i.r!~~'i ",~" ,:'.~~~ ,,:.;.:~.
'~l'
~
' ::',~Jry.:*t:H~:::
LTAW NE-ESE Lake Took-A-While (on site)
- ~""~,
- <:,::( ~:(:.4~::;:~:::*~/:(\:}c.t;;~*\'.2 ":'~:~".!';',
i.'~'.::' ~~ ':q.~: F~
~'
t~!' ",;:-;~:;:~,: ::~i:" ::~*ot)/*)~.;;:<~.,
"3S2 0.5 NE SSES Backup Meteorological Tower 12S1 0.4 SSES WesfBiIilding 13S6" '0.4' 'PormerLaydown Area, WesfofConfers Lane' f:*~~'?~~~?i.:.~:'(!7*_t*7'.*~:~ ;;~~ :.~.:~ !::".~:::=#t=I~~*~.'~~ ;i.:,:*;:~~~~( y~t:~?7~~t!t~SOIU;}~: {;::~~. ::':~~.:~;~T ;~f~~1~i:~ T1~~Y:\~;',~~j-:~t?;~:~
3S2 '0.5 NE 'SSES Backup Meteorological Tower 12S1 0.4' SSES West Building' 13S6 0.4'" 'W F01Tl1er Layd6wn'Area, West of Confers Lane 2003 Radiological Em'ironmental Monitoring Report
II II Appendix C Appendix C TABLEC2 TABLEC2 (Page 22 of (Page of 4) 4)
Sampling Sampling Locations Locations for for the the SSESSSES Radiological Environmental Radiological Environmental Monitoring Monitoring Program Program -- 2003 2003 Less Than Less Than One One l\'liIe l\'liIe from from the the SSES(&)
SSES(&) ** See See Figure Figure 55 Location Location Distance Distance Direction Direction Description Description Code Code (miles)
(miles)
- ~\:.~;~', :_~:*,;.~~i;:*(',s*.;:Y~f :~:,:;;':'::; ~£~~-lt; .: GROUND,WATER;~;;;::!I~{:.~f\~",~::~::,':~::-:-,:t:, -, ", :.'.:" ; ~.
2S2 2S2 0.9 0.9 '.'. '.'. NNE NNE -,-, SSES Energy SSES Energy Infonnation Infonnation Center Center 4S4 4S4 0.5 0.5 ENE, SSES ENE, SSES Learning Learning Center Center From One From One to to Five Five Miles Miles From From the the SSES SSES ** See See Figure Figure 6 6
~ "~i~ .<:,;;.:::*:t:i:.'\~~"" '~:'!t~/;:i:\.rj:-:)i ,'In?f~';:;:~';::f;)>;'; FISW~!;':A:;;-"~;: ::~'~~S:'j,:',~:;:,!;;,:~;n;; 't~,',ll~ ,~.<~ . >"' ~ " :-:~ _.'::"~~~ ,
IND IND 0.9 -- 1.4 0.9 1.4 .. - ',.' ESE ESE ':' At or Below At or Below thethe SSES SSES Discharge Discharge Diffuser Diffuser 2B 2B 1.6 1.6 -NNE
-NNE Gould Island Gould Island 7B 7B 1.2 1.2 SE SE Bell Bend' Bell Bend' lOD1 lOD1 3.0, 3.0, _SSW ,_.
_SSW ,_. R. R. & & C:
C: Ryman Farm Ryman Farm
_,_10D2 '3.1
. '3.1 SSW SSW Raymond Ryman Raymond Ryman Fann Fann 12B2 12B2 1.7 1.7 WSW _,
WSW _, Berger Berger Fann Fann .. "
I1D2 I1D2 3.5 3.5 Lupini Field-Lupini Field- U.S.
U.S. Route Route 93. 93.
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring ReportReport e-g e-g
AppendixC TABLEC2 TABLEC2 (page 33 of (page of 4) 4)
LOcations fo'r Samplhig LOcations Samplhig the SSES fo'r the SSES
.,., Radiological Radiological Environmental Environmental Mo'nitoring Mo'nitoring Program Program ~ 2003 2003 Greater than Greater than Five Five Miles Miles from from the SSES(a) -- See the SSES(a) See Figure Figure 7 7
- , ."\ ~ i ~
Location' Location' Distance Distance Direction Direction . . Description Description Code Code (miles)
(miles) 12H2 12H2 26 26 wsw wsw Danville .Water Danville .Water Co.
Co. (treated)
(treated) 2H 2H 30 30 NNE' NNE' Near Falls.
Near Falls. Pa.
Pa.
12F 12F 6.9 ;. - .- 'WSW.'
6.9 'WSW.' Old Berwick Old Berwick TestTest Track Track 6G1 6G1 13.5 13.5 ESE ESE Freeland Substation Freeland Substation 8G1 8G1 12 12 SSE SSE PPL SFC PPL SFC -- Humbo1t Humbo1t Industrial Industrial Park Park 8G1 8G1 ,12
,12 SSE .'
SSE PPL SFC PPL SFC -- Humbolt Humbolt Industrial Industrial Park*
lOG1 lOG1 *14 ,SSW, .. *Davis Farm
,SSW, Farm 12F3 12F3 5.2 5.2 WSW WSW Berwick Water Berwick Water Company Company
) .
C-9 C-9 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
II II AppendixC TABLEC2 TABLEC2 (Page 4 (Page 4 of of 4)4)
Sat:npling Locations for Sat:npling Locations for th~ SSESSSES Radiological Environmental Radiological Environmental Monitoring Monitoring Program Program -- 2003 2003 a) a) AU distances from AU distances from the the SSES SSES to to monitoring monitoring locations locations are measured from are measured from thethe standby gas standby gas treatment treatment vent vent at at 442001N341 442001N341 17 17 (Pa.
(Pa. Grid Grid System.
System. The The location location are based codes are codes based on on both both distance distance andand direction direction from from the the SSES.
SSES. The The letters letters inin the the location codes location codes indicate indicate if if the the monitoring monitoring locations locations are are on on site site (within (within the the site site boundary) or, boundary) jf they or, jf they areare not not on on site, site, the the approximate approximate distances distances of of the the locations locations from the from the SSES SSES as as described described below:
below:
S -on site S -on site E-E- 4-5 miles 4-5 miles A -- <1 A <1 mile mile F -- 5-10 F miles 5-10 miles B 2 B miles 2 miles G -- 10-20 G miles 10-20 miles C 3 C 3 miles miles H- >20 H- miles
>20 miles D -- 3-4 D 3-4 miles miles The numbers preceding The numbers preceding the the letters letters inin the the location codes provide location codes provide the the directions directions of of the monitoring the monitoring locations locations from from thethe SSES SSES by by indicating indicating thethe sectors sectors in in which which theythey are are located. A located. A total total 'of
'of 1616 sectors sectors (numbered (numbered 1 1 through through 16) 16) equally equally divide divide an an imaginary circle imaginary circle on on aa map map of of the the SSES SSES and and its vicinity, with its vicinity, with thethe SSES SSES at at the the center center of the of the circle.
circle. The The middle middle of of sector sector 1 1 is is directed directed duedue north north (N). Moving clockwise (N). Moving clockwise from secto~ 1, from 1, the the s.ectorimmediately s.ectorimmediately adjacent adjacent to to sector sector 11 is is sector sector 2, 2, the the middle,of middle,of which is which is directed directed due due north, north, northeast northeast (NNE). Continuing to (NNE). Continuing to move move clockwise, clockwise, the the numbers increase sector numbers sector increase to to 16, 16, which which is is the the north, north, northwest northwest sector.
sector.
The numberS The numberS folJowing folJowing the the letters letters inin the the location are used codes are location codes used to to differentiate differentiate sampling locations found sampling locations found in in the the same same sectors sectors atat approximately approximately the the same same distances distances from the from the SSES.
SSES.
b) b) No actual location No actual location is is indicated indicated since since fish fish are are sampled sampled overover anan area area which which extends extends through 3 through 3 sectors sectors (5, (5, 6, 6, 7)
- 7) near near the the outfall outfall area.
area.
c) c) No pennanent locations No pennanent locations exist; exist; samples samples are taken based are taken based onon availability.
availability.
Consequently, it Consequently, it is is not not necessary necessary to to assign assign aa number number fonowing fonowing the the letter letter in in the the location code.
location code.
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report C*lO
,r f;. "
r, APPENDIXD APPENDIXD
.;i t 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report D*l
I I Appendix D Appendix D 2003 LAND 2003 LAND USE USE CENSUSCENSUS RESULTS RESULTS The SSES Technical The SSES Technical Requirements Requirements require require thatthat aa census census be be conducted conducted annually annually during during the growing the growing season season to to detennine detennine the the location location of of the the nearest nearest milk milk animal, animal, residence residence and and 22 22 garden greater garden greater than than 5050 m m (approx.
(approx. 500 500 ftft )) producing producing broadbroad leaf leaf vegetation vegetation within within aa distance of distance of 8 km (approx.
8 km (approx. 5 5 miles) miles) in in each each ofof the the 1616 meteorological meteorological sectors sectors surrounding surrounding the SSES.
the SSES. To To comply comply withwith this this requirement, requirement, aa land-use land-use census census waswas conducted conducted for for the the SSES during SSES during 2003.
2003.
A comparison A comparison of of the the 2002 2002 andand 2003 2003 LandLand UseUse Census Census results results for for the the SSES SSES indicates indicates the the changes listed in changes listed in the the tables tables below.
below. TabJes TabJes 1 1 display display thethe changes changes in in the the nearest nearest gardens gardens and Table and Table 2 2 displays displays thethe changes changes in in sampling sampling of of irrigated irrigated foods foods from from 2002 2002 toto 2003.
2003.
Overall, the changes Overall, the changes since since thethe 2002 2002 Land Land Use Use Census Census werewere minimal.
minimal. In In 2003, 2003, the the nearest garden nearest garden in in sector sector 55 waswas revised revised from from 1.4 1.4 miles miles to 1.8 miles to 1.8 miles from from the the SSES.
There was There was no no garden garden identified identified in in sector sector 14 14 which which met met the the requirements requirements forfor sampling sampling in in 2003. The 2003. farm identified The farm identified in in 2002 2002 (P.(P. Moskaluk, Moskaluk, Jr.) Jr.) in in sector sector 14. did not
- 14. did not plant garden plant aa garden in 2003.
in 2003.
TABLEt TABLEt CHANGE FROM CHANGE FROM 2002 2002 TO' TO' 2003'IN 2003'IN NEAREST NEAREST GARDENS GARDENS AS DETERMINED AS DETERMINED BY BY THE THE 20032003 LAND LAND USE USE CENSUS CENSUS 2002 2002 2003 2003 Distance Distance Distance Distance Sectorl Sectorl Owner's Owner's fromSSES fromSSES Owner's Owner's fromSSES fromSSES Direction Direction Name Name (mi.)
(mi.) Name Name (mi.)
(mi.)
51E 51E KozlowskilWitts KozlowskilWitts 1.4 1.4 W. Daily W. Daily 1.8 1.8 14IWNW 14IWNW P. Moskaluk.
P. Moskaluk. Jr. Jr. 1.3 1.3 N/A N/A N/A N/A These changes in These changes in gardens gardens had had nono impact impact on on the the intended intended sampling sampling of of fruits fruits and and vegetables during vegetables during 2003.
2003. Because Because of of the the milk milk monitoring monitoring that that is is performed, performed, therethere is is no no requirement to requirement to sample sample fromfrom gardens gardens thatthat have have aa potential potential forfor the the deposition deposition of of activity activity by way by way of of the the airborne airborne pathway.
pathway.
Radiological Environmental
- 2003 Radiological Monitoring Report Environmental Monitoring Report D*2
Irrigated fruits and Irrigated fruits and vegetables vegetables were monitored at were monitored at 22 indiCator indiCator locations locations during during 2003.
2003. The The only crop only crop irrigated irrigated in in 2003 2003 was was potatOes; potatOes; :: No No other' fields other' fields within within 10 10 miles miles downriver downriver of of the SSES the SSES were were irrigated irrigated in in 2003, 2003, because because wet wet weather weather prevailed prevailed much much ofof the the spring spring and and summer."
summer." , , ;, ' ,'
TABLE TABLE 2 2 CHANGE FROM CHANGE FROM 20022002 TO '2003 IN TO '2003 IN VEGETABLES VEGETABLES IRRIGATED IRRIGATED WITH WITH SUSQUEHANNA RIVER SUSQUEHANNA RIVER WATERWATER FROM FROM DO\VNSTREAM DO\VNSTREAM OF OF THE THE SSES SSES DISCHARGE DURING DISCHARGE DURING 2003 2003 Distance Distance fromSSES fromSSES SectorlDirection SectorlDirection Owner.
Owner. (mi.)
(mi.) 2002, 2002, 2003 2003 I1F21SW I1F21SW Chapin (Drake)
Chapin (Drake) FarmFarm 5.5 5.5 N/A' N/A' Potatoes Potatoes I1D2ISW I1D2ISW Lupini Farm Lupini Farm (Rt.
(Rt. 93)93) 3.5 3.5 N/A' N/A' Potatoes Potatoes "I' '
~ . .!.'"
.'. '. "f ~ ,
,I f
.. ,: ~ f ** , f"'; : i .': ~ .,
D-3 D-3 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
I I AppendixD AppendixD TABLE 33 TABLE U!
Nearest residence, garden, Nearest residence, garden, and and dairy dairy anima]
anima] in in each each ofof the the 16 16 meteorological meteorological sectors sectors within aa 5-miIe within 5-miIe radius of the radius of the Susquehanna Susquehanna Steam Steam Electric Electric Station, Station, 2003.
2003.
NEAREST NEAREST NEAREST NEAREST NEAREST.
NEAREST.
SECTOR SECTOR DIRECTION DIRECTION RESIDENCE RESIDENCE GARDEN GARDEN DAIRY ANIMAL DAIRY ANIMAL 1
1 N N 1.3 1.3 mimi 3.2mi 3.2mi >5.0 mi
>5.0 mi 2
2 NNE NNE 1.0mi 1.0mi 2.3 mi 2.3 mi ii >5.0 mi
>5.0 mi 3
3 NE NE O.9mi O.9mi 2.7mi 2.7mi >5.0 mi
>5.0 mi 4
4 ENE ENE 2.1 mi 2.1 mi 2.4 mi 2.4 mi a,c,d,f,1 a,c,d,f,1
>5.0 mi
>5.0 mi 5
5 E E 1.4 mi 1.4 mi ll,C ll,C 1.8 mi 1.8 mi 4.5 mi 4.5 mi gg 6
6 ESE ESE O.5mi O.5mi 2.5 mi 2.5 mi 2.7 mi 2.7 mi 7
7 SE SE 0.5 mi 0.5 mi 0.6 mi 0.6 mi >5.0' mi
>5.0' mi 8
8 SSE SSE 0.6 mi 0.6 mi 1.5 mi 1.5 mi >5.0 mi
>5.0 mi 9
9 S S 1.0mi 1.0mi 1.1 mi 1.1 mi >5.0 mi
>5.0 mi 10 10 SSW SSW 0.9mi 0.9mi 1.2mi 1.2mi 3.0 mi 3.0 mi ll,b,c.d,e,g ll,b,c.d,e,g 11 11 SW SW 1.5 mi 1.5 mi 1.9mi 1.9mi >5.0 mi
>5.0 mi 12 12 WSW WSW 1.1 mi 1.1 mi 1.1 mi 1.1 mi 1.7 mi 1.7 mi g.i g.i 13 13 W W 1.2 mi 1.2 mi 1.2 mi 1.2 mi 5.0 mi 5.0 mi gg 14 14 WNW WNW 0.8mi 0.8mi >5.0mi
>5.0mi >5.0 mi
>5.0 mi V
15 15 NW NW 0.8mi 0.8mi 1.8 mi 1.8 mi 11 >5.0mi
>5.0mi 16 16 NNW NNW 0.6mi 0.6mi 4.0mi 4.0mi 4.2mi 4.2mi Chickens raised aa Chickens raised for for consumption consumption at at this this location.
location.
b b Ducks raised for Ducks raised for consumption consumption at at this this location.
location.
C C Eggs consumed Eggs consumed from from chickens chickens at at this this location.
location.
d d Geese raised Geese raised for for consumption consumption at at this this location.
location.
ee Pigs raised Pigs raised for for consumption consumption at at this this location.
location.
ff Turkeys raised Turkeys raised for for consumption consumption at at this this location.
location.
S S Fruits/vegetables raised Fruits/vegetables raised for for consumption consumption at at this this location.
location.
bb Rabbits raised Rabbits raised for for consumption consumption at at this location.
- this location.
- ii Beef cattle Beef cattle raised raised for for consumption consumption at at this this location.
location.
jj Goats raised Goats raised for for consumption consumption at at this this location.
location. **
Ie Ie Pheasants raised Pheasants raised for for consumption consumption at at this location.
- this location.
- II Sheep raised Sheep raised for for consumption consumption at this location.
at this location.
- No locations
- No locations were were identified identified as as raising raising rabbits, rabbits, goats, goats, and and pheasants pheasants during during 2003.
2003.
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report D4 D4
APPENDIXE APPENDIXE
- r
.j,
- ' ; ':i i'
- ," , * ~' t " I; I" .,;1 i'.'
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report - E-1 E-1
II II AppendixE AppendixE TLD MEASUREMENTS TLD MEASUREMENTS The The PPLPPL dosimetry dosimetry system system used used for for monitoring monitoring ambient ambient radiation radiation levelslevels in in the the environment consists environment consists of of Panasonic Panasonic 710A 710A readers readers and and Panasonic Panasonic UD-S14 UD-S14 TLDs. TLDs. The The UD-SI4 TLD UD-SI4 TLD badges badges eacheach contain contain fourfour elements.
elements. ElementsElements 2, 2, 3, 3, and and 44 in in each each badge badge are made are made of of calcium calcium sulfate sulfate with with SOO mg/cm22 of SOO mg/cm of filtering filtering and and element element 11 is is composed composed of of 22 Hthium tetraborate Hthium tetraborate with with filtering filtering of of 2525 mg/cm mg/cm ** Only Only thethe calcium calcium sulfate sulfate elements elements are are normally used normally used forfor environmental environmental measurements measurements because because of of their their higher higher JightJight output output per per of radiation unit of unit radiation exposure exposure relative relative to to the the lithium lithium tetraborate tetraborate and,and, consequently, consequently, greater greater sensitivity for sensitivity for the the detection detection and and measurement measurement of of radiation.
radiation.
Note: Element Note: Element 11 would would be be ofof value value in in the the event event ofan ofan unusually unusually large large release release of of noble gases, noble gases, especialIy especialIy xenon, xenon, that that would would produce produce relatively relatively low-energy low-energy X-ray or X-ray or gamma gamma emissions.
emissions. This This is is because because the the lithium lithium tetraborate tetraborate does does not over-respond not over-respond to to such such low-energy low-energy emissions emissions as as does does the the calcium calcium sulfate.
sulfate.
The TLD element The TLD element manufacturers' manufacturers' attempt attempt to to make make eacheach element element as as similar similar as as possible possible to to each of each of the the other other elements elements in in each each batch batch that that is is produced.
produced. Nevertheless, Nevertheless, each each element element ends up ends up somewhat somewhat different different in in its its resp~nse to to radiation.
radiation. In In order order to to minimize minimize the the effect effect of these of these inherent inherent differences differences when comparing actual when comparing actual monitoring monitoring results results forfor different' different' elements, Element elements, Element Correction Correction FactorsFactors (ECFs)
(ECFs) are are determined determined for for each each element.
element. The The ECFs are ECFs are used used to to effectively, effectively, normaIiz~ the. the. readings readings of of the the field field elements elements placedplaced at at particular monitoring particular monitoring locations locations for for given.
given. monitoring monitoring periods periods to to thethe average average of of the the readings that readings that would would De De expected expected if if so-called so-called reference* elements elements were were to to bebe placed placed simultaneously at simultaneously at those those individual individual locations.
locations. Reference Reference elements elements are are elements elements that that have have been demonstrated been demonstrated to to display display superior superior measurement measurement performance.
performance.
The selection process The selection process for for reference reference elements elements involves involves repeatedly repeatedly irradiating irradiating aa large large set set of elements, of elements, processing processing them, them, calculating calculating the the mean mean response response for for each each setset ofof elements, elements, and evaluating and evaluating the the deviation deviation of of each each individual individual elementelement response response from from the the mean mean response. After response. After this this process process has has been been repeated repeated at at least least several several times, times, the the elements elements with with the least the least variability variability in in their their responses responses and and withwith meanmean responses responses nearestnearest to to the.
the. mean mean response of response of the the entire entire population population of of elements elements are are chosen chosen as as reference reference elements.
elements.
To determine To determine ECFsECFs for for individual individual field field elements, elements, the the elements elements are are first first exposed exposed to to known amounts of known amounts of radiation radiation (100 (100 mR) mR) and and processed, processed, aa minimum minimum of of three three times times each.
each.
Each element Each element reading reading is is then then divided divided by by the the mean mean of of the the readings readings obtained obtained from from reference elements reference elements (typically (typically 30 30 toto 35)
- 35) that that werewere exposed exposed to to the the same same amounts amounts of of radiation as radiation as the the elements elements for for which which the the ECFs ECFs are are being being determined determined and and that that were were processed at processed at the the same same time time as as these these elements.
elements. The The meanmean quotient quotient (ratio)
(ratio) is is then then calculated for calculated for each each element element by by summing summing the the quotients quotients obtained obtained for for each each processing processing and and then dividing then dividing byby the the total total number number of of the the processings processings performed.
performed.
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report E-2 E-2
Appendix E Appendix E The following The following equation equation shows shows how how ECFs,are ECFs,are calculated: calculated:
- ;', ," -it' E 2;-
- :-L
'1 EuJ ECF=
': n
. (, .;
where where
- - ...:. t ~ ~ -: #: ..
an uncorrected an uncorrected exp'osure exp'osure reading reading for for the the 'element.
'element.
, * "'-; ; ';' )1' :; ,. "" '
=the total n =the total number number of individual of individual ..!"' .
element exposures element exposures averaged.
averaged.
Er~/ = the mean
= the mean of tlie ECF~corrected exposure of tlie exposure readings readings of of the the reference reference elements.
elements.
Irradiated control1LDs are Irradiated control1LDs are processed processed (read) (read) with with the the batches batches of of TI.Ds TI.Ds from from the the field field toto provide both provide both processing processing calibration calibration information information and and quality quality control.
control. Field Field control control 11.Ds, which 11.Ds, which accompany accompany the the field field TLDs TLDs when when they they are are being being takentaken toto their their monitoring monitoring locations and locations and subsequently subsequently retrieved retrieved from from these these locations,locations, and and cave cave control control TLDs, TLDs, which are which are stored stored with with the the field field TLDs TLDs for for the the periods periods between between annealing annealing and and field field
~- distribution and distribution and between between retrieval retrieval fromfrom the the field' field' and and processing, processing, are are also also read read with with the the field 11.Ds field 11.Ds to to provide provide checks checks on on the the exposures exposures that that the the field field TIDsTIDs might might receive receive on on way to their way their to and and from from their their monitoring monitoring locations locations arid arid while while in in storage, storage, respectively.
respectively.
The raw data The raw data from from the the field field 11.D 11.D processings processings is is Run Run Calibration Calibration FactorFactor (RCF)
(RCF) corrected corrected using the using the irradiated irradiated control1LD control1LD data. data. The The irradiated irradiated control control 11.Ds 11.Ds areare exposed exposed to to 100 100 mR from mR from aa cesium-137 cesium-137 source source at at the the Battelle Battelle Lab Lab in in Richland Richland WA. WA. The The irradiated irradiated 11.Ds 11.Ds are accompanied are accompanied en en route route toto and and from from the: the: Battelle Battelle Lab Lab by:transit by:transit control control 11.Ds.
11.Ds. An An estimate of estimate of the the exposures exposures received received by by thethe irradiated irradiated 11.Ds 11.Ds in-transit in-transit is is obtained obtained by by processing the processing the transit transit controls controls and and determining determining the the transit transit control control mean mean byby thethe following following equation:
equation:
, n where where . }'<;- -i' _', .
the the mean mean of of the the elementally elementally corrected corrected exposure exposure readings readings of of all all the transit the transit control control elements.
elements.
the uncorrected exposure the uncorrected exposure reading reading of of each each individual individual transit transit control element:
control element:
E*3 "",2003 Radiological Radiological Environmental Environmental Monitoring Monitoring Report Report f - ~~ 1 ~
- II II AppendixE AppendixE I
'J ECP; =
ECP; = the elemental correction the elemental correction factor factor of of each each individual individual transit transit control control element.
element.
n=
n = the total the total number number of of individual individual element element exposures exposures averaged.
averaged.
The mean The mean of of the the transit transit control control exposures exposures is is then then subtracted subtracted from from each each of of the the elementally corrected exposures elementally corrected exposures of of the the irradiated irradiated elements elements to to obtain obtain thethe net net exposures exposures for each for each element element resulting resulting from from the the irradiation.
irradiation. The The mean mean of of these these netnet exposures exposures is is then then divided by divided by the the known known exposure exposure (100 (100 mR)mR) from from the the irradiation irradiation to to determine determine the ReF.
the ReF.
The following The following equation describes the equation describes calculations performed:
the calculations performed:
+/-(~-E
)it:
n RCF==---------~
KEiC where where RCF = = thethe run correction factor run correction factor for for an an individual individual field field monitoring monitoring element.
element.
=
E/ = the exposure the exposure reading reading of of each each individual individual irradiated irradiated control control element.
element.
ECP; =
ECP; = the elemental correction the elemental correction factorfactor ofof each each individual individual irradiated irradiated control control element.
element.
=
nn = the total the total number number of of individual individual element element exposures exposures averaged.
averaged.
KE = the KEicic = the known known exposure exposure for for each each ofof the the irradiated irradiated control control elements.
elements.
Exposure readings Exposure readings for for individual individual field field monitoring monitoring elementselements are are corrected corrected using using thethe appropriate mean transit appropriate mean transit exposure exposure and and the the elemental elemental and and runrun correction correction factors factors asas follows:
follows:
where where CExx CE =
= the corrected the corrected exposure exposure readingreading for for field field monitoring monitoring element element x. x.
UE xx =
UE = the uncorrected the uncorrected exposure exposure reading reading for for field field monitoring monitoring element element x. x.
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report E-4 E-4
Appendix E Appendix E ..
\..../ >". I ~'::.: ,~>; _1" ECF:
ECF: =
= the elemental the elemental correction correction factor factor for for field field monitoring monitoring element element x. x.
ETC ETC = mean
= mean transittransit exposure exposure :.,' " '
RCFxx =
RCF = the run the run correction correction f~ctor for for field field monitoring monitoring element element x. x.
NOTE:
NOTE: The The mean mean transit transit exposure'is"determined exposure'is"determined from from thethe elements elements of of the the TLDs TLDs thatthat accompany the accompany the field field TLDsTLDs during during transportation transportation to to and and fromfrom thethe field field locations,'
locations,' ,"
The exposure* representing The representing each each environmental' environmental' nionitoring' nionitoring' location location ~ and and monitoring monitoring period is period normaliy the is normaliy the mean mean ofthe ofthe corrected corrected exposure exposure readings readings for for aa total total of of six six calcium calcium sulfate elements, sulfate elements, three three from from each each of tWo differerit,TLDs of tWo differerit,TLDs at at ea*ch location.
location. The:following The:following equati~n shows shows the the calculation calculation ofthis ofthis exposure:
exposure: ,
where where E=
E= cc the mean of the mean of the the corrected corrected exposure exposure readings readings for for aa given given monitoring monitoring location and location and period, period, ,,
CEI =
CEI = the corrected the corrected exposure exposure reading reading of of anan individual individual element element for for aa given given monitoring monitoring location location and and period. period.
n = the
= the total total number number of of individual individual element element exposures exposures averaged.
averaged.
The mean of The mean of th~ correctedcorrected eXp'osure eXp'osure readings:
readings: for' aa for' give~ location location and and period period may may be be calculated using calculated using less less than than the the six six calcium calcium sulfate sulfate elements elements if if the the reading reading fromfrom oneone ofthe ofthe elements is elements is more more than than twotwo standilrd standilrd deviations' deviations' !from' !from' the" the" mean.
mean. In In this this situation, situation, thethe mean would mean would be be recalculated recalculated with with only only five five element element readings, readings, excluding excluding the the element element reading that reading that was was moremore than' than' two two stan~~~ d~v~at~<?ns from~heoriginally calculated calculated mean.mean.
The mean'may The mean'may be be automaticaHy'calculated automaticaHy'calculated by'the by'the dosimetty dosimetty software software with with as as few few asas four element four element readings readings before before the dahds flagged".'
the dahds flagged".' "The "The toliowing' toliowing' calculation calculation is is used used toto determine the determine the standard standard deviatiori deviatiori of~e \~~rrectea
~. . \ \
elemental exposure elemental exposure readings:
readings: ,,
where where E-S " 20032003 Radiological Radiological Environmental Environmental Monitoring Monitoring Report Report
II **
AppendixE AppendixE the standard the standard deviation deviation of of the the corrected corrected exposure exposure readings readings fromfrom aa given monitoring location given monitoring location andand period period for (n-l) degrees for (n-l) degrees of of freedom.
freedom.
Ee =
Ee = the mean of the mean of the the corrected corrected exposure exposure readings readings for for aa given given monitoring monitoring location and location and period.
period.
CEi =
CEi = the corrected the corrected exposure exposure reading reading ofof an an individual individual element element for for aa given given monitoring location and monitoring location and period.
period.
n =
= the total the total number number of of individual individual element element exposures exposures averaged.
averaged.
The standard monitoring The standard monitoring period period for for the the r.eporting r.eporting ofof TLD TLD exposures exposures is is the the calendar calendar quarter. The quarter. The calendar calendar quarter quarter is is defined defined as as aa period period of of 91.25 91.25 days.
days. The The actual actual monitoring periods monitoring periods forfor TLDs TLDs theinin the field field are are often often for for times times other other than than 91.25 91.25 days.
days. The The means of means of the the corrected corrected exposures exposures for for these these nonstandard nonstandard periods periods mustmust be be normalized normalized to to the standard the standard calendar calendar quarter.
quarter. The The following following equation equation shows shows how how thethe normalization normalization is is performed:
performed:
NE= ~x91.25 NE=
'--./
NE NE = mean
= mean corrected corrected exposure exposure normalized normalized to to aa standard standard calendar calendar quarter quarter of of 91.25 days.
91.25 days.
Ee =
Ee = the mean of the mean of the the corrected corrected exposure exposure readings readings for for aa given given monitoring monitoring location and location and period.
period.
MP = = the the actual actual TLD TLD monitoring monitoring period period (time (time in in the the field) field) inin days.
days.
TLD DATA TLD DATA INTERPRETATION INTERPRETATION Pre-operational Pre-operational and and operational operational data data areare compared compared for for thethe purpose purpose of of determining determining whether or whether or not not TLD TLD datadata may may indicate indicate aa dose dose contribution contribution from from SSESSSES operation.
operation.
Between 1979 Between 1979 and and 1994, 1994, bothTLD bothTLD types types andand TLD TLD processing processing systems systems changed changed moremore than once.
than once. InIn order order toto avoid avoid possible possible confusion confusion in in data data interpretation interpretation as as aa result result ofof these these changes, ratios changes, ofTLD doses ratios ofTLD doses for for specific specific indicator indicator locations locations to to the the average average of of thethe TLD TLD doses for doses for control control locations locations from from operational operational periods periods compared compared to to their their counterparts counterparts fromfrom the preoperational the preoperational period.
period. Comparison Comparison of of these these ratios ratios is is performed performed in in lieu lieu of of comparing comparing the actual the actual operational operational and and preoperational preoperational doses. doses. The The following following equation equation shows shows how how these ratios these ratios are are calculated:
calculated:
I
'-...-/
2003 RadioJogicaJ 2003 RadioJogicaJ Environmental Environmental Monitoring Monitoring Report Report E-6 E-6
AppendixE AppendixE where where rjrj = = the indicator-to-control-average dose the indicator-to-control-average dose ratio ratio for for aa particular particular location and location and calendar calendar quarter, quarter, dj dj = --the
the quarterly quarterly dose dose for for aa particular particular indicator indicator location, location, and and de
de = the the average average quarterly quarterly dose dose for for certain certain control control locations.
locations.
Note:
Note:
The rj are The rj are the the quotients quotients ofth(dndicator ofth(dndicator doses doses toto the the average average doses doses of of the the following control following control locations:
locations: 3G4, 3G4, 4Gl~ 7GI, 7GI, 12Gl, 12Gl, andand 12G4.
12G4. OnlyOnly these these control10cations are control10cations used because are used because they they were were the the only only ones ones existing existing during during the the preoperational period.
preoperational period.
Operational Operational rjrj forfor indicator indicator locations locations that that dodo notnot have have preoperational preoperational histories histories are are compared with compared with thethe range range of of preoperational-preoperational- con'trol-to:.control-average con'trol-to:.control-average ..dose dose ratios ratios (rc)
(rc) experienced at experienced at control control locations.
locations. --It It dm'be'safely dm'be'safely assumed assumed thatthat the preoperational range the preoperational range of these of these rc rc at at control control locations locations are are the the result result of of variations variations in in the the levels levels ofof background background radiation at radiation at those those locations.
locations. Any Any operational operational indicator indicator rjrj for for anan indicator indicator location location without aa preoperational without preoperational history history that that is is above above the the uppermost uppermost rangerange expected expected at at control control locations based locations based on on preoperational preoperational data data is is assumed assumed to to suggest suggest aa possible possible contribution contribution from the from the SSES SSES operation.
operation. The The following following equation equation shows shows howhow rcrc is is calculated:
calculated:
where where rc rc is the control-to-control-average is the control-to-control-average dose dose ratio ratio for for aa particular particular location and location and calendar calendar quarter, quarter, de de is the is the quarterly quarterly dose dose for for aa particular particular control control location, location, and and de de is the is the average average quarterly quarterly dose dose for for certain certain control control locations.
locations.
E-7 E-7 -- 2003 2003 Radiological Radiological En\'ironmental En\'ironmental Monitoring Monitoring Report Report
I
- Appendix E Appendix E
>**J where where DSSES DSSES = the
= the dose dose attributable attributable toto SSES SSES fuelfuel cycle cycle operations, operations,
=
the indicator-to-control the indicator-to-control average ratio for average ratio for aa particular particular location location and calendar quarter, and calendar quarter, 1.22 1.22
= the highest expected the highest expected rc rc for for control control locations locations due due to variations to variations in natural in natural radiation radiation levels levels based based onon preoperational preoperational data.
data. Refer Refer to location to location 12G4 12G4 inin Attachment Attachment 1. 1.
DCA DCA =
= the average the average quarterly quarterly dose dose for for control control locations.
locations.
OF OF =
= the occupancy the occupancy factor.
factor.
Each year, the Each year, the SSES SSES attributable attributable doses doses calculated calculated .for
.for each each calendar calendar quarter quarter are are summed summed for all for all calendar calendar quarters quarters at at each each location location to to obtain obtain annual annual doses doses byby location.
location.
. I
"....J 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report £-10
£-10
DETERMINATION DETERMINATION OF OF GROSS GROSS ALPHA ALPHA AND/OR AND/OR GROSS BETA GROSS BETA ACTIVITY ACTIVITY .. ..
TELEDYNE TELEDYNE BROWN BROWN ENGINEERING ENGINEERING ENVIRONMENTAL SERVICES ENVIRONMENTAL SERVICES Aliquots of Aliquots of water water samples samples are are evaporated evaporated to to near dryness in near dryness in beakers.
beakers. The The remaining remaining volumes (approximately five volumes (approximately five milliliters milliliters or or less) less) are transferred to are transferred to stainless stainless steel steel planchets and planchets and evaporated evaporated to to dryness.
dryness. .; .; ..
All planchets are All planchets are counted counted in, in, Jow Jow background background gas-flow gas-flow proportional proportional counters.
counters.
Calculations of Calculations of both both gross gross alpha alpha and and beta beta activities activities include include the the use use of of empirical empirical self-self-absorption correction absorption correction curves curves to to account account for for changes changes in in effective effective counting counting efficiency efficiency occurring as occurring as aa result of changes result of changes in in the the masses masses ofof residue residue being counted.
being counted.
Weekly air particulate Weekly air particulate ""filters filters are are placed placed into'planchets into'planchets as as received received and and counted counted in in low low background gas-flow background gas-flow proportional proportional counterS.
counterS. No No corrections corrections 'are 'are made made forfor beta beta self-self-absorption when absorption when calculating calculating the the gross gross beta beta activities activities of of the the air air particulate particulate filters filters because because of the of the impracticality impracticality of of weighing weighing the the deposit deposit and:
and: because because the the penetration penetration depth depth ofof the the deposit into deposit into the the filter filter is is unknown.
unknown. ..
CALCULATION OF CALCULATION OF THE THE SAl\1PLE SAl\1PLE ACTIVITYACTIVITY unit volume unit pC; pC; volume or or mass mass 222
[f-
[f-222 (V)(E)
R (V)(E)
.] + + 2~
222 (V) 222 (V) (E)
(E) net activity net activity randomrandom uncertainty uncertainty E-11 E-11 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
I
- AppendixE AppendixE
~J where:
where: C C =
total counts total counts for for sample sample tt
= count time count time for for sample/background sample/background (minutes)
(minutes)
~ =
= background count background count rate rate of of counter counter (cpm)
(cpm) 2.22 2.22 =
= dpm dpm pCi pCi V(M)
V(M) =
= volume or volume or mass mass of of sample sample analyzed analyzed E
E =
= efficiency of efficiency of the the counter counter (cpm/dpm)
(cpm/dpm) 4.66 4.66 =
= sigma level sigma level Calculation of Calculation of the the Minimum Minimum Detectable Detectable Concentration Concentration (MDC)
(MDC) Value Value 4.66~R.
MDC=
MDC= II 2.22 (V) 2.22 (V) (E)
(E) \
---../
))
. I 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report E-12 E-12
AppendixE AppendixE RADIOCHEMICAL RADIOCHEMICAL DETERMINATION ** -"
DETERMINATION OF
.<-' 1.
1 .)
)44 J J .,
OF 1-131 1-131
,IN CHARCOAL
,IN CHARCOAL AND AND VEGETATION VEGETATION SAMPLES SAMPLES TELEDYNE TELEDYNE BROWN BROWN ENGINEERING ENGINEERING ENVIRONMENTAL SERVICES ENVIRONMENTAL SERVICES Radioiodine is Radioiodine is separated separated from from the the sample sample matrix matrix to to periodate periodate solution.
solution.
Charcoal filters are Charcoal filters are 'opened
'opened andand the the exPosed exPosed ::charcoal charcoal is' is' emptied emptied 'into 'into aa refluxing refluxing flask, flask, iodide carrier iodide carrier is is added, added, andand the the mixture mixture is is refluxed refluxed in in sodium sodium hydroxide hydroxide to to remove remove the the iodine absorbed iodine absorbed on on the the charcoal charcoal and and bringing bringing it it into into sohition.
sohition. The The resulting resulting iodide iodide solution is solution is oxidized oxidized with with hypochlorite hypochlorite to to periodate.
periodate.
Vegetation samples Vegetation samples are are chopped,':iodide chopped,':iodide 'carner 'carner added, added, the the mixture mixture 'evaporated
'evaporated to to dryness, leached dryness, leached with with sodium sodium hydroxide, hydroxide, and and fused fused in in aa muffle furnace. The muffle furnace. The resulting resulting melt is melt is dissolved dissolved in in distilled distilled waterwater and and filtered. filtered. The The resulting resulting iodide iodide solution solution isis with hypochlorite oxidized with oxidized hypochlorite to to periodate periodate..
- '\'\ ii ..
The periodate solution The periodate solution is reduced t~ 'iodine is reduced 'iodine with with hydroxylamine hydroxylamine hydrochloride, hydrochloride, and and extracted into extracted into toluene toluene asas free iodine.: "'The;iC)~ineJs back free iodine.: back extracted extracted into into disti11ed disti11ed water water through reduction through reduction to to iodide iodide with with aqueous aqueous 'sodium 'sodium bisulfite bisulfite and and isis ultimately ultimately precipitated precipitated as palladium as palladium iodide.
iodide. TheThe precipitate precipitate is is weighed weighed for for chemical chemical yield yield and and is mounted mounted on on aa nylon planchet nylon planchet for for low low level level beta beta counting.
counting.
The dried The dried precipitate precipitate is is beta beta counted counted on on aa low-level low-level counter. counter.
CALCULATION OF CALCULATION OF THE THE SAMPLE SAMPLE ACTIVITY ACTIVITY
[--R6] ~
C C -+Rb 2
2 t A=
A= tt +/-
+/- tt 2.22(V)(
2.22(V )()')(
)')( DF DF )( )(E) E) 2.22(V 2.22(V )( )(y)(
E) net activity net activity random uncertainty random uncertainty where:
where: A A =
= activity concentration activity concentration (PCill) (PCill)
C C =
total counts total counts from from sample sample tt
= counting time counting time for for samplesample (min) (min)
Rb Rb =
= background count background count rate rate of of counter counter (cpm) (cpm)
V V 2.22 2.22 =
= dpm dpm pCi pCi E-13 E-13 "2003 Radiological "2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
I I AopendixE AopendixE v
v =
= volume of volume of sample sample analyzed analyzed (liters)
(liters)
\.J yy =
chemical yield chemical yield of of the the mount mount oror sample sample counted counted DF DF
= decay factor decay factor from from the the collection collection (milk/vegetables)
(milk/vegetables) oror midpoint midpoint of compositing period of compositing period (water/charcoal (water/charcoal cartridges) cartridges) to to the the mid-mid-count time count time E
E =
= efficiency of efficiency of the the counter counter for for the the 1-131 1-131 betas.
betas.
4.66 4.66 =
= sigm~ level level Note: Efficiency Note: Efficiency isis detennined detennined by by counting counting an an 1-131 1-131 st~ndard.
Calculation of Calculation of the the MDC MDC MDC MDC 4.66~*
2.22(V)(y)( DF)(E) 2.22(V)(y)( DF)(E)
'-.-/
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report* E-t4 E-t4
.. 'l: '"..
AppendixE AppendixE RADIOCHEMICAL~DETERMINATION OF , ".. J. ... ~
- OF 1-131 1-131 IN MILK IN MILK AND AND WATER WATER SAMPLES SAMPLES FRAMATOMEANP FRAMATOMEANP ENVIRONMENTAL LABORATORY ENVIRONMENTAL LABORATORY First, iodide carrier First, iodide carrier is is added added to to either either aa two-kilogram two-kilogram sample sample aliquot aliquot ofof milk milk oror water.
water.
For water, For water, the the next next step step isis to to add add sodium sodium hypochlorite, hypochlorite, followed followed by by hydroxylamine hydroxylamine hydrochoride, and hydrochoride, and finalJy finalJy sodium sodium bisulfite; bisulfite; to to convert convert all all of of thethe iodine iodine in in the the sample sample to to iodide. After iodide. After sufficient sufficient timetime for for equilibration equilibration of of the the stable stable iodide iodide carrier, carrier, anion anion exchange resin exchange resin is is added added to the sample to the sample to to extrac(the extrac(the iodide iodide from from thethe sample sample aliquot.
aliquot. The The iodide ion iodide ion isis subsequently subsequently removed removed from from the the 'resin
'resin using using sodium sodium hypochlorite.
hypochlorite. It It is is then then reduced to reduced to elemental elemental iodine iodine andand transferred transferred from from the the aqueous aqueous phasephase toto the the toluene.
toluene. TheThe iodine is iodine is then then reduced reduced to to iodide iodide using using sodium sodium bisulfite bisulfite andand back back extracted extracted into into the the aqueous phase.
aqueous phase. Once Once in in the the aqueous aqueous phase,phase, the the iodide iodide is is precipitated precipitated as as cuprous cuprous iodide iodide following the following the addition addition ofof cuprous cuprous chloride.
chloride. -:-: :: .. ,.,. ..
Another aliquot of Another aliquot of sample sample may may be be used,used, if if activity activity is is detected detected in in the the sample, sample, to to determine the determine the original original stable stable iodide iodide content content of of the the sample sample using using aa specific-ion specific-ion electrode.
electrode.
This information This information would would thenthen be be used used to to correct correct the the chemical chemical yield yield determined determined from from thethe
\.../~ mass ofthe mass ofthe dried dried precipitate.
precipitate.
The dried The dried precipitate precipitate isis then then counted counted using using aa beta/gamma beta/gamma coincidence coincidence counter.
counter.
CALCULATION OF CALCULATION OF SAMPLE SAMPLE ACTIVITY ACTIVITY A
A =-t----:~----'-----
Where:
Where:
A = activity
= activity concentration concentration (pCi/l) (pCi/l)
G G =
= gross gross count count at at the the end end of of the the sample sample counting counting interval interval (t)
(t) tt = = sample sample counting counting interval interval B
B =
= background count background count raterate (cpm)
(cpm)
A =
A decay constant
= decay constant for 1-131 (5.987E-5 for 1-131 (5.987E-5 min-I) min-I) 2.22 2.22 = dpm/pCi
= dpm/pCi ..
V = volume
= volume of of sample sample (I) (I) y y = chemical
= chemical yield yield (recovery)
(recovery) of of the the iodide iodide E-IS E-IS 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
II II Appendix E Appendix E D
D = decay
= decay factor factor (e>i.T)
(e>i.T) where where AA is is the the decay decay constant constant for for 1-131 1-131 and T is and T is the the ,,
\-......,/
\-......,/
II decay from sample period from decay period sample colIection colIection (milk)
(milk) or or the the mid-point mid-point of of the the sample sample p'eriod (water) compositing p'eriod compositing (water) to to the the mid-point mid-point of of the the counting counting interval interval E
E =
= is the is the 1-131 1-131 beta/gamma beta/gamma counting counting efficiency efficiency (cpmJdpm)
(cpmJdpm)
CALCULATION OF CALCULATION OF MDC MDC 4.66 *J..
4.66 *J.. *t'
- t' J~
MDC MDC Where:
Where:
MDC MDC = minimum
= minimum detectable detectable activity activity concentration concentration (pei/l)
(pei/l) 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report E-16 E-16
AppendixE DETERMINATION DETERMINATION OF OF TRITIUM TRITIUM IN IN WATER WATER BY LIQUID BY
- LIQUID SCINTILLATION
, OJ SCINTILLATION :COUNTING
- ."co " "
- COUNTING TELEDYNE TELEDYNE BROWN BROWN ENGINEERING ENGINEERING ENVIRONMENTAL'SERVICES ENVIRONMENTAL'SERVICES Ten mjlJiJiters of Ten mjlJiJiters of water water is is mixed mixed witli' witli' liquid liquid scintillation scintillation material and counted material and counted for for typicaI1y 200 typicaI1y 200 minutes minutes toto determine determine its its a~tiYitY.' ,
I
. ~,;
- ~ ....
CALCULATION OF CALCULATION OF THE THE SAMPLESAMPLE 'ACTIVITY 'ACTIVITY FOR FOR TRITIUM TRITIUM
, .; .. :~. i' ':
_pCi=
.e.e
[~~&]
.2.22(V)(E) -,
.2.22(V)(E)
+ 2P;
-, 2.22(V)(E) 2.22(V)(E) net activity activity random uncertainty uncertainty .,
, )
net random where:
where: C C =
= total counts total counts from from ,sample r,'. f'
,sample
~ ,(
tt =
= count time count time for for sample sample (minutes) (minutes)
Rb Rb =
= background count background count rate rate of of counter counter (cpm)
(cpm) 2.22 2.22 =
dpm dpm pCi pCi vv
= initial volume initial volume before before enrichment enrichment (liters) (liters)
E E =
= efficiency of efficiency of the the countercounter for for tritium tritium (cpm/dpm)
(cpm/dpm)
,
- I Calculation of the Calculation the MDC MDC .
-., ' : "t- "
-,'-- . 4_66~R' MDC b;; , ,,:.' t (2.22)(V)(E)
'J ,,'
',1, i * . ~ .
- * -0'"
E*l7 :: " ~.. ~003 Radiological Radiological Environmental Environmental Monitoring Monitoring Report Report
II II AppendixE AppendixE Calculation of Calculation of SSES SSES Attributable Attributable Direct Direct Radiation Radiation Dose Dose based based on on Onsite Onsite Indicator Indicator TLD ,Measurements TLD ,Measurements For TLD locations For TLD locations where where directdirect radiation radiation dose dose contributions contributions from from thethe SSES SSES are are indicated, these indicated, these calendar calendar quarter quarter doses doses are are estimated estimated based based on on the the amounts amounts referred referred to to as as the excess the excess ratios.
ratios. Excess Excess ratio ratio for for each each location location '5 rj for
'5 rj for aa particular particular calendar calendar quarter quarter is is the amount the amount by by which which that that fifi exceeds exceeds the the high high end end ofof its its range range of of preoperationa'l preoperationa'l rj. rj. The The excess ratio excess ratio atat aa specific specific location location isis multiplied multiplied times times both both thethe average average dosedose forfor control control locations measured locations measured during during that that calendar calendar quarter quarter and and an an occupancy occupancy factorfactor based based on on aa reasonable estimate reasonable estimate ofof the the portion portion ofof the the calendar calendar quarter quarter thatthat aa MEMBER MEMBER OF OF THE THE PUBLIC might PUBLIC might spend near an spend near an onsite onsite TLD TLD location.
location. The The following following is is aa table table ofof occupancy factors occupancy factors that that are are used:
used:
Environmental Environmental TLD TLD Monitoring Monitoring Locations Locations Occupancy Occupancy FactorsFactors Onsite Onsite 4.56E-4 4.56E-4 Offsite Off site (other (other than than Private Private Residences)
Residences) 3.65E-3 3.65E-3 Private Residences Private Residences 1 1
The following equation The following equation is is used used for for obtaining obtaining direct direct radiation radiation doses doses attributable attributable to to the the SSES at SSES at indicator indicator TLDTLD locations locations when when preoperational preoperational data data exists exists for for those those locations:
locations:
where where DssEs ==
DssEs the dose the dose attributable attributable toto SSES SSES fuelfuel cycle cycle operations, operations, rj rj = the
= the indicator-to-control indicator-to-control average average ratioratio for for aa particular particular location location and calendar and calendar quarter, quarter, ru ru = the
= the indicator-to-control indicator-to-control average average ratio ratio corresponding corresponding to to the the upper upper end of the end of the 95%
95% confidence confidence range range forfor aa particular particular location for location for the the preoperational preoperational period, period, andand DCA DCA = the
= the average average quarterly quarterly dose dose for for control control locations.
locations.
OF OF = the
= the occupancy occupancy factor.
factor.
The equation below The equation below is is used used for for obtaining obtaining direct direct radiation radiation dosesdoses attributable attributable to to the the SSES SSES at indicator at indicator locations locations when when preoperational preoperational datadata does not exist does not exist for for those those locations:
locations: '0 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
AppendixE AppendixE
\...../' Flagging Em'ironmental Flagging Em'ironmental TLD TLD Measurements Measurements for for Possible Possible Non-Natural Non-Natural Dose Dose Contributions Contributions .. ' , .' ,.:' ;" , . ,:
, ", ~ , -: ., .' ' :; ~ ~"'"
Confidence ranges, Confidence ranges, within within which:
which: 95% 95% i of of 'environmental
'environmental TLD TLD dosesdoses resulting resulting from from natural, background natural, background radiation radiation areare expected'to expected'to be; be; have have been been derived derived for for each each location location with aa preoperational with preoperational history history by by multiplying multiplying "the' "the' standard standard deviation deviation (S)(S) of of the the fjfj for for the the location by location by P1e P1e appropriate appropriate tt scor~ (t) (t) base~;on the the applicable applicable degrees degrees ofof freedom freedom for for -
each each location.
location. (Degrees (Degrees of of freedom freedom ,(dflare ,(dflare .equal .equal to to thenumber thenumber of of ratios ratios that that were were averaged les~ one.)
averaged one.) .. The The product product of of the the tt score score arid arid the the standard standard deviation deviation (tS)
(tS) was was then then subtracted from subtracted from the the mean mean (x)
(x) to to dete~ine t~elower end end ofof the the 95%
95% confidence confidence range range (R) and (R) and added added to to the the mean*to obtain obtain t~t:upper. end end of of the the range range (R)(R) as as indicated indicated by by the the following equation:
following equation: .
The following The following tt scores scores were were used used in in the' the' ~ge calculaiions: calculaiions: .
, .t SCORES* ; , , -
df df to.os to.os 11 12.706 12.706 22 ,
[
.. 4.303 4.303 .
33 .. 3.182 3.182 44 2.776 2.776 55 2.571 2.571 66 "- " 2.447 2.447 77 2.365 2.365
! * ~. '.' 1
- f For For indicator indicator locations locations with with no no preoperational preoperational history, history, TLD TLD results results are are flagged flagged for for potential potential non-natural non-natural ,dose ,dose contributions contributions to to TLD.measurements TLD.measurements based based onon comparisons comparisons to to the the maximum maximum .. expected expected variation, variation, ,in ,in ,control,,;,to-control-average
,control,,;,to-control-average dose dose ratios ratios (re:)
(re:) for for control locations.
control locations. The The expected expected ranges ranges of of fe for each fe for each coni,rolconi,rol location location forfor each each calendar calendar quarter during quarter during the the 1980-81 1980-81 preoperational preoperational period period have have been been calculated.
calculated. The The highest highest expected re expected re ,,for for all all the the preope~tional co~tr~lloca~i~ms is is 1.22.
1.22.
. ( ~ .
Ratios for Ratios for indicator indicator locations locations greater greater .. than than 1.22, 1.22, are are ,flagged
,flagged for for possible possible SSESSSES direct direct radiation dose radiation dose contributions.
contributions. { *** j L '
~:
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report E-8 E-8
II II itppendix E itppendix E DETERMINATION OF DETERMINATION OF GAMMA GAMMA EMITTING EMITTING RADIOISOTOPES RADIOISOTOPES
\J TELEDYNE TELEDYNE BROWN BROWN ENGINEERING ENGINEERING ENVIRONMENTAL SERVICES ENVIRONMENTAL SERVICES & &
. FRAMA TOME ANP ANP .
ENVIRONMENTAL LABORATORY ENVIRONMENTAL LABORATORY Gamma emitting radionuclides Gamma emitting radionuclides are are detennined detennined with with the the useuse of of aa lithium-drifted lithium-drifted gennanium (Ge(Li>>
gennanium (Ge(Li>> and and highhigh purity purity gennanium gennanium detectors detectors with with highhigh resolution resolution spectrometry in spectrometry in specific specific media.
media. such such as, as, air air particulate particulate filters, filters, charcoal charcoal filters, filters, milk, milk, water, vegetation, water, vegetation, soil/sediments.
soil/sediments. biological biological media, media, etc.
etc. Each Each sample sample is is prepared prepared and and counted in counted in standard standard geometries geometries suchsuch as as one one liter liter or or four four liter liter wrap-around wrap-around Marinelli Marinelli containers, 300 containers, m] or 300 m] or 150 150 m]m] bottles, bottles, two-inch two-inch filter filter paper paper source source geometries, geometries, etc. etc.
The analysis of The analysis of each each sample sample consists consists ofof calculating calculating the the specific specific activities activities of of all all detected detected radionucHdes as radionucHdes as well well as as the the minimum minimum detectable detectable concentration concentration for for aa standard standard Hst Hst of of nuclides. The nuclides. The gennanium gennanium detection detection systems systems are are calibrated calibrated for for each each standard standard geometry geometry using certified using certified radionuclide radionuclide standards standards traceable traceable to to the the National National Institute Institute ofof Standards Standards and Technology.
and Technology.
CALCULATION OF CALCULATION OF THE THE SAMPLE SAMPLE ACTIVITY ACTIVITY Net pCi // vol or mass =
[C-B]
[C-B]
---=----=----
= ---=----=----
+
+ 2.JC+B 2.JC+B 2.22(V)(E)(GA)DF)(t) 2.22(V)(E)(GA)DF)(t) 2.22(V)(E)(GA)(DF)(t) 2.22(V)(E)(GA)(DF)(t) net activity net activity random uncertainty random uncertainty where:
where: cc =
= area, in counts, area, in counts, of of aa spectral spectral region region containing containing aa gamma gamma emission of emission of the the nuclide nuclide of of interest interest Note (l):
Note If the (l): If the detector detector exhibits exhibits aa peak peak in in this this region region when when counting aa blank, counting blank, thethe counts counts from from that that peak peak are are subtracted subtracted from from C before C before using using thethe above above equation.
equation.
Note If no (2): If Note (2): no peaks peaks areare exhibited, exhibited, thethe counts counts in in the the channels channels where the where the predominant predominant peaks peaks for for gammas gammas from from selected selected radionuclides would radionuclides would be be expected expected areare summed summed for for CC and and used used inin the calculation the calculation of of "net" "net" activity.
activity.
B B =
= background background countscounts in in the the region region ofof interest, interest, calculated calculated by by fitting fitting aa straight straight line line across across the the region region connecting connecting the the two two adjacent adjacent regions.
regions.
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report E*18
Appendix E Appendix E Note:
Note: If no peak If no peak exists exists in in aa region region from from which which aa "net" "net" activity activity is is being being calculated, background calculated, background is is represented represented by by the the average average ofof the the counts in counts in one one channel channel from from each each side side ofof that that region.
region.
tt =
= counting interval counting interval ofof sample sample (minutes)
(minutes) 2.22 2.22 =
= dpmJpCi dpmJpCi V
V =
= volume or volume or mass mass ofof sample sample analyzed analyzed E
E =
efficiency of efficiency of counter counter at at the energy region the energy region of of interest interest GA GA
gamma abundance of gamma abundance of the the nuclide nuclide atat the the gamma gamma emission emission energy energy under consideration under consideration DF DF
decay factor decay factor from from sample sample collection collection time time oror midpoint midpoint ofof sample sample collection (air 1-131) collection (air 1-131) toto midpoint midpoint of of the the counting counting interval interval Calculation of Calculation of the the MDC MDC MDC( pCi MDC( pCi // vol vol or or mass mass )
)=22*22(V 22(V I( I( ~~;::X DF DF X Xt II The width of The width of the the region region around around thethe energy energy where where an an emission emission is is expected expected isis calculated calculated differently for differently for MDCs MDCs than than itit is is for for the the width width of of aa peak peak that that is is actually actually identified.
identified.
Consequently, the Consequently, the value of B value of B used used inin the the two two equations equations may may differ.
differ.
E*19 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
I.:,
APPENDIXF APPENDIXF
~. ; ..
.. ;J ~ I .'
.,,1
- 1 ~
) ;, " , ;
,F-I'
,F-I' 2~03 R,adiological Environmental R,adiological Environmental Monitoring Monitoring Rep~rt
II II Appendix F Appendix F Exceptions Exceptions to to thethe SSES SSES Technical Technical Requirements Requirements occurred occurred in in the the monitoring monitoring of of the the following ~edia: drinking following drinking water, water, surface surface water, water, air, air, and and ambient ambient radiation radiation monitoring.
monitoring.
These exceptions These exceptions involvedinvolved sample sample collections collections that that did did not not take take place place for for the the required required periods due periods due to to sampling sampling equipment equipment problems problems and and various various environmental environmental conditions conditions (rain) that (rain) that impacted impacted sample sample col1ection col1ection or or analysis.
analysis.
These exceptions are These exceptions are discussed discussed in in this this appendix appendix and and specifically specifically documented documented in in the the tables of tables of Appendix Appendix I. I.
Drinking Water Drinking Water Sampling Sampling at at thethe Danville Danville Municipal Municipal Water Water Facility, Facility, monitoring monitoring location location 12H2, 12H2, proceeded flawlessly proceeded flawlessly during during most most of of 2003, 2003, with with only only one one exception.
exception. The The only only exception exception during 2003 during 2003 occurred occurred when when thethe sample sample collectors collectors incorrectly incorrectly mixed mixed the the drinking drinking water water sample for sample for week week 1 of the 1 of the April April monthly monthly composite composite period period with with the the week week 11 sample sample of of the the April monthly April monthly composite composite period period from from Surface Surface WaterWater monitoring monitoring location location 6S5.6S5. The The April monthly April monthly composite composite for for monitoring monitoring location location 12H212H2 sent sent for for analysis analysis contained contained only only weeks 2-4 weeks 2-4 for for April April 2003.
2003.
There were no There were no malfunctions malfunctions of of the the ACSACS at at monitoring monitoring location location 12H212H2 during during 2003.
2003.
Sampling at Sampling at this this location location was was routine routine (as(as expected) expected) for for 100%
100% of of the the year.
year.
Surface Water Water
"\.J Surface Monitoring Monitoring at. at. control control lOCation lOCation 6S6,.
6S6,. thethe ..SSES SSES River River Water Water Intake Intake Structure, Structure, and and
"\.J indicator.1ocation 2S7 indicator.1ocation 2S7 or or its its alternate alternate location location 6S7, 6S7, the the SSES SSES Cooling Cooling Tower Tower Blowdown Blowdown Discharge (CTBD)
Discharge (CTBD) to to the the Susquehanna Susquehanna River, River, areare the the only only environmental environmental surveillance's surveillance's of surface of surface water water required required by by SSES SSES Technical Technical Specifications.
Specifications. The The other other SSES SSES REMP REMP routine indicator routine indicator surface surface waterwater monitoring monitoring location location on on the the Susquehanna Susquehanna River,River, which which isis downstream from downstream from the the SSES SSES discharge discharge to to the the river, river, and and the the monitoring monitoring location location at at LTAW are LTAW are not not required.
required. They They have have been been monitored monitored to to provide provide added added assurance assurance thatthat the the environment is environment is not not being being compromised compromised by by radiological radiological releases releases resulting resulting from from the the SSES SSES operation.
operation.
SampJing SampJing at at locations locations 6S6 6S6 and and 2S7 2S7 or or 6S7 6S7 isis required required to to be be performed performed by by the the collection collection of aliquots of aliquots at at time time intervals intervals that that are are small small compared compared to to the the compositing compositing period. period.
Composite samples Composite samples from from these these locations locations are are required required to to bebe analyzed analyzed monthly monthly and and are are expected to expected to be representative of be representative of the the streams streams fromfrom which which they they are are collected.
collected.
Problems occurred in Problems occurred in 2003 2003 with with the the automatic automatic composite composite sampler sampler (ACS)
(ACS) at at sampling sampling location 6S6 location 6S6 during during portions portions of of the the following following collection collection periods:
periods: March March 17, 17, through through March 24, March 24, 2003 2003 and and June June 23,23, through through June June 26,26, 2003.
2003. Sample Sample collectors collectors discovered discovered low low flow through flow through the the ACSACS due due to to rising rising river river level level causing causing debris debris and and silt silt build-up build-up on on intake intake screens. Initially, screens. Initially, the the ACS ACS sample sample flow flow rate rate was was adjusted adjusted to to insure insure sufficient sufficient volume volume was collected.
was collected. Preventive Preventive maintenance maintenance was was performed performed on on the the ACS ACS (cleaned (cleaned lines) lines) and and the sample the sample flow flow rates rates were were reset reset to to 1.5 1.5 gpm.
gpm.
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report F-2 F-2
Appendix F
'-...J" The ACS at The ACS at monitoring monitoring location location 6S6,operated 6S6,operated routinely, routinely, (as (as ,expected)
,expected) for for approximately approximately of' 2003~ ,No 97% of' 97% ,No malf~,nc~ons, of.'th( of.'th( AC~. at at ID,?nitoring ID,?nitoring l#ation l#ation 6S6 6S6 required required th,e th,e colleCtion of colleCtion
- ! . I of grab grab samples samples during during 2003.
2003. .~ ~ ~
0c '
Surface'water,samples Surface'water,samples could could ~ot be'i~en :8t :8t :ACS'l~ation 2S7 2S7 from ,October 3~t 1011 from ,October 1011 through october through october 44 atat 0541 0541 due due to 'pMver failure~ Power'was to 'pMver Power'was restored restored to to the the sampler sampler on on October 4, October 4, 2003 2003 atat 0541.
0541. There There was was adequate adequate volume volume for for sample sample requirements.
requirements. The The ACS at ACS at monitoring monitoring location location 2S7 2S7 operated operated routinely routinely (as (as expected) expected) for for approximately approximately 99% of 99% of 2003.
2003.
Reasons Reasons for for exceptions exceptions to to REMP REMP air air sampling sampling during during 2003 2003 included included the the following:
following: loss loss of electrical of electrical power power to to air air sampling sampling stations stations and and air air sample sample equipment equipment problems problems (pump (pump malfunctions).
malfunctions). .
Electrical Electrical power power to to the the air air sampling stations at sampling stations at monitoring monitoring locations locations 3S2,3S2, 13S6, 13S6, 13S6Q, 13S6Q, 12S1, and 12S1, and 12El 12El was was interrupted interrupted for for about about 3-4 3-4 hours hours on'September on'September 19, 19, 2003, 2003, during during the the monitoring period monitoring period from from September September 17 17 through through September September 24,2003.
24,2003. There There was was aa wide wide area power area power outage outage during during the the referenced referenced time time period period duedue toto Tropical Tropical StormStorm Isabel.
Isabel.
Power was Power was restored restored to to the the airair sampling sampling equipment equipment and and adequate adequate sample sample volume volume was was achieved for achieved for thethe monitoring monitoring period.
period.
The sample pump The sample pump at at monitoring monitoring station station 12El 12El experienced experienced aa pump pump motor motor failure failure during during the monitoring the monitoring period period from from October October 1 1 through through October October 8,2003.
8,2003. Low Low sample sample volume volume was obtained was obtained during during the the sample sample periodperiod duedue to to the the pump pump motor motor failure.
failure. The The Air Air Sample Sample Pump was Pump was replaced.
replaced.
The sample The sample pump pump failed failed at at monitoring monitoring stationstation 6G6G 1 1 during during the the monitoring monitoring periodperiod from from June 44 through June through June June 11,11, 2003.
2003. Low Low sample sample volume volume was was obtained obtained during during thethe sample sample period due period due to to the the pump motor failure.
pump motor failure. The The Air Air Sample Sample Pump Pump was was replaced.
replaced.
Collectively, the Collectively, the air air sampling sampling equipment equipment at at the the sixsix air air monitoring locations operated monitoring locations operated routinely routinely (as (as expected) expected) for for more more than than 99%99% of of 2003 2003 in in spite spite of of the the exceptions noted exceptions noted above.
above.
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report F*3
II II Appendix F Appendix F Ambient Radiation Ambient Radiation Monitoring Monitoring EXceptions Occurred to EXceptions Occurred to the the monitoring monitoring of of ambient ambient radiation radiation during' during' the the second and second and fourth quarterly fourth quarterly monitoring monitoring periOds of 2003~ The periOds of The second second quarterly quarterly monitoring monitoring period period was April was April 29 29 through through July July 24,2003.
24,2003. The The TLD's at location' TLD's at location' 3S4 were wet 3S4 were wet and and unable unable to to process for process for the the referen~ed monitoring monitoring period.
period. The The fourth fourth quarterly quarterly monitoring monitoring period period was October was October 21, 21, 2003 2003 through through January January 30,2004.
30,2004. The TLD's at The TLD's at location location 14B3 14B3 were were wet wet and unable and unable to to process.
process. . . .
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report F4 F4
. J:
,I
. ; ~ ~'.
~ ,.
APPEN"pIX G" i"
i ",,
G" APPEN"pIX
.:; ) t
. " 1' . J ~ ;~ -' .,.
',. ** 1 f -.;~ : : ".' '": .':- "'.'" ~ ':' ;
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report -:
.I,.. . , .~
- G*l
I I AppendixG AppendixG The averages for The averages for indicator indicator and and control control locations locations reported reported in in the the Summary Summary of of Data Data Table, Table, which summarizes which summarizes the all measured all measured values, the entire values, when entire year's year's results when available, results for available, whether whether or the SSES for the or not SSES REMP, not they REMP, were they were were calculated were reported reported in calculated using in Appendix.
using Appendix. II
- "y tables. Values tables. Values belowbelow the the MDCs, MDCs, even even zeroes zeroes and and negatives, negatives, were were part part of the averaging of the averaging process for process for these these analysis analysis results.
results. When When no no measured measured results results areare available available in in these these cases, "LLO" cases, "LLO" is is reported.
reported.
Preferably, Preferably, the the averages averages reported reported in in the the Summary Summary of of Data Data table table forfor sample sample mediamedia that that are normally are normally collected collected continuously continuously are are determined determined using using onlyonly results results fromfrom continuously continuously collected samples.
collected samples. Occasionally, Occasionally, grab grab samples samples are are taken taken for for these these media media whenwhen equipment malfunctions equipment malfunctions or or other other anomalies anomalies preclude preclude or or otherwise otherwise perturbperturb routine routine continuous sampling.
continuous sampling. These These grabgrab samples samples are are taken taken to to minimize minimize the the time time periods periods when when no sampling no sampling is is being being performed, performed, or, or, inin some some instances, instances, when when continuous continuous sampling sampling is is considered to considered to be be nonrepresentative.
nonrepresentative.
Because grab Because grab samples samples are are snapshots snapshots of of the the media media over over brief brief periods, periods, it it is is preferable preferable not not to average the to average the analysis analysis results results of of these these samples samples with with those those forfor continuously continuously collectedcollected composite samples.
composite samples. However, However, when when equipment equipment malfunctions malfunctions are are protracted, protracted, relatively relatively large periods large periods of of time time could could be entirely unrepresented be entirely unrepresented by by averages averages if the results if the results from from grab grab sample analyses sample analyses are are not not considered.
considered.
Allowing analysis Allowing results for analysis results for grab grab samples samples to to be be weighted weighted equallyequally with with those those representing relatively representing relatively large large periods periods of of time time would would tend tend to to bias bias the the resulting resulting averages averages unjustifiably towards unjustifiably towards the the conditions conditions at at the the times times that that thethe grabs grabs areare obtained.
obtained. Averages Averages obtained in obtained in this this way way might might lessless accurately accurately reflect reflect thethe conditions conditions for for thethe combined combined period period of continuous of continuous sampling sampling and and grab grab simlpHng simlpHng than than ifif only only the results from the results from continuous continuous sampling were sampling were used.
used. OnOn thethe other other hand.
hand. using using weighting weighting factorsfactors for for the the analysis analysis results results of grab of grab samples samples derived derived fromfrom the the actual actual timetime itit takes takes to to collect collect those those samples samples would would lead to lead to the the grab grab sample sample analysis analysis results results having having aa negligible negligible effecteffect on on the the overall overall average average and not and not justifying justifying the the effort effort involved.
involved.
Grab samples collected Grab samples collected in in lieu lieu ofof normal normal continuous continuous sampling sampling are typically obtained are typically obtained at at regular intervals regular intervals corresponding corresponding to to the the intervals intervals (weekly)
(weekly) at at which which the the continuously continuously .
collected collected samples samples wouldwould usually usually be be retrieved retrieved for for eventual eventual compositing.
compositing. For For example.
example.
grab samples grab samples are are collected collected once once aa week week but but may may be be composited composited monthly monthly in in place place ofof continuously collected continuously collected samples samples that that would would normally normally be be retrieved retrieved weeklyweekly and and composited monthly.
composited monthly. Since Since each each grab grab sample sample is is used used to to represent represent an an entire entire week, week, albeit albeit imperfect, it imperfect, it is is reasonable reasonable to to weight weight the the analysis analysis results results thethe same.
same. Thus,Thus, the the results results ofof one weekly one weekly grabgrab areare given given approximately approximately one-fourth one-fourth the the weight weight of of the the results results forfor aa monthly composite monthly composite samplesample collected collected continuously continuously for for each each of of the the four four weeks weeks in in aa month. Similarly, month. Similarly, the the analysis analysis results results of of aa composite composite of of four four weekly weekly grab grab samples samples would would cany the cany the same same weight weight as as the the analysis analysis results results forfor aa composite composite of of four four weeks weeks of of continuously col1ected continuously col1ected sample.
sample.
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring ReportReport G*2
cc
SUMMARY
SUMMARY
OF TABLEG TABLEG C'C' OF DATA 1
1 DATA FORFOR SSF.SSSF.S
((
OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVlRONMENTAL ENVlRONMENTAL MONITORING MONITORING PROGRAM PROGRAM .1003 .1003 NAMEOFFACILITY: SUSQUEIIANNASTEAMELECTRICSTATION NAMEOFFACILITY: SUSQUEIIANNASTEAMELECTRICSTATION LOCATION OFFACIUTY:
LOCATION OFFACIUTY: LUZERNE LUZERNE COUNTY, COUNTY, PENNSYLV PENNSYLVANlA ANlA Reporting Period:
Reporting Period: December 30, December 30, 2001 2001 to to JJ mua" mua" 30, 30, 20042004 Paget ort',
Paget ort',
ANALYSIS AND ANALYSIS AND LOWERUMIT LOWERUMIT NUMBEROP NUMBEROP MnDIUMORPATIlWAY MnDIUMORPATIlWAY TOTAL NUMBER TOTAL NUMBER OF OF ALLINDICATOR ALLINDICATOR LOCATIONS LOCATIONS tocAllONwrmmGHBSTMllAN tocAllONwrmmGHBSTMllAN CONIROLLOCATION CONIROLLOCATION NONROUllNB NONROUllNB SAMPI..ED SAMPI..ED OFANALYSBS OFANALYSBS DBTl!CTION DBTl!CTION MllAN(3)
MllAN(3) NAME NAME MI!AN(3)
MI!AN(3) MBAN(3)
MBAN(3) REPOR'I1ID REPOR'I1ID (UNITOFMEASUREMENT) PHRFORMIID~ll (UNITOFMEASUREMENT) (llD)!22 (llD)!22 RANGll RANGll DISTANCE AND DISTANCE AND DIRECTION DIRECTION RANGll RANGll RANGE RANGE MBASUREMENTS!~
Amblmt Radiation Amblmt Radiation TLD TLD 333 333 2.02£+01 (301 2.02£+01 (301 1301) 9S2 9S2 4.06B+Ol 4.06B+Ol (4/4)
(4/4) 1.90£+01 (32/32) 1.90£+01 (32/32) 00 (mRlstd. qu.)
(mRlstd. qu.) (1.27£+01 **
(1.27£+01 4.47E+Ol) 4.47E+Ol) 0.2 0.2 mi mi S S (3.17£+01 (3.17£+01 -- 4.47£+01) 4.47£+01) (1.4tE+01 --
(1.4tE+01 2.36E+01) 2.36E+01)
Surface Water Surface Water OrossBeta OrossBeta 48 48 4 4 6.06B+OO 6.06B+OO (36/36)
(36/36) 2S7 2S7 1.t0E+OI 1.t0E+OI (12/12)
(12/12) 2.37E+OO 2.37E+OO (12/12)
(12/12) 00 (pCiIl)
(pCiIl) (2.42E+00 (2.42E+00 1.59£+01) 1.59£+01) 0.1 0.1 mi mi NNI!
NNI! (7.08£+00 (7.08£+00 1.59£+01) 1.59£+01) (6.08£.01 (6.08£.01 4.32£+00) 4.32£+00)
Tritium Tritium 48 48 2000 2000 1.57E+03 1.57E+03 (36/36)
(36/36) 2S7 2S7 4.42E+03 4.42E+03 (12/12)
(12/12) 3.18£+01 3.18£+01 (12' 12)
(12' 12) 00
(-3.54£+01
(-3.54£+01 1.66E+04) 1.66E+04) 0.1 0.1 mi mi NNI!
NNI! (1.13£+02 (1.13£+02 1.66E+04) 1.66E+04) (-4.98£+01
(-4.98£+01 1.37£+02) 1.37£+02)
Iodine-13 II Iodine-13 90 90 3.6SE-OI 3.6SE-OI (64 164) 2S7 2S7 7.7'7E-Ol 7.7'7E-Ol (26/26)
(26/26) 2.58£.01 2.58£.01 (26/26)
(26/26) 00
(-1.10£.01
(-1.10£.01 1.9tE+00) 1.9tE+00) 0.1 0.1 mi mi NNI!
NNI! (-1.10£.01
(-1.10£.01 1.91£+00) 1.91£+00) (-I.00E-02
(-I.00E-02 7.20£.(1) 7.20£.(1)
- ' .. ~" .... tl :",'j'l
, I.! - "'; " ~';-'. r\' r:,.. :' ;' ~, ~ 1. 1 " ":'Y': ;
OammaSpec OammaSpec ,,' :',
......... "1 r',"
K40' 48' (12112)
- JJ (
( , : -J \
K40' 48' 3.s8E~OOl (36/36)(36/36) 6SS 6SS 4.7SE+00 4.7SE+00 (12112) tiOB-Oi tiOB-Oi (12/12)
(12/12) 00
(-3.ooE+01
(-3.ooE+01 S.ooE+OI)
S.ooE+OI) 0.9:
0.9: mi mi ',:ESB:: (-2.40£+01'
',:ESB:: (-2.40£+01' 4.10£+01) 4.10£+01) (-1.70£+01
(-1.70£+01 ~
- 2.40E+OI) 2.40E+OI)
~ ~.
48
"" II l r*. '-. " ~ 0 '"
M:n:54
M:n:54 48 15' 15' .8.31E-02
.8.31E-02 (36/36)
(36/36) 6S6 6S6 tSSE-02' tSSE-02' (12/12) (12/12) 2.5SE-02 2.5SE-02 (i2/ll)
(i2/ll) 00
(-1.90E+00
(-1.90E+00 .. 1.50E+00) 1.50E+00) 0.8 0.8 mi" ESE mi" ESE (.I.ooE+OO
(.I.ooE+OO 2.IOE+OO) 2.IOE+OO) (.1.00£+00
(.1.00£+00 2.10£+00) 2.10£+00)
Co-58 Co-58 48 15 15 -2.0SE-Ol
-2.0SE-Ol (36/36)
(36/36) 6SS 6SS 1.83E-Ol 1.83E-Ol (12' 12)
(12' 12) .8.09£.01
.8.09£.01 (12/12)
(12/12) 00 48
(-3.300+00
(-3.300+00 3.60E+00) 3.60E+00) 0.9 0.9 mi mi ESE ESE (.2.40E+00
(.2.40E+00 2.50E+00) 2.50E+00) (*2.10£+00 2.00£.(1) 2.00£.(1)
Pc-59 48 30 1.49£-01 (36/36) 6SS 1.23£+00 (12/12) 4.85£.01 (12/12) 0 0
Pc-59 48 30 1.49£-01 (36/36) 6SS 1.23£+00 (12/12) 4.85£.01 (12/12)
(-6.00£+00
(-6.00£+00 4.70E+00) 4.70E+00) 0.9' 0.9' mi mi ESE ESE (.2.10E+00
(.2.10E+00 4.70E+00) 4.70E+00) (.1.40£+00 .... 5.80£+00) 5.80£+00)
<:0-60
<:0-60 48 48 15 15 2.96E-Ol 2.96E-Ol (36/36)
(36/36) 2S7 2S7 3.90£.01 3.90£.01 (12/12)
(12/12) 2.63£.01 2.63£.01 (12/12)
(12/12) 00
(-I.tOE+oo
(-I.tOE+oo -- 1.90E+00) 1.90E+00) 0.1 0.1 mi mi NNI!
NNI! (-8.00£-01
(-8.00£-01 -- 1.90£+00) 1.90£+00) (-8.00£.01
(-8.00£.01 3.00£+00) 3.00£+00)
Zn-6S Zn-6S 48 48 30 30 -4,8iMI (36/36)
-4,8iMI (36/36) 6SS 6SS 7,92.E-OI (12/12) 7,92.E-OI (12/12) .2.91£.01
.2.91£.01 (12/12)
(12/12) 0 0
(-1.07E+Ol
(-1.07E+Ol 7.70£+00) 7.70£+00) 0.9 0.9 mi mi ESE ESE (-5.50£+00 ..
(-5.50£+00 6.00E+00) 6.00E+00) (-4.40£+00 *7.00£+00)
.. ~.
"0#' t . 't "0 ~ \! ' '. '.',1
TABLEG TABLEG
SUMMARY
OFDATAFORSSES
SUMMARY
OFDATAFORSSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORlNGMONITORlNG PROGRAM* 2003 2003 NAMEOFFAClUTY: SUSQUEIIANNASTEAMELECTRlCSTATION NAMEOFFAClUTY: SUSQUEIIANNASTEAMELECTRlCSTATION LOCATION OFFACIUTY:
LOCATION OFFACIUTY: LUZERNE COUNTY, PENNSYLVANIA LUZERNE COUNTY, PENNSYLVANIA Reporting Period:
Reporting Period: December 30, December 30, 2002 2002 to to January 30, January 30, 2004 2004 Pa,c%o(13 Pa,c%o(13 ANALYSIS AND ANALYSIS AND LOWERI1MlT LOWERI1MlT NUMBER OF NUMBER OF MEDIUM OR PA11lWAY MEDIUM OR PA11lWAY TOfALNUMBER TOfALNUMBER OF OF ALL INDICATOR ALL INDICATOR LOCATIONS LOCATIONS LOCATIONwrrnmGllP.ST LOCATIONwrrnmGllP.ST MIlANMIlAN CONTROLl.OCATION CONTROLl.OCATION NONROtmNB NONROtmNB SAMPI.lID SAMPI.lID OFANALYSBS OFANALYSBS DB1'ECTION DB1'ECTION MIlAN(3}
MIlAN(3} NAME NAME M.EAN(3}
M.EAN(3} M.EAN(3)
M.EAN(3) REPORTP.D REPORTP.D OFMRAS\lRE.}.i\1Nr) PERFORMED
~UNIT OFMRAS\lRE.}.i\1Nr) PERFORMED !l}
!l} !Ul>lPl
!Ul>lPl RANGB RANGB DISI'ANCB DISI' ANCB AND AND DlRF..cI1ON DlRF..cI1ON RANGE RANGE RANGB RANGB MBASURBMl!NTS~4l Sud ace WJlter Sudace WJlter (oonL)
(oonL) Zr*9S 48 48 30 30 -6.20E-Ol (36/36)
-6.20E-Ol (36/36) 6SS 6SS (12/12)
- 2.92&01 (12/12) 4.02&01 (12/12) 4.02&01 (12/12) 0 0
(pCiIl)
(pCiIl) (oS.80B+00 (oS.80B+00 - 3.70B+00) 3.70B+00) (9.ooE-OI (9.ooE-OI mi mi ES£ ES£ (-2.90£+00 1.70£+00) 1.70£+00) -(3.00£+00
-(3.00£+00 1.50£+00) 1.50£+00)
Nb-9S 48 48 15 15 -S.60R-02 (36/36)
-S.60R-02 (36/36) 686 686 2.96R-Ol (12/12) 2.96R-Ol (12/12) 2.96R-Ol (12/12) 2.96R-Ol (12/12) 0 0
(-3.~0£+OO .; 3.40£+00) 3.40£+00) (S.ooE-Ol (S.ooE-Ol mi mi RSE RSE (-2.2OR+00
(-2.2OR+00 -- 4.40£+00) 4.40£+00) -(2.2OR+00
-(2.2OR+00 - 4.40£+00) 4.40£+00)
C&-134 C&-134 48 48 IS IS 3.83R-Ol (36/36) 3.83R-Ol (36/36) 2S1 2S1 4.73E-Ol (12/12) 4.73E-Ol (12/12) 3.13E-Ol 3.13E-Ol (12/12)
(12/12) 0 0
(-1.70£+00
(-1.70£+00 - 2.80£+00) 2.80£+00) (l.ooE-Ol (l.ooE-Ol mi mi NNE NNE (*9.00E-Ol -- 1.40E+00) 1.40E+00) -(2.10R-Ol
-(2.10R-Ol I.5OR+OO)
I.5OR+OO) c&-131 c&-131 48 48 18 18 (36/36)
S.97R-02 (36/36) LTAW LTAW 6.08E-OI (12/12) 6.08E-OI (12/12) 4.50R-OI (12/12) 4.50R-OI (12/12) 0 0
(-1.40£+00
(-1.40£+00 - 3.70£+00) 3.70£+00) on site on site NE-RS£ NE-RS£ (-1.20B+00
(-1.20B+00 -- 3.1OR+00) 3.1OR+00) -(1.60£+00
-(1.60£+00 . 4.70E-(1) 4.70E-(1)
Ba*140 48 48 60 60 8.91E-Ol (36/36) 8.91E-Ol (36/36) LTAW LTAW 1.36£+00 (12/12) 1.36£+00 (12/12) (12/12)
- 2.S4E-OI (12/12) 0 0
(-3.40£+00
(-3.40£+00 . 5.70£+00) 5.70£+00) on site on site NE-RSB NE-RSB (-1.50B+OO
(-1.50B+OO . 5.10B+00) 5.10B+00) -(5.00£+00 -- 2.7OR+OO) 2.7OR+OO)
La*140 48 48 15 15 1.03B+OO (36/36) 1.03B+OO (36/36) LTAW LTAW 1.57B+00 (12/12) 1.57B+00 (12/12) .2.81R-OI (12/12)
(12/12) 0 0
(-3.90B+00
(-3.90B+00 - 6.50B+00) 6.50B+00) on site on site NE-ES£ NE-ES£ (*1.80E+OO -- 6.5OR+00) 6.5OR+00) -(5.80£+00 . 3.1OR+00) 3.1OR+00) c: (
('
(' c'c' TABLEG TABLEG
((
SUMMARY
SUMMARY
OF OF DATA DATA FOR FOR SSES SSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MOmTORING MOmTORING PROGRAM* 2003 2003 NAME OF NAME OF FACILITY:
FACILITY: SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECTRIC ELECTRIC STATION STATION LOCATION OF LOCATION OF FACILITY:
FACILITY: LUZERNE LUZERNE COUNTY.
COUNTY. PENNSYLVANIA PENNSYLVANIA Reporting Period:
Reporting Period: December 30, December 30, 2001 2001 to to January 30,2004 January 30,2004 Page30ftl Page30ftl ANALYsts AND ANALYsts AND LOWERUMlT LOWERUMlT NUMBBROF NUMBBROF MEDlUMORPATIlWAY MEDlUMORPATIlWAY TOrALNUMBER TOrALNUMBER OF OF AlL INDICATOR AlL INDICATOR LOCATIONS LOCATIONS LOCATIONwmUI[OUESTMEAN LOCATIONwmUI[OUESTMEAN CONIROLLOCATION CONIROLLOCATION NONROUI'INB NONROUI'INB SAMPLED SAMPLED OF ANALYSES OF ANALYSES DETECTION DETECTION Ml!AN(3)
Ml!AN(3) NAME NAME MEAN (3)
MEAN (3) MEAN (3)
MEAN (3) REPORTED REPORTED OF MBAStJREMENT) RANOB DISTANCB AND DIRECTION DIRECTION RANOB RANOB
~UNlT OF PI!RFORMI!D ~ll MBAStJREMENT) PI!RFORMI!D (U.Dl~2~ RANOB DISTANCB AND RANOB RANOB MBAS1.lRBMBNl'S'~
Potable Water Potable Water OrossAlpha OrossAlpha 12 12 1.69E*OI (12/12)
(12/12) 12H2 12H2 t.69B-OI (12/12) t.69B-OI (12/12) Only indicator Only indicator 00 (pCiIl)
(pCiIl) (*6.S4E*Ol . t.37E+OO) t.37E+OO) 26 26 ml ml wsw wsw (-6.S4B-01
(-6.S4B-01 -- l.37E+OO) l.37E+OO) stations sampled stations sampled for this medium.
this medium.
for OrossBeta OrossBeta 12 12 44 2.26E+OO (12/12) 12112 12112 2.26E+OO (t2/12) 00 (8.98B-01 - 4.26E+OO) 26 26 ml WSW ml WSW (8.98B-Ol - 4.26E+OO)
Iodine-13 II Iodine-13 26 26 1.78E*Ol 0.(/26) 12H2 12H2 1.7gB-Ol 0.(/26) 0 0
(.1.60B-Ol - S.SOE*OI) 26 26 ml WSW ml WSW (-1.60B-Ot - S.SOE*OI)
Tritium Tritium 12 12 2000 2000 6.43B+OI (12/12) 12H2 12H2 6.43B+Ol (12/12) 00
(-7.67E+OO l.93B+02) 26 26 ml WSW ml WSW (*7.67E+OO l.93B+02)
OammaSpec OammaSpec K-40 K-40 12 12 4.04E+OO. (12112). 12H2 12H2 .. ': ~ 4.04E+OO* (12112) : '; 00
(*2.00E+Ol ~ . 4.IOB+0l) 26'"
26'" ml WSW ml WSW (.2.00B+Ot: .", 4.10B+Ol)
Mn-S4 Mn-S4 12 12 IS IS *S.36E*02 (12/12) " I 12H2 12H2 *S.36E*02 (12112)' " .
00
(*1.40E+OO *. 9.00E*Ol) 26 '
26 ml WSW ml WSW (.1.40E+OO 9.00B-Ol)
Co-S8 12 12 IS IS -4.26E-Ol (12/12) 12112 12112 -4,26E-OI (12/12) 00
. WSW .. 6.00B-Ol) 26 ml WSW
(-1.20B+OO 6.00E*Ol) 26 ml (.1.20B+OO F~S9 12 12 30 30 -3.69B-Ol (12/12) 12112 12112 -3.69E-0l (12/12) 00
(*3.60B+OO - 3.00B+OO) 26 26 ml WSW ml WSW (*3.6OE+OO . 3.00B+OO)
Co-60 Co-60 12 12 IS I.SSB*OI (12112) 12U2 12U2 USB*Ol (12/12) 00
(-7.00B-Ol - ,8.00B*Ot) 26 26 ml WSW ml WSW (.7.00E*OI ., 8.00B*Ol)
Zn-6S
, Zn-6S 12 12 30 30 --1.21E+OO . (12 112) , 12H2 12H2 -t.21E+OO (12/12) 00
(.9.80E+OO "- ,6.IOB+OO) 26 26 ml WSW ml WSW (*9.S0B+OO - 6.10B+OO)
Zr*9S 12
. 12 " 30 . , _-S.llB-OI . (12/12) ,
30 t2H2 t2H2 -S.nE*Ot (12112) 00
(-2.60B+OO - 4,OOB-Ol) 26 26 ml WSW ml WSW (*2.60B+OO - 4.00B-Ol)
TABLEG TABLEG
SUMMARY
SUMMARY
OF OF DATA DATA FORSSES FORSSES OPERATIONAL RADIOLOGICAL OPERATIONAL .ENVIRONMENTAL MONITOlUNG RADIOLOGICAL .ENVIRONMENTAL MONITOlUNG PROGRAM* Z003 Z003 NAME OF NAME OF FACILITY:
FACILITY: SUSQUHlIANNA SUSQUHlIANNA STRAMSTRAM ELECTlUC ELECTlUC STATION STATION LOCATION OF LOCATION OF FACILITY:
FACILITY: LUZERNE LUZERNE COUNTY, COUNTY, PENNSYLVANIA PENNSYLVANIA Reporting Period:
Reporting Period: December JO.
December JO. 1002 1002 to to January 30,lOO4 January 30,lOO4 Page40flJ Page40flJ ANALYSIS AND ANALYSIS AND LO'WERUMlT LO'WERUMlT NUMBBROP NUMBBROP MEDIUM MEDIUM OROR PAllIWAY PAllIWAY TOrALNUMBBR TOrALNUMBBR OF OF AlLlNDlCATOR LOCATIONS AlLlNDlCATOR LOCATIONS LOCATION WmUIIGIIBSr LOCATION WmUIIGIIBSr MEAN MEAN CONfROLLOCATION CONfROLLOCATION NONROUTINB NONROUTINB SAMPLED SAMPLED OFANALYSBS OFANALYSBS DBI'ECllON DBI'ECllON MBAN(3)
MBAN(3) NA:b.tn NA:b.tn MEAN (3)
MEAN (3) ME.AN(3)
ME.AN(3) lU!PORIED lU!PORIED
~UNITOPMBASURHMt!NT) Pl!RFORMED~il !UD~~l! RANGE RANGE DlSTANCB DlST ANCB AND AND DlRECl10N DlRECl10N RANGE RANGE RANGE RANGE MEASURJl.MBNTS(4!
MEASURJl.MBNTS(4!
Potable Water (con) Nb-9S 12 IS 1.8SE-OI (12/12) 12H2 1.8SE-Ol (12/12) Onlyindk:ator 0 (pCiIl) (-I.IOE+OO - 1.IOE+(0) 26 mi WSW (-I.IOE+OO - I. 1OE+OO) stations sampled for this medium.
Cs-I34 12 15 9.23E..Q2 (12/12) 12112 9.23E-02 (12/12) 0
(-S.70B-Ol - I.ZOE+OO) 26 mi WSW (-S.70E-Ol 1.20E+(0)
Cs-137 12 18 -1.4IE-Ol (12/12) 12112 -1.41E-Ol (12/12) 0
(-2.40B+00 - 1.60E+(0) 26 mi WSW (-2.40E+00 - . 1.60E+(0)
Ba-140 12 60 3.OSE-Ot (12 I 12) 12H2 3.0SE-Ol (12/12) 0
(-2.80E+00 . 7.20E+(0) 26 mi WSW (-2.80E+00 - 7.20E+(0)
La-140 12 15 3.72E-DI (12/12) 12H2 3.72E-0l (12/12) 0
(-3.20B+00 - 8.30E+(0) 26 mi WSW (-3.20E+00 - 8.30E+00)
((
cc TABLEG TABLEG
SUMMARY
SUMMARY
OF OF DATA DATA FORFOR SSES SSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORING MONITORING PROGRAM. 2003 2003 NAl\m OF NAl\m OF FACILITY:
FACILITY: SUSQUEHANNASUSQUEHANNA STEAM STEAM ELECTRICELECTRIC STATION STATION LOCATION OF LOCATION OF FACILITY:
FACILITY: LUZERNELUZERNE COUNTY, COUNTY, PENNsYLVANIA PENNsYLVANIA Reporting Period:
Reporting Period: , D<<ember 30, D<<ember 30, 2002 2002 to to January 30,1004 January 30,1004 PageSor13 PageSor13 ANALysts AND ANALysts AND LOWERUMIT LOWERUMIT , , NUMBBROF NUMBBROF MEDIUM ORPATIIWAY TOTAL MEDIUM ORPATIIWAY NUMBER TOTAL NUMBER OF OF AlL INDICATOR AlL INDICATOR LOCATIONS LOCATIONS LOCATIONWrll1InGlmsTMEAN LOCATIONWrll1InGlmsTMEAN CONI'ROLLOCATION CONI'ROLLOCATION NONROUI1NB NONROUI1NB SAMPLED SAMPLED OF ANALYSES OF ANALYSES DETEcrrON DETEcrrON MBAN(3)
MBAN(3) NAMP;'
NAMP;' MEAN (3)
MEAN (3) MEAN (3)
MEAN (3) REl'ORTIID REl'ORTIID
~UNIT OFMBAS'UREMi!.Nn OFMBAS'UREMi!.Nn PERFORMED PERFORMED [tl [tl (Ul)~~1~ RANGB RANGB DTSTANCB AND DTSTANCB AND nnmcrrON, nnmcrrON, RANGB RANGB RANGB RANGB ' MBAStJRBMP.NTS~
Fish Fish OammaSpec -,
(pCi/kg wet) K-40 13 3.S8E+03 \1/7) LTAW 3.67B+03 (I II) , 3.16E+03 (6/6) 0 (1.30E+D3
. 4.~9E+03) on site NE*ESE (3.67B+?3. - 3.67B+03) (1.30E+03 - 3.92E+03)
Mn-S4 13 130 1.9SE+00 (1/7) LTAW S.74E+00 (t / t) 3.ISE+00 (616) , .0
(.9.19E+OO , - 9.69E+OO) on site NE*ESE (S.74E+00 - 5.74E+00) (.6.18E+00 - I.34E+Ol)
Co-5S 13 130 *t.67B+00.. \1/7) LTAW *9.80E-Ot (11 I) *2.S3E+00 (6/6) 0
(-9.09E+OO'* * ,6.3.~+(6)
.. i -~ ~
on site NE-EsE (.9.~OE~?1 . \'
" .9.~OE.OI)
(-6.l4E+00* * . t.2lE+OO)
Fe-59 13 260 *9.S1E+00 \1 /7) LTAW t06E+OI. (Ill)! ;., " ; -1.6~+00. (616).;, 0
(-4.40B+of" * : I.S7E+Ot)' onsitC NE-ESE (I.06E+Ol " * ,"~.1.000+Ot) (.2.84E+Ot /' * '2 l.88E+OI)
, ~..... '. -
- :~r*~'~' '
Co-60 13 t30 -1.S9B+00 \1 /7) .. , " 211 " -'-.
1.31E*Ot (6/6),., , 1.31E-OI ,; (616) . 0
(-7.97E+oO: - , 4.40B.f.00), 30 m1 NNE (.8.69E+00, - ' 9.99E+OO) (.8.69E+OO,; - '" 9.99E+00)
, . .. .,';.", * 'j zn.6S 13 260 -3.99E+OI \1/7) 211 ., -3.26E+00 (616) ." "I ** *3.26E+00 . (616) : " . .. 0
(.S.6mtOl'; - 2.8SE+00) 30 m1 NNE (*2.9SB+Ot - 9.28E+00) (.2.9sE+01 . - ! " 9.28E+00)
Zr*9S 13 1.68E*Dl (1/7) 21I 3.B4E+OO (616) 3.B4E+OO (616) 0
('l.SOB+O~ , . , ~.36E+Dt)* 3D mi NNE (*3.2SE+00 - 1.38B+Ol) (*3.2SE+00 1.38E+Ot)
Nb-9S 13 O.OOE+OO (1/7) 2H O.OOE+OO (616) O.ooE+OO (616) 0 (O.OOE+oo*' . O.OOE+OO) 30 mi NNE (O.OOE+OO - O.OOE+OO) (O.OOE+OO - O.OOE+OO)
Cs*l34 130 *1.86E+Ol (117) LTAW 3.39E+OO . (Ill) *l.47B+Dl (616) , 0 13
(-4.3SB+0~ - 3.39E+OO) on site NE*ESE (3.39E+OO . 3.39B+OO) (*6.66E+OI .. 1.19E+OO)
Cs-137 13 ISO 4.S3E+00 \1/7) IND S.I9E+OO (616) -t.78E+00 (616) 0
(*7.78B*Ot - -, J.22E+Ol) . 0.9-1.4, ' -mi ESE (-7.7m*OJ - 1.22E+Ol) (.8.29E+00 - 3.14E+OO)
Ba-140 13 4.8SE+Ol \1/7). " , LTAW " 1.S0B+02 ' (I 11) *3.49E+Ot (616) , 0
,,(.S.44E+Ol " ';. 1.8SE+02) on site NE*ESE (J.SOE+02
- T __ * ~_ ~ .. _ .. ~ -
- I.S0E+02) (.2.26E";.02 - 4.39E+Ol)
La*140 13 *6.S7B+00 \1/7) IND. *6.2SB+00 (616) *7.2SE+OO (616) 0
(-S.2SE+Dl. - 3.3lE+Ol), ,. 0.9-1.4 mi ESB (*S.2SE+Ot 3.31E+0l) (-1.94E+Ol - 7A2E*Dt)
.. .~ ~ , ;" -: . .. , .
)'
0*7
TABLEG TABLEG
SUMMARY
SUMMARY
OF OF DATA DATA FOR FOR SSES SSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVlROl'tl'MENTAL ENVlROl'tl'MENTAL MONITORING MONITORING PROGRAM *2003 NAMEOFFAClLlTY:
NAMEOFFAClLlTY: SUSQUEllANNASTEAMELECTRlCSTATION SUSQUEllANNASTEAMELECTRlCSTATION LOCATIONOFFACILlTY: LUZERNECOUNTY,PENNSYLVA.NIA LOCATIONOFFACILlTY: LUZERNECOUNTY,PENNSYLVA.NIA Reporting Reporting Period:
Period: De~er3O,2002 to to 30, 2004 JanlUll)' 30, JanlUll)' 2004 Page 6 Page 6 of of 13 13 ANALYSIS AND ANALYSIS AND LOWER IDUT LOWER IDUT NUMBnROF NUMBnROF MEDIUM ORPAnlWAY MEDIUM ORPAnlWAY TOfALMJMBER TOfALMJMBER OF OF A1J.INDJCATOR LOCATIONS A1J.INDJCATOR LOCATIONS LOCATION WmUIIGUBST LOCATION WmUIIGUBST MEAN MEAN CONIROLLOCATION CONIROLLOCATION NONROUllNB NONROUllNB SAMl'lllD SAMl'lllD OFANALYSns DlITBCTION OFANALYSns DlITBCTION MEAN (3)
MEAN (3) NAME NAME MEAN (3)
MEAN (3) MEAN (3)
MEAN (3) RBPORTED RBPORTED lUNlTOPMBASUREMENr) PERFORMED!I}
lUNlTOPMBASUREMENr) PERFORMED!I} ~UDH2! RANGE RANGE DISTANCE AND DISTANCE AND DlRBC110N DlRBC110N RANGB RANGB RANGB RANGB Ml!A<;UREMEN1'SS!"2 Ml!A<;UREMEN1' !"2 Sediment Sediment Gamma Spec (pCiIkg dry)
(pCiIkg Be-1 8 3.30E+02 (6/6) 12P 6.99E+02 (2/2) 2.91E+02 (2/2) 0
(-2.53E+Ol
- 7.26E+02) 6.9 mi WSW (6.7IE+02
- 1.268+02) (2.58E+02
- 3.25E+02)
K-40 8 1.318+04 (6/6) LTAW 1.528+04 (2/2) 1.23E+04 (2/2) 0 (1.04E+04
- 1.58E+04) ons.iJ.c NE-ESI! (1.47E+04
- 1.58E+04) (1.23E+03
- 1.73E+04)
Mn-54 8 9.58E+00 (6/6) LTAW 1.368+01 (2/2) 3.11E+00 (2/2) 0 (1.78E+00 - 2.55E+OI) onsile NE*ESE (1.78E+00
- 2.55E+Ol) (-3.54E+00 . - 9:7SE+00)
Co-58 8 *l.07E+Ol (6/6) 12P *1.79E-Ol (212) *1.94E+Ol (2/2) 0
(-2.57E+Ol
- 2.4IE+00) 6.9 mi WSW (1.78E+00
- 2.4IE+00) (-2.828+01 * -1.05E+Ol)
Fe-59 8 -6.29E+00 (6/6) 2B 2.58E+Ol (2/2) 2.58E+Ol (2/2) 0
(-2.98E+Ol - 4.928+01) 1.6 mi NNE (2.3IE+00
- 4.928+01) (2.31E+00
- 4.928+01)
Co-60 8 4.578+00 (6/6) 78 7.79B+00 (2/2) .2.50E+00 (2/2) 0
(-9.06E+00 - 1.128+01) 1.2 mi SE (4.428+00 1.128+01) (-1.2OE+Ol
- 7.04E+00)
Zn-6S 8 7.53E+00 (6/6) LTAW 2.57E+Ol (2/2) *3.328+01 (2/2) 0
(*2.05B+Ol - 4.05B+Ol) ons.iJ.c NE-ESB (1.08B:,:01
- 4.05E+01) (-6.23E+Ol * -4.07E+OO)
Zr-95 8 1.95E+Ol (6/6) 78 3.60E+Ol (2/2) 1.38B+Ol (2/2) 0 (1.20E+00
- 4.37E+Ol) 1.2 mi SE (2.83E+Ol
- 4.37E+Ol) (5.34E+OO - 2.228+01)
Nb-95 8 0.008+00 (6/6) 2B O.ooE+oo (2/2) O.ooE+oo (2/2) 0 (O.ooE+oo
- O.OOE+OO) 1.6 mi NNE (0.008+00
- O.ooE+OO) (O.OOE+OO
- O.OOE+OO)
Cs-l34 8 150 -2.28E+oo (6/6) LTAW 4.96E+00 (2/2) -6.59E+00 (2/2) 0
(-8.528+00
- 7.96B+OO) onsile NE*ESE (1.978+00
- 7.96E+00) (-l.07E+Ol * .2.538+00)
Cs-137 8 180 5.2OE+Ol (6/6) 78 8.928+01 (2/2) 7.56E+01 (2/2) 0 (6.91E+00 - l.ooE+02) 1.2 mi SE (7.8 1E+0 1 l.ooE+02) (4. 14E+Ol 1.IOE+02)
Ba*l40 8 -2.30E+Ol (6/6) 12F -4.68E+00 (2/2) -4.79E+Ol (2/2) 0
(*9.928+01
- 7.40E+Ol) 6.9 mi WSW (.7. llE+OO * *2.25E+oo) (*I.IOE+02 1.428+01)
cc c'c',,
TABLEG TABLEG
((
SUMMARY
SUMMARY
OF OF DATA DATA FOR FOR SSES SSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORING MONITORING PROGRAM *2003 NAME OF NAME OF FACILITY:
FACILITY: SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECTRIC ELECTRIC STATION STATION LOCATION OF LOCATION OF FACILITY:
FACILITY: LUZERNE LUZERNE COUNTY, COUNTY, PENNSYLVANIA PENNSYLVANIA Reporting Perlo!l:
Reporting Perlo!l: December 3D, December 3D, 2002 2002 to to January 30, January 30, 2004 2004 Page 7 Page 7 or or 13 13 ANALYSIS AND ANALYSIS LOWERUMIT AND LOWERUMIT NUMBER OF NUMBER OF MEDWMORPAntWAY MEDWMORPAntWAY Tal'ALNUMBER Tal'ALNUMBER OF OF AlL INDICATORLOCAlIONS AlL INDICATORLOCAlIONS LOCAlIONWITHInGIIESTMBAN LOCAlIONWITHInGIIESTMBAN CONTROLLOCAlION CONTROLLOCAlION NONROUI'INB NONROUI'INB SAMPLED SAMPLED OF ANALYSES OF ANALYSES DETECITON DETECITON MBAN(3)
MBAN(3) NMm NMm MEAN (3)
MEAN (3) MBAN(3)
MBAN(3) REl'OR11ID REl'OR11ID roNIT DFMEASUREMl!N'I1 PI!RFORMED roNIT DFMEASUREMl!N'I1 PI!RFORMED ~tl ~l(2! RANGB RANGB DISTANCB AND DISTANCB AND DJRl!C1l0N DJRl!C1l0N KANGB KANGB KANGB KANGB MJ!ASUREMF.NTS~~
Sediment (COI1l) La-140 8 -9.83E+00 (6/6) 7B 2.81E+OI (2/2) 1.91E+Ot (2 J 2) 0 (pCi/kg dry) (-9.79HtOl '
",
- 4.89E+Ol) 1.2 mi SE (7.3SE+00 - 4.89E+Ol) (1.78E+01 . 2.0SE+01)
';"1 ,t "
Ra-226 8 2.27E+03 (6/6) 7D 2.6tE+03 (2/2) t.60E+03 . (212) 0 (1.96E+03',
- 2. 86E.f.03) 1.2 mi SE (2.36E+03 . 2.86E+03) (7.S0E+02, . 2.4SE+03)
Th-228 8 3.21E+03 (6/6) 7D 3.SIE+03 (2/2) 3.01E+03 (2/2) 0 (2.46E+03
- 3.S6E+03) 1.2 mi SE (3.47E+03 - 3,S6E+03) (1.28E+D,3 - 4.74E+03)
, Ground Water 'Oammaspec (PC:III) , K-40' , 36 -l.SSE+oo (24/24) 252 2.49E+00 (12/12) 2.33E+OO (12/12) 0 t....I, * .
(-5.100+011
~ 'j. '-;;;',
,..-;- "j -
2.70E+OI)
O.9~ mi"'NNE: (-1.9OE+OI ;\!. '2.70E+Ol) *:"*(-3.30E:tOl f'* - 5.3oE+Olj',:'.'l I:' :' .-.-..' ".. ':"~ :;~~ .:~ \ ~~ ~/"~,\
" ~
, 1Mn:.S4 :36 15 -1.18E*0t' (24/24) lID 1.92E*01 (12/12) l.92E-Ol (12/12) 0
(-2.90E+oo
- 2.10E+OO), 5.2: mi WSW: (.1.40Efoo ;, ,* '2.00EfOO) (-1.40E+oif'.' 2.ooE+OO)':: ,
! ,-, : ~: .. ~: .. - '. -.
~,. " _. I
'" ~ ( *
\
. ,\,-
'~"
!C0:58 36 IS -1.57E-Ol' (24/24) 12F3 -5.ooE-02 (12/12) *5.ooE-02 (12/12) 0
(-2.70E+00
- t.70E+OO) 5.2" mi WSW:; (-1.70E+00 1.200+00) (-1.70E+00 1.20E+OO)' ' :
Fe-59 36 30 S.B3E-OI (24'/24) 252 6.42E-OI (12112) 3.7SE-Ol (12/12) 0
(-S.30E+00 - 6.10E+00) 0.9 mi NNE (*S.30E+00 . 6.10Efoo) . (-4.20E+00
- 8.50E+00)
Co-60 36 15 *t:2BE-01 (24/24) 4S4 3.33E*02 (12/12) *1.0BE*01 (12/12) 0 i
(*2.40E+00 - 2.ooE+OO) 0.5 mi ENE (.I.S0E+00 2.ooE+OO) (-2.BOE+oo
- 1.9OE+OO) , .
Zn-6S 36 30 -1.32E+oO (24/24) 4S4 -1.20E+00 '(12/12) -4.43E+00 (12/12) 0
(*9.40E+00
- 8.S0E+OO) 0.5 mi ENE (*9.40E+OO - 8.500+00) (-2.BOE+oo ' . 2.80E+OO)
, Zr*9S 36 30 -6.54E-OI (24"24) 12F3' 1.1sE+oo '(12/12) 1.1SE+00 '(12/12) 0
(-S.70E+00 - '3.30Efoo) 5.2 mi WSW (-2.70E+00 - 5.40E+00) (-2.70E+00 - 5.400+00)
Nb-9S '36 is ~2.46E-02 '(24124), : 4S4 3.83E-Ol (l~ 112) .2.42E-01 (12112) 0
(-2.90Efoo
. ~- '- -- .
- 3.ooE+OOj
~. *... , .. ,
0.5 mi ENE (-2.70E+00 - . 3.ooE+00) (-2.40E+00
- 2.10E+00)
Cs-l34 36 15 1.74E-Ol (24/24) 4S4, ' 4.42E-Ol (12/12) -3.67E-Ot (12 112) 0
(.2.40E+00
- 2.80E+OO) 0.5 ' mi ENE (-9.ooE-OI' , ,2.80E+00) (*1.70E+00 1.20E+00)
, . "w.'
().IJ
TABLEG TABLEG
SUMMARY
SUMMARY
OF OF DATA DATA FORFOR SSES SSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORING MONITORING PROGRAM* 2003 2003 NAME OF NAME OF FACILITY:
FACILITY: SUSQUEIIANNA SUSQUEIIANNA STEAM STEAM ELECTRIC ELECTRIC STATION STATION LOCATION OF LOCATION OF FACILITY:
FACILITY: LUZERNE LUZERNE COUNTY, COUNTY, PENNSYLVANIA PENNSYLVANIA Reporting Period:
Reporting Period: December 30. 2002 December 30. 2002 to to JJ anulll')' 30. 2004 anulll')' 30. 2004 Page 8 Page or 13 8 or 13 ANALYSIS AND ANALYSIS AND LOWERUMIT LOWERUMIT NUMBER OF NUMBER OF MEDIUM MEDIUM OR OR PATIlWAY PATIlWAY TOTAL NUMBER TOTAL NUMBER OF OF INDICATOR LOCAnONS AU. INDICATOR AU. LOCAnONS LOCAnON WmllllGllEST LOCAnON WmllllGllEST MEAN MEAN CONTROL LqCAnON CONTROL LqCAnON NONROUT1NE NONROUT1NE SAMPLED SAMPLED OF ANALYSES OF ANALYSES DETECI10N DETECI10N MEAN (3)
MEAN (3) NAME NAME MEAN (3)
MEAN (3) MEAN(l}
MEAN(l} REFORTfl>
REFORTfl>
OF MEASUREMENTI
~UNIT OF PERroRMED ~1 ~
MEASUREMENTI PERroRMED (LlDl!2~ RANGB RANGB DISTANCE AND DISTANCE AND DmECTION DmECTION RANGE RANGE RANGB RANGB MEASUREMENTS!41 MEASUREMENTS!41 Ground Water (COOl) Cs*137 36 18 -1.28B-OI (24/24) 252 -1.14B-OI (12/12) -3.75&01 (12/12) 0 (pCi/I) (-1.70E+OO 1.40E+OO) 0.9 mi NNE (*1.70E-+OO - 1.40E+oo) (-2.20E-tOO
- I.20E-+OO)
Ba440 36 60 *2.67B-Ol (24/24) 454 6.08B-Ol (12/12) t.08B-OI (12/12) 0
(*5.20B+OO 3.ooE+OO) 05 mi ENE (-1.80E+OO - 2.60B-+OO) (-4.80E+OO
- 5.IOE-tOO)
La-I40 36 IS -2.96B-Ol (24/24) 454 7.ooB-OI (12/12) I.2SB-OI (12/12) 0
(-6.ooE+OO 3.40B+OO) 05 mi ENB (*2.10B-+OO
- 3.ooE-tOO) (*550E-+OO
- S.80E-tOO)
H*3 36 2000 5.44B+OI (24/24) 454 8.43E+Ol (12/12) 1.74E+Ol (12/12) 0
(-6.74B+Ol 1.93E+(2) 05 mi ENE (*2.46E-tOO
- 1.93E+(2) . (-8.84B+OI
- 8.86B+Ol)
Air Particulates Gross Beta 312 10 I.46E+Ol (208 I 208) 3S2 1.51E+OI (52/53) l.34B+Ol (104 I 104) 0 (E*03 pCi/ml) (359E+OO
- 3.17E+Ol) 05 mi NE (5.30E+Ol
- 4.91E-tOO) (3.16E+OO
- 3.10E+Ol)
Air Iodine 1-131 312 70 6.01B-04 (208 1208) 3S2 8.29B-04 (52/52) -6.44E-OS (104 1104) 0 (B-03 pCi/m3) (*S.27B-03
- S.97B-03) 05 mi NB (S.20B+OI * .2.79B-OJ) (.3.74B-OJ
- 6.30B-OJ)
Air Particulates GammaSpcc Quarterly Composite Be-7 24 9.06E+Ol (16/16) 1251 9.10B+OI (4/4) 8.2 1E+OI (8/8) 0 (E-03 pCilml) (6.70E+Ol 1.11B+(2) 0.4 mi WSW (7.6SB+Ol 1.06E+(2) (6.63B+Ol :- 9.34E+OI)
K-40 24 1.29B-+OO (16/16) 3S2 2.2IB-+OO (4/4) 9.20B-Ol (8/8) 0
(-4.94E+OO
- 4.04E+OO) 05 mi NB (2.27B-Ol
- 4.04E+oo) (-5.79E+OO
- 4.66B+oo)
Mn-54 24 3.63B-02 (16/16) 601 1.10B-Ol (4/4) 9.2JB-02 (8/8) 0
(-6.98B-02
- 2.2JB-Ol) 135 mi ESE (-5.7SB-Ol
- 3.29B-OI) (*S.75B-Ol 3.29E-Ol)
(;,10 L'-.
((
TABLEG TABLEG
SUMMARY
SUMMARY
OF OF DATA DATA FORFOR SSES SSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORING MONITORING PROGRAM* 2003 2003 NAMEOFFACILITY: SUSQUEIJANNASTEAMELECTRlCSTATlON NAMEOFFACILITY: SUSQUEIJANNASTEAMELECTRlCSTATlON ",
LOCATION OF LOCATION OF FACILITY:
FACILITY: L~ZERNE COUNTY, COUNTY, PENNSYLVANIA, PENNSYLVANIA, .' .'
Reporting Period:
Reporting Period: ,, DfCember DfCember 30, 30, 2001 2001 to ','
to ',' January 30, January 30, 2004 2004 -"-"
,,' ",Paie9orl3
",Paie9orl3 .. ,.,...
.. "" ~ ..
ANALYSISAND ANALYSISAND LOWERUMIT LOWERUMIT ** ,,
- I.
. I .
NUMBER OF NUMBER OF MEDIUMORPAntWAY MEDIUMORPAntWAY TOTALNUMBER TOTALNUMBER OF OF Au.tNDlCATOR Au.tNDlCATOR LOCATIONS LOCATIONS t:.aCATIONv.TnllRGHF.STMEAN t:.aCATIONv.TnllRGHF.STMEAN CONl'ROLlOCATION CONl'ROLlOCATION NONltOUl'INP.
NONltOUl'INP.
SAMPU!D SAMPU!D OF ANALYSES OF ANALYSES DB1"I!C1lON DB1"I!C1lON .. MEm(3)
MEm(3) ,, ,, NAMe NAMe MEm(3) ,,
MEm(3) MBAN(3)
MBAN(3) "" REPORTED REPORTED (UNIT OFMBASlJR.EMEND (UNIT 1'l!RFORMBD (l)
OFMBASlJR.EMEND 1'l!RFORMBD (l) (W)(1)
(W)(1) RANGB RANGB DtSTANCB ANDDnmC1lON DtSTANCB ANDDnmC1lON RANGB RANGB RANGB RANGB MBAmREMJ!NTS(4)
MBAmREMJ!NTS(4)
Afr PartrculatH (cont) ,~. ~. .. t, , I' Quartedy Composite Co-58 24 *1.76E*02 (16 I 16) 3S2 1.3SE*Ol (4 14) *9.0lE-02 (8 I S) o (E*Ol pCiIm3) (-:3.02E.Ol "- 4.75E*Ol) O.S mi NE" (-6.89E*02
- 4.7SE*Ol) (*3.SSE*Ol - 4.g6E-02)
., \' ,
PC:S9 24 *9.55E*02 (16 I 16) 1251 S.03E-OI (4 14) 4.0SE-Ol (8 I 8) o
(*I.ISE+OO - t.OgE+OO) 0.4 mi 'WSW (1.0SE-OI - I) (.8.34E-Ol
- 1.27E+oo) 24 2.3gE*02 (16 i 16) Sot 8.38E-02 (4 I 4) 5.70E-02 (8/8) o
, (-I.4SE-OI'
.' . '."" ..- , ,0: ,.:
24 *2.8gE-Ol (16 116) 1251 -7.97E-Ol (4 14) ,~2.46E-Ol , (8 18) " ""; o
(.I.34E+OO" - 6.2SE-Ol)' 0.4' mi"'wSW (~S.~Ot ,:'. 6.~1) ,J (.l.Ol~:*OO, -" 2.?3E-0l)*
- ~, ~: .. I_
- r!:' J" .. ;
r ',(. L' ~
2'J'*9S ' 1.78E-02 (16 116) 13S6 8.62E-02 (414)..., *7.31E-02 (8/8) ':' -," o
(-S.13~~(!: * : ~.??E.o15':: 0.4 mi W (.3.07E.Ot', - ,4.77E-01) (-2.42E-Ol, -" 9.69E-0l)
- *
- f :'.."
Nb-9S' 24 O.OOE+OO (16 116) 601 O.OOE+OO * (4/4) '; ,;~,., O,OOE+OO, (8/8) " ' , o
((i.OOE+OO " .: O.OOE+oO)' 13.S mi' ESE (o.oOE+OO' ': O.OOE+OO) (O.OOE+OO' - ,O.oOE+oO)
Cs*l34 24 50 O.OOE+OO (161 16) 1281 *3,46E-02 (414) -3.00E-Ol (8 18) , l o
(.S.96E-Ol " ' 8.9tE*0l) 0.4 mi WSW (-9.70E-0l
- 4.42E-0l) (-'S.09E-Ot, - 2.49E-02)
Cs-137 24 60 4.15E*02 ,(16 116) 13S6 1.19&01, (414) 2.07E-02 (8/8) o
(.9.46E*02 - J.6lE-Ol) 0.4 mi W (6.29&02 1.6 IE-O 1) (.6.S2E-02 t.OlE-ot)
Ba-140 .24 -4.S9E+OO (16/16) 12EI 5.S4E+OO (4 14) 2. 12E*Ot (8 IS) o
(-2.38E+?I,,' 1.74E+0l), 4.7 mi WSW, (-4.OlE+OO - -t.74E+01) (.1.19E+OI -, S.l7E+OO)
La-140 24" *2.94E+OO ' (16 / 16) 1251 1.97E+oO (4 /4) 4.77E-Ol ' (8 /8) o
, (-2.42E+Ol . ' 4.8IE+OO) 0.4 mi WSW , (-4.43E-01 - -4.8lE+OO) (-S.49E+OO
- l.2SE+OI)
-<, \
.. , ,,,, ~,
. , 'j
~ ., , .
TABLEG TABLEG
SUMMARY
SUMMARY
OF OF DATA DATA FORFOR SSES SSES OPERATIONAL RADIOLOGICAL OPERATIONAL ENVIRONMENTAL MONITORING RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRA¥. 2003 2003 NAME OF NAME OF FACIUTY:
FACIUTY: SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECTRIC ELECTRIC STATION STATION LOCATION OF LOCATION OF FACIUTY:
FACIUTY: LUZERNE COUNTY, PENNSYLVANIA LUZERNE COUNTY, PENNSYLVANIA Reporting Period:
Reporting Period: 30, 2002 December 30, December 2002 to to January 30, January 30, 2004 2004 Page 10 Page 10 ot13 ot13 ANALYSIS AND ANALYSIS AND LOWERUMlT LOWERUMlT NUMBBROP NUMBBROP M1IDItJM ORl'ATIlWAY M1IDItJM ORl'ATIlWAY TOTALNUMBER TOTALNUMBER OF OF ALL INDICATOR ALL INDICATOR LOCATIONS LOCATIONS LOCATION MlllmGImsT LOCATION MlllmGImsT MEAN MEAN CONrROLLOCATION CONrROLLOCATION NONROtmNB NONROtmNB SAMl'llID SAMl'llID OPANALYSES OPANALYSES DEl"ECIlON DEl"ECIlON MBAN{3)
MBAN{3) NAME NAME MEAN (3)
MEAN (3) MBAN(3)
MBAN(3) REPORTED REPORTED
~UNIT OFMBASUREMBNI1 PHRFORMED ~I~
OFMBASUREMBNI1 PHRFORMED ~IlJ)lP! RANOB RANOB DISTANCE AND DISTANCE AND DIREmlON DIREmlON RANOB RANOB RANGE RANGE MBASUREMF..Nl'S~4!
Milk Milk 1-131 1-131 76 76 5.32B-02 (57/57) 5.32B-02 (57/57) 1001 1001 9.0SE-02 (19/19) 9.0SE-02 (19/19) 9.0SB-02 (19/19) 9.0SB-02 (19/19) 00 (pC'JJ1)
(pC'JJ1) (-1.70E-OI
(-1.70E-OI -- 4.40E-Ol) 4.40E-Ol) 14 14 mi SSW mi SSW (-S.ooE-02
(-S.ooE-02 -- 4.50E-Ol) 4.50E-Ol) (-8.ooE-02
(-8.ooE-02 -- 4.50B-0l) 4.50B-0l)
OammaSpcc K-40 76 1.38E+03 (57/57) 1001 1.41E+03 (19/19) 1.4IE+03 (19 119) 0 (9.4~E+02 1.55E+03) 14 mi SSW (S.19E+02 - 1.53E+03) (8.19E+02 ' - 1.53E+03)
Mtr54 76 -1.8SB-Ol (57/57) 10DZ -5.268-02 (19/19) -4.428-01 (19/19) 0
(-4.30E+OO - 2.50E+00) 3.1 mi SSW (-2.60E+oo - 2.50E+00) (-3.IOE+OO - 1.60E+OO)
Co-58 76 -4.ooE-OI (57/57) 1001 -7.S9E-02 (19/19) -7.898-02 (19119) 0
(-4.10E+00 - 3.30E+00) 14 mi SSW (-3.70E+00 - 2.30E+00) (*3.70E+00 - 2.30E+00)
Fe-59 76 4.60E-Ol (571 S7) IOD2 8.32E-Ol (19/19) 1.42B-OI (19/19) 0
(-1.20E+Ol 1.228+01) 3.1 nu SSW (-4.ooE+OO - .8.ooE+OO) (-4.60E+OO - 7.30E+00)
Co-60 76 2.41E-Ol (57/57) 1001 6. 11E-Ol (19/19) 2.21£*01 (19/19) 0
(-4.70E+00 - 5.40E+00) 3 mi SSW (-3.00£+00 . 3.30E+00) (-2.9OE+00 . 2.9OE+00)
Zn-65 76 -2.77E+00 (57/57) 1002 -9.2IE-Ol (19/19) -2.928+00 (19/19) 0
(-I.60E+Ol . 7.00E+00) 3.1 nIi SSW (-I.60E+Ol - 7.00E+OO) (-I.34E+Ol - 4.20E+00)
Zr*95 76 -2.63E-02 (57 J 57) 12H2 3.58£.01 (19/19) -2.5gB-01 (19119) 0
(-7.20E+00 - 3.60E+00) 1.7 mi WSW (-4.30E+OO - 3.60E+00) (-4.30E+00 - 7.50£+00)
Nb-95 76 2.56E-Ol (57/57) 1001 4.31E-Ol (19/19) 4.31E-Ol (19/19) 0
(-2.80£+00 - 4.70£+00) 14 mi SSW (-2.00£+00 - 2.70E+00) (-2.00£+00 - 2.70E+00)
Cs-l34 76 15 -S.71E-03 (57/57) 1002 4.11B-01 (19/19) *2.21&01 (19/19) 0
(-4.00E+OO . 4. 1OE+OO) 3.1 mi SSW (-1.70£+09 - 2.80£+00) (-2.80E+00 - 2.6OE+00)
Cs*137 76 18 -S.71E-03 (57/57) 1001 S.58E-Ol (19/19) 5.58B-01 (19/19) 0
(-3.20£+00 - 3.S0E+00) 14 mi SSW (-1.20E+OO* - 2.60E+OO) (-1.20E+00 - 2.60E+OO)
Ba-140 76 60 -2.49B-Ol (57/57) 1001 1.89£-01 (19/19) 1.89E*OI (19/19) 0
(-4.80£+00 - 5.00E+00) 14 nIi SSW (-2.70E+OO - 3.90£+00) (-2.70E+00 - 3.9OE+00)
La-l40 76 15 *2.8SB-Ol (571 S7) . 1001 2.16.6-01 (19119) 2. 16E-Ol (19/19) 0
(-5.50E+00 - .5.80E+00) 14 nIi SSW (-3.10E+OO . 4.40E+00) (-3.10E+00 - 4.40E+00)
( (~ (
TABLEG TABLEG
SUMMARY
SUMMARY
OF OF DATADATA FOR FOR SSES SSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORING MONITORING PROGRAM* 2003 2003 NAME OF NAME OF FACILITY:
FACILITY: SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECTRIC ELECTRIC STATION STATION LOCATION OF LOCATION OF FACILITY:
FACILITY: LUZERNE LUZERNE COUNTY, COUNTY, PENNSYLVANIA PENNSYLVANIA Reporting Period:
Reporting Period: 'Detember
'Detember 30, 30, 2002 2002 to to Ianuary Ianuary 30, 30, 2004 2004
': Page Page 11 11 olllolll ~ . -I"
. -I" ** II **
ANALYSIS AND ANALYSIS AND LOWERUMIT LOWERUMIT NUMBER OF NUMBER OF MEDIUMORPA111WAY MEDIUMORPA111WAY TOfALNUMBER TOfALNUMBER OF OF AIL INDICATOR AIL INDICATOR LOCATIONS LOCATIONS LOCATIONwmJlnGHBSTMEAN ,,
LOCATIONwmJlnGHBSTMEAN CONTROL LOCATION CONTROL LOCATION NONROtmNB NONROtmNB SAMPI.J!l)
SAMPI.J!l) OP ANALYSES OP ANALYSES Dm:nCTION Dm:nCTION M1lAN(3)
M1lAN(3) NA}.m NA}.m MEAN (3)
MEAN (3) MEAN (3)
MEAN (3) REI'OImID REI'OImID (UNlT OPMBAS1.lREMEN"O (UNlT PERFORMED ~Sl OPMBAS1.lREMEN"O PERFORMED (lll))(Zl (lll))(Zl RANGB RANGB DISTANCE AND DISTANCE AND DIRECTION DIRECTION ,.' ,.' ,, RANGE RANGE ',' ',' ,, RANGE RANGE MEAStJREMENTS~4!
son son Gamma Gamma Spec Spec (pCiIkg chy) K-40 8 l.44E+04 (6/6) 13S6 1.62E+04 (2/2) 1.06E+04 (2/2) 0 (l.03E+04 1.82E+04) 0.4 mi W (l.43E+04
- 1.82E+04) (1.02E+04
- 1.10E+04)
Mn-S4 8 *1.S0E+00 (6/6), 13S6 *S.ooE-OI (2/2) *1.20E+Ol (2/2) 0
(.9:ooE+00 * '4.00E+OO) 0.4 mi W (.S.ooE+oo
- 4.00E+OO) (-I.90B+Ol - -S.OOE+OO)
Co-58 8 *6.33E+00 (6/6) 3S2 l.OOE+OO (2/2) " O.OOE+OO (2/2) 0
(-1:8OB+01 * ,9'OOE+OO) 0.5 mi NE (:7.00~+OO
- 9.00E+OO) (-S.OOE+OO
- S.OOB+OO)
Pc-59 8 -6.17B+OO (6/6), ' 1356 , 4.00B+OO (2/2);., .,:' 4.05B+Ol (2/2) 0
, ,I J. ~ ,~
, (~2.80E+61
'1' : :.' ~ ~. r
- 3.60B+0l)
... ~
0.4 tid W (-2.8~+.01
- 3.60E+Ol) (.7.2OB+01 - *9.00E+OO)
"CO-:60 8 4.00B+00 7.00E+OO (2'.2) , .1.OOB+Ol (2/2) 0
,f1.80E+01 (6 1,6)" .,'
-1.2QE+01) 3S2,_
0.5 mi
,'rm (2.00E+OO - 1.20B+Ol) (.1.80B+Ol - -2.00E+OO)
~ 1 . , ..... "!-
Zn-6S 8
- l.87B+O I (6/6) " 1251 . ..
~
,9.00E+00 (2/2), S.OOB+OO (2/2) 0
(-1. 1OE+02
- 6.ooB+Ol) 0:4 mi WSW (-3.2OB+01 - *S.ooB+01) (.3.00E+Ol
- 4.00B+Ol)
Zr-9S 8 -1.15B+03 (6 /6) 801 4.80B+Ol (2/2) .' 4.80B+Ol (2/2) 0
(-6.70B+03
- 3.00B+01) 12 mi SSE (4.70B+(Jt
- 4.90E+01) (4.70B+Ol
- 4.90B+Ol)
~95 8 4.67B+00 (616) 801 1.70E+Ol (212) 1.70B+Ol (2/2) 0 (4.30E+Ol
- l.60E+Ol) 12 mi SSE (.S.OOE+OO
- 3.90E+01) (.S.OOE+oo - 3.90B+OI)
Cs*l34 8 3.83B+00 (6/6) 801 3.30E+Ol (212) 3.30E+Ol (2/2) 0
(-7.00E+OO - 2.40E+Ol) 12 mi SSE (l.40E+Ol - S.20E+Ol) (1.40E+Ol
- 5.20E+Ol)
,Cs-137 8 4.28B+Ol (6/6) 1281 8.60E+Ol (2/2) 7.45B+Ol (2/2) 0
(*2.10E+Ol * " 9.60B+Ol) 0.4- mi:*WSW . (7.60E+Ol ". 9.60B+Ol) (S.20B+Ol
- 9.70E+Ol)
Ba*140 8 6.67B-Ol (6/6) 3S2 2.S0E+01, . (212) -1.80B+O'l (2/2) 0
(.S:OOE+Ol" .' 8.00E+0I) O.S 'IDi NE ' (1.ooE+Ol
- 4.00B+Ol) (.2.S0E+Ol - -1.IOE+Ol)
. La-l40 8 -1.13B+Ol (6 /6) 3S2 l.05B+Ol (212) .2.0SB+Ol (2/2) 0
-(4.90B+Ol - 1.40E+0l) . 0.5 ini NE (7.00E+oo, .- 1.40B+OI) -(2.80E+Ol - -1.30E+Ol)
.. ;. ~
f,r ' " ***
~ ... :',',
- t ' ** ,,: ,I * . ..... : I
(].13
TABLEG TABLEG
SUMMARY
SUMMARY
OF OF DATA DATA FOR FOR SSES SSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORINGMONITORING PROGRAM* 2003 2003 NAME OF NAME OF FACILITY:
FACILITY: SUSQUEHANNASTEAMELECTRICSTATION SUSQUEHANNASTEAMELECTRICSTATION LOCATION OF LOCATION OF FACILITY:
FACILITY: LUZERNE LUZERNE COUNTY,COUNTY, PENNSYLVANIA PENNSYLVANIA Reporting Period:
Reporting Period: 30, 1001 December 30, December 1001 to to January 30, January 30, 1004 1004 Page 11 Page or 13 11 or 13 ANALYSIS AND ANALYSIS AND LOWERllMIT LOWERllMIT NUMBER OF NUMBER OF MEDIUMORPAnlWAY MEDIUMORPAnlWAY TarALNUMBER TarALNUMBER OF OF AILlNDlCATOR LOCAnONS AILlNDlCATOR LOCAnONS LOCAnONWnllInGUBSl'MEAN LOCAnONWnllInGUBSl'MEAN CONrROLLOCAnON CONrROLLOCAnON NONROUIlNB NONROUIlNB SAMPLED SAMPLED OPANALYSIlS OPANALYSIlS DBTBCllON DBTBCllON MEAN (3)
MEAN (3) NAME NAME MEAN (3)
MEAN (3) MEAN (3)
MEAN (3) REPORTED REPORTED
!UNITOFMBASUREMENT) PERFORMED!!}
!UNITOFMBASUREMENT) PERFORMED!!} !un~p~ RANGB RANGB DlSTANa!
DlST ANa! AND AND DIRECIlON DIRECIlON RANGB RANGB RANGB RANGB MBAWRE.MENTS(4!
MBAWRE.MENTS(4!
Soil (com)
Soil (com) &a-226
&a-226 0 0 00 (pCiJkg dIy)
(pCiJkg dIy) nl.-228 8 7.89E+02 (6/6) 382 1.02E+03 (2/2) 8. 15E+02 (2/2) 0
(-2.00&00 1.00E+03) 0.5 mi NE (UlOE+03 - I.04E+03) (7.30E+02 - 9.00E+02)
Food/Garden Crops OammaSpcx:
(pC'1Ikg wet) Be-7 2 8.43E+00 (2/2) UP2 1.39E+Ol (1 I) 0 (2.95E+OO 1.39E+Ol) 5.5 mi SW (1.39E+Ol
- 1.39E+Ol)
K-40 2 4.S6E+03 (2/2) 1102 4.66E+03 (111) 0 (4.47E+03 - 4.66E+03) 3.5 mi SW (4.66E+03 - 4.66E+03)
Mn-S4 2 -4.75E-Ol (2/2) UD2 1.36E+00 (111) 0
(-2.31E+00 - 1.36E+OO) 3.5 mi SW (1.36E+00 - 1.36E+00)
Co-58 2 -1.28E+OO (2/2) 1102 -1.07E+00 (111) 0
(-1.48E+00 - .1.07E+00) 3.5 mi sW (-1.07E+00 - -1.07E+00)
Fe-59 2 *3.75E-Ol (2/2) llF2 1.97E+OO (111) 0
(-2.72E+00
- 1.97E+00) 5.5 mi sW (1.97E+00 - 1.97E+00)
Co-60 2 3.48E+00 (2/2) llF2 5.53E+OO (111) 0 (1.42E+00 - 5.53E+00) 5.5 mi SW (5.53E+00
- 5.53E+00)
Zn-6S 2 -2.01E+Ol (2/2) llF2
- I.69E+O 1 (1/1) 0
(-2.33E+Ol - .1.69E+Ol) 5.5 mi SW (*1.69E+Ol * *1.69E+0l)
Zr-95 2 7.40E-Ol (2/2) 1IP2 5.73E+OO (1/1) 0
(-4.25E+OO
- 5.73E+00) 5.5 mi Sw (5.73E+00 * . 5.73E+00)
~95 2 O.OOE+OO (2/2) UD2 O.OOE+OO (1/1) 0 (O.OOE+OO
- O.OOE+OO) 3.5 mi SW (O.OOE+OO
- O.OOE+OO) 1-131 2 -6.32E+00 (2/2) 1IP2 -6.01E+OO (111) 0
(-6.63E+00 - -6.01E+OO) 5.5 'mi SW (-6.01E+00 * -6.01E+00)
(
co.
co. ((
TABLEG TABLEG
SUMMARY
SUMMARY
OF OF DATA DATA FOR FOR SSES SSES OPERATIONAL RADIOLOGICAL OPERATIONAL RADIOLOGICAL ENVIRONMENTAL ENVIRONMENTAL MONITORING MONITORING PROGRAM *1003 NAME OF NAME OF FACILITY:
FACILITY: SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECTRIC ELECTRIC STATION STATION LOCATIONOFFACILITY: LUZERNE LOCATIONOFFACILITY: LUZERNE COUNTY, COUNTY, PENNSYLVANIA PENNSYLVANIA Reporting Period:
Reporting Period: December 30, December 30, 2001 2001 to to January 30, January 1004 30, 1004 Page13ort3 Page13ort3 LOWERUMIT ANALYSlSAND LOWERUMIT ANALYSlSAND NUMBBROP NUMBBROP MEDIUM MEDIUM OR OR PATIlWAY PATIlWAY TOl'ALNUMBER TOl'ALNUMBER OF OF AIL INDICATOR AIL INDICATOR LOCATIONS LOCATIONS LOCATIONwmlIDGHEST LOCATIONwmlIDGHEST MEAN MEAN CONI'ROL LOCATION CONI'ROL LOCATION NONROUl1NB NONROUl1NB SAMPlED SAMPlED OF ANALYSES OF ANALYSES DETECTION DETECTION MBAN(3)
MBAN(3) NAME NAME MEAN (3)
MEAN (3) MEAN (3)
MEAN (3) REPORTIID REPORTIID (UN!TOFMBASUREMENl) PERFORMED (UN!TOFMBASUREMENl) PERFORMED Cll Cll (llD) (1)
(llD) (1) RANGE RANGE DISTANc:B AND DISTANc:B AND DIRECTION DIRECTION RANGE RANGE RANGE RANGE M1!ASU1U!MENTS(4)
M1!ASU1U!MENTS(4)
Food/Garden Crops (conl)
(pCiIkg wet) Cs-I34 2 -t.9lE+OI (2/2) llF2 -1.S2E+Ol (1 fl) 0
(-2.00E+Ol -1.82E+Ot) 5.5 mi SW (-1.82E+Ol . -1.82E+OJ)
Cs-137 2 -3.S4E+OO (2/2) 1100 -1.07E+OO (Ill) 0
(-6.00E+OO - -1.07E+OO) 3.S mi SW (-t.07E+OO - -1.07E+OO)
Ba-140 2 1.89E+01 (212) llF2 4.4lE+Ol (1fl) 0
(-6.32E+OO . 4.4lE+Ol) S.S mi SW (4.41E+Ot . 4.4tE+Ol)
La-140 2 -l.B4E+OO (2f2) 1100 5.5SB-Ot (1ft) 0
(-4.24E+OO - S.5gB-Ol) 3.5 ml SW (5.5gB-Ot - 5.5SB-Ot)
I. The I. The total nnmber of total nnmber of analysis analysis does does not not include include duplicates, duplicates, splits, splits, or or tepealed analyses.
tepealed analyses.
- 2. The Teclmica1
- 2. The Teclmica1 Requirement LtO's are Requirement LtO's are shown shown when when applicable.
applicable.
- 3. The
- 3. The means means areare based based on an available on an available measured measured results.
results. When possible, this When possible, this includes includes those those below below the MDCs as the MDCs as wen wen as as those those above above them.
them.
- 4. USNRC reporting
- 4. USNRC levels are reporting levels are specified specified in the Teclmica1Requiremcnts.
in the Teclmica1Requiremcnts.
0*15
APPENDIX*H
[:;; ;,
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report H-1
II II AppendixH AppendixH
..... ""'." .) ::::".~--, .~.; .'
- j".~,
The data presented The data presented in in the the following following tablestables werewere included included if if specific specific analysis analysis results results routinely exceeded routinely exceeded the the applicable applicable MDCsMDCs 2003 inin 2003 andlor andlor routinely routinely may may have have done done so so in in previous years.
previous years. The The comparisons comparisons may may be be useful useful forfor observing observing any any step step changes changes that that may may occur in occur in the.
the. environment environment over over aa wide wide area.
area. However, However, thethe importance importance attached attached to these to these comparisons shouid' comparisons shouid' be be tempered tempered by by 'the
'the understanding' understanding' that' that' changes, changes, inin methods.
methods. of of '" I
- analysis, analysis, typical typical MDCs MDCs achieved achieved by by thethe analyses, analyses, andand averaging averaging methods over the methods over the years years \.......J may tend may tend to blur the to blur the picture in sOIl1~ cases.
picture in cases.
2003 Radiological 2003 Radiological En~jronmentall\lonitorlng Report Report H-2 H-2
, A,;,iendiX H AMBIENT RADIATION AMBIENT RADIATION MONITORING', MONITORING', l;
.: ;;: ~
TABLEHI AMBIENT AMBIENT RADIA RADIA nON nON LEVELS LEVELS AS AS MEASURED MEASURED BY BY TLDS TLDS (mRlSTD (mRlSTD QTR) QTR) .
Location -,-
--Location -, - , " "-. ~Indicator:':"':"""::-' .-r..,- ,-*-~~Control~~ .:-~
Period Period Pre-Op .. : Operational Pre-Op Operational 1978-81 1982-02 2003 1978-81 1982-02 '2003 Ran2e Ran2e 18.5-19.2 14.7-20.8 - 15.0-17.9 14.8-20.8 -
Mean Mean 18.9 18.2 20.2 16.3 17.9 19.0
.\
AQUATIC PATHWAY
- AQUATIC PATHWAY MONITORING MONITORING
~
o.
. :. ,,~ ...
~~, ~
~' .:
~ ,
"" '"TABLE H 2 SURFACE 'NATER SURFACE 'NATER GROISS GROISS BETAACTIVITJES BETAACTIVITJES (pCiJI) (pCiJI) ,
Indicator' 'Control ~' ...w Location
-~--. ~
~..-~
Indicator' 'Control
~ -~.
Location
~
Period Period Pre-Op Operational " Pre-Op , Operational' "
1978-81 1982-02 2003 1978-81 1982-02 2003 Range Range 3.2-4.9 3.0-7.7
. -- 2.9-5.2 2.8-6.7 --
,Mean 5.6 . *.:.~6:1;:~
,Mean 3.8 " 4.0 3.8 2.4 TABLE H3
" : TABLE H3 SURFACE SURFACE WATERJODINE-131WATERJODINE-131 ACTIVITIES ACTIVITIES (pCiJI)
Location Location "
- Indicator I , Coritrol " ,
Period Period ; Pre-Op Operational Pre-Op Operational 1979-81 1982-02 2003 1979-81 1982-02 2003 Range Range 0.24-0.37 0.06-0.61 -- 0.29-0.43 0.03-1.0 --
Mean Mean 0.29 0.32 0.36 0.36 0.32 0.26
.. "t I
, ;: : j;' ~\TABLE*H 4 , , ~ "' ~ .., .
'-SURFACE
'-SURFACE WATER WATER TRITIUM TRITIUM ACTIVITIES ACTIVITIES (pCiJI) (pCiJI)
Location* ' , Indicator I i: rjl~~: .,Control i , "
"Period
, "Period Pre-Op ;-"', Operational' 1 ' :'Pre-Op' \ .".. Op.erational
- .. ~.
., 1978-81 ',', 1982.:02* -~003 .. ,1978-81, ,:1982-02* 2003
- -:Ran2e .. '101-122 126-1363" -.'.-! 119-319 -239 - +212 --
Mean Mean 109 573 1,576 171 52 32
- 1990 results
- 1990 results were were not not averaged averaged with with 1982-01 1982-01 data data because because the the validity validity ofthe ofthe values is 1990 values 1990 is questionable questionable in in some some instances. instances. Laboratory Laboratory analysis analysis error error isis suspected. See suspected. See the the 1990 1990 AnnualAnnual Report. Report.
H-3 H-3 :2003 RadiologicalRadiological Environmental Environmental Monitoring Monitoring Report Report
II II AppendixH TABLEH5-,, "" , . ,
DRINKING WATER DRINKING WATER GROSS GROSS ALPHA ALPHA ACTIVITIESACTIVITIES (pCiJI) (pCiJI)
Period Period Preoperational-"
Preoperational-" . ' Operational Operational 1980- 81 1980- 81 . 1982 1982 -02 -02 2003 ""
2003 Ran2e' Ran2e' - ' : 0.10.1 -10.0-10.0 -,
Mean-Mean- ."*1
" , , 1.3 1.3 1.4 1.4 0.18 0.18
.. TABLEH6 TABLEH6 DRINKING WATER DRINKING WATER GROSS GROSS UETA UETA ACTIVITIES ACTIVITIES (pCiJI) (pCiJI)
Period Period Preopera tional Preopera tional Operational Operational 1977 -- 81' 1977 81' ' ,
1982 1982 -- 02, 02, 2003 2003 Ranee Ranee
. 2.2 2.2 -- 3~2 2.1 .... 5.4' 2.1 5.4' ----
Mean Mean ><' " ,, 2.7 2.7 '3:1
'3:1 2.1 2.1
.... ~
TABLEH7 TABLEH7 DRINKING ,WATER DRINKING ,WATER TRITIUM TRITIUM ACTIVITIES ACTIVITIES (pCiJI) (pCiJI)
Period Period Preoperational',
Preoperational', Operational
' , 1977"": 81' , ,
1982 - 02 2003 Ran2e' --
Ran2e' 101 -194 '-247 :.. +220 Mean Mean 132 " 62 62 TABLEHS' TABLEHS' FISH POTASSIUM-40 FISH POTASSIUM-40 ACTIVITIES ACTIVITIES (pCi/g (pCi/g wet)wet)
- Location Location ::. ", '. Iridicator;* -:
- J ,",
- , * * * ~J
, Control Control Period Period ; Pre-Op Pre-Op Operational Operational Pre-:-Op
. Pre-:-Op Operational :
Operational 1977-81 1977-81 1982-02~ 2003:
2003: 1977-81 1977-81 1982-02 1982-02 2003 2003 Ram~e 2.7 -- 3.5 2.7 3.5 ' ',3~1 '-5.3 '-5.3 ---- 2.8 -- 3.6 2.8 3.6 3.1 -4.2 3.1 -4.2 _._.
Mean Mean 3.2 3.2 ,3.8
,3.8 3.6 3.6 3.2 3.2 3.5 3.5 3.2 3.2 2003 Radiological 2003 Radiological Enyironmental Enyironmental Monitoring Monitoring Report Report H-4 H-4
\\ ..Armendix Armendix H** .
SEDIMENT SEDIMENT POTASSIUM-40 POTASSIUM-40 ACTIVITIES ACTIVITIES (pCi/~ dD'l dD'l
.. Location Location Indicator Indicator
,. 7~" * .,
- Control Control Period .. " ,
Period " , ,Pre--Op , :' . Operational , Prc-Op .Operational
"'1978*81 1982-02 2003 "'1978-81 1982-02 .*.*2003 Ran2e" Ran2e" . 8.6-10.4 7.4';13.6 7.5-11.0 : ',6.2-13.0 ~ -.'
'--
- t *
'Mean
'Mean " > '9.3 "': 10.8 l " '12.3 ~
'7.7 ' 10.5 12.9 SEDIME:ST SEDIME:ST RADIUM-226 RADIUM-226 ACTIVITIES ACTIVITIES (pCi/2 (pCi/2 dry) dry)
Location Location Indicator Indicator Control Control Period Period *Pre--Op Operational' .Pre--Op Operational
,:1978-81 " : ~1982-02 ". '2003 : "1978-81 c 1982-02 2003 Ran2e Ran2e : '0.5-0.7 0.5-2.0: - ,0.6-1.9 0.4-2.1 '. --
Mean Mean ; , 0.6 '15 '," ",2.4', , 0.7 1.5 1.6
~ .' .. ;
. ~- ,- - ' .
i
':TABLEHll-:
SEDIMENT THORIUM-228
. SEDIMENT THORIUM-228 ACTIVITIES ACTIVITIES (pCi/g (pCi/g dry) dry) ,,
,, Location Location Indicator' 11 .. ': : . Control Period Period . 1984': 02* ,'f ." ' '2003 *1984 ~ 02* 2003 Range Range 0.9 - 1.7 0.8-2.F* -
Mean Mean 1.1 3.2 1.1 3.0
...... '\ . ,:.. l' ,- "
...... r~ * " *** ;; ..
~
- Th-232 was was reported reported instead instead ofTh-228ofTh-228 in:*1990 ....
- ,:: :. I!' ,
- Th-232 J"
'( ~
,f;;.
~:.
":.: ~',,:
- ~<
,;,,\; ;':':rtABLEHii*: '
.. :.*:SEDIMENT CESIUM-137 CESIUM-137 ACTIVITIES ACTIVITIES (pCilg (pCilg dry) dry) .
.. Location" 1 . ,
~
., ..,'.., Indicator .. I '" ... ~ ~ ;
- 'Control ;. ~ "'"
.. 'Pre--Op' , .
Period Period " <", Operational . .... *:Pre:"Op.,: ': .. " . Operational "'
..- .
- I ~.1978-81* '.. :1982~2 __ ~2003 ... ,11978-81 ' 1982-02 " 2003 Range Range 0.08-0.15* . 0.04-0.17 I .
..*. ! __ f
., - "0.08-0.21 0.06-0.21 -
Mean Mean 0.10 0.09 0.07 0.11 0.11 0.08 H-S H-S ~'." 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
II II AppendixH AppendixH ATl\10SPHERIC PATHWAY ATl\10SPHERIC PATHWAY MONITORING MONITORING
. ': ','1'
.. TABLEH13" TABLEH13" AiR PARTICULATE AiR PARTICULATE GROSS GROSS BETA BETA ACTIVITIES ACTIVITIES (E-3 ilCilm33)) ,,
(E-3 ilCilm Location :: Indicator, ,, Control Control
~
Location Period Period Pre-Op ; i' Operational "Pre-Op Operational 1978-81 " 1982-02 . 2003 . 1978-81 1982-02 2003 Range Range 24- 97 13 - 29 -- 24 -102 12-28 --
Mean Mean 61 16 15 62 16 13 TABLEH14 AIR I~ARTICUL)~TE BERYLI..IUM-7ACTivriiiS(E-fpCilm AIR BERYLI..IUM-7ACTivriiiS(E-fpCilmJ., J.,
.. Location Location
-.-. Indicator' . , Control
- Period Period . Pre-Op* Operational Pre-OU .. ' Operational 1978-81 1982-02* 2003 1978-81 1982-02* 2003 Ranee Ranee 69 - 81 50 - 137 -- 59 - 85 49 -126 --
Mean Mean 76 *95 91 72 88 . 82 .
- 1990 1990 results results were were not not averaged averaged with with 1982-01 1982-01 data data becausebecause the the validity validity of of the the 1990 values 1990 values is is questionable questionable in in some some instances.
instances. Laboratory Laboratory analysis analysis error error is is suspected.
suspected. See See the'1990 the'1990 'Annual
'Annual Report.
Report.
TERRESTRIAL PATHWAY TERRESTRIAL PATHWAY MONITORING MONITORING TABLE HIS SOIL POTASSIUM-40 SOIL POTASSIUM-40 ACTiVITIES ACTiVITIES (pCil2 (pCil2 dry) dry)
Location Location ' , Indicator' . -, -;.'. . . , . .****Control Period..
Period ..
Pre-Op Operational Pre-Op. Operational . ':
1979&81 *.1984-02 2003 . 1979&81 1984-02 . 2003'
.:.: Ran2e Ran2e c' c'
. 9.2 - 9.7 9.4-15.3 - 9.1'-1 [0 7.4-14.1 --
Mean Mean 9.5 11.7 14.4 10.1 10.5 10.6 .
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report .. H-6 H-6
- Appendix Appendix H H
"~TABLEH 16 16
," .. ':':~ '::>;'~i',,!~~SOILRADIUM-226ACTIVITIES '(pCilg '(pCilg di'y)'~:!" .. ' .. .. .' -,
Location I Location Indicator Indicator . Control Control .,
Period Period ' Pre-Op,: ;';Operational,:', : .. Pre-Op , Operational
- ...... *~:*.;. .... t . " 1979&81, ~~1984*02* ;: 2003*' , 1979&81 .**.~1984*02 2003 "
-Range,
-Range, .0
'0.8 -1.3 ,0.8 - 2.5 o' i
0.8 - 1.2' 1.0 - 2.2.' --
- o .
1 Mean 1 Mean 1.1 1.6 i' :0 1.0 1.7
- Radium-226 Radium-226 was was not not measured measured inin 2002 2002 or or 2003.
2003.
TABLEH 17
,, ,, SOIL SOIL THORIUM~228 :ACTIVITIES :ACTIVITIES (pCi/g (pCi/g dry) dry)
Location Location Indicator Indicator Control Control Period Period Pre-Op Operational Pre-Op Operational 1979&81 1984*02 2003 1979&81 1984*02 2003 I Range Range 0.9 -1.3 0.8-2.0 -- -- 0.7 -2.4 --
I Mean Mean 1.1 1.0 0.8 1.0 1.0 UJS TABLEH 18 TABLEH 18
.. .. .'. :SOIL:SOIL CESIUM~137,ACTIVITIES (pCi/g (pCi/g (lIj)
(lIj)
Location Location Indicator Control Period Period Pre*Op Operational Pre-Op Operational 1979&81 1982*02 2003 1979&81 1982-02 2!2L1 Range Range 0.5 -0.7 0.02 - 0.5 -- 0.2 -1.2 0.09 -1.2 --
Mean Mean 0.6 0.2 0.04 0.7 0.4 V.VI TABLEH TABLEH 19 19
_i " *
.. MILK MILK POTASSIUM~40 ACTIVITIES ACTIVITIES JJ)CiII). JJ)CiII). . ;' "
Location Location Indicator Indicator Control Control Period Period Pre-Op Operational Pre-Op Operational 1978*81 1985*02 2003 1978*81 1985-02 2003 Range Range 1222-1500 1241-1422 -- 1273-1500 1247-1472 --
Mean Mean 1325 1333 1383 1390 1331 1406
,, .. ,'2003
,'2003 Radiological Radiological Environmental Environmental Monitoring Monitoring Report Report
II II AopendixH AopendixH
',TABLE
',TABLE H20 H20 GROUND WATER GROUND WATER TRITIUM TRITIUM ACTIVITIES ACTIVITIES (pCiII)
(pCiII)
Location Indicator Control Location Indicator .. Control Period Period 'Pre-Op'
'Pre-Op' ,, Operational:
Operational: .. Pre-Op.',
Pre-Op.', .. .. .. Operational Operational 1980-81 1980-81 1982-02 1982-02 2003 1980-81 ,, 1982-02 2003 .. 1980-81 1982-02 2003',
2003',
.. Range' Range' .. -- .. ,, 9~109" .. ~206 '~'+ 180, 180,
117-119 117-119 ;.206~+260 -- ""
Mean Mean 101 101 59 59 54 54 118 118 67 67 17 17 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report H-8 H-8
f f II
/
/
- I
I
'J; ,,
'J; APPENDIX II APPENDIX I\....,.../"
I\....,.../"
I, I,
J.;;
J.;;
..~ !.
'2003 Radiological
'2003 Radiological Environmental Environmental Monitoring Monitoring Report Report 1-1
II II APDendixl APDendixl Results Results of of analyses analyses are are generally generally reported reported in in the the following following tables tables to to two two significant significant figures. Random figures. Random uncertainties uncertainties of of counting counting are are reported reported to to the the same same decimal decimal placeplace as as the the result.
result.
Calculated values for Calculated values for analysis analysis results results areare reported reported with with the the random random uncertainty uncertainty of of counting at counting at two two standard standard deviations deviations (28), (28), determined determined by by considering considering both both the the sample sample and background and background count count rates.
rates. The The uncertainty uncertainty of of an an activity activity is is influenced influenced by by the the volume volume or mass or mass of of the the sample, sample, the the background background count count rate, rate, the the count count times, times, the the method method usedused toto round otT round otT the the value value obtained obtained to to reflect reflect its its degree degree of of significance, significance, and and other other factors.
factors. The The uncertainties of uncertainties of activities activities determined determined by by gamma gamma spectrometric spectrometric analyses analyses are are also also influenced influenced by by the the relative relative concentrations concentrations of of the the radionuclides radionuclides in in the the sample, sample, the the energies energies and intensities and intensities of of thethe gammas gammas emitted emitted by by those those radionuclides, radionuclides, and and the the assumptions assumptions used used in selecting in selecting the the radionuclides radionuclides to to be be quantitatively quantitatively determined.
determined.
Results reported as Results reported as less less than <<) in than <<) in these these tables tables areare below below thethe minimum minimum detectable detectable (MDCs). The concentrations (MDCs).
concentrations The MDC MDC is is an an estimate estimate of of the the detection detection capabilities capabilities of of the the overall measurement overall measurement method, method, taking taking intointo account account not not only only the the counting counting system, system, butbut also also the characteristics the characteristics of of the the sample sample beingbeing courited.
courited. WhenWhen the the MDC MDC is is used used as as the the level level to to decide whether decide whether or or notnot to to enter enter aa measured measured value value into into aa table, table, there there is is aa 50%
50% chance chance that that the value the value will be entered will be entered whenwhen the the actual actual sample sample activity activity isis equivalent equivalent to to the the MDC.
MDC.
There is There is only only aa five five percent percent chance chance that that aa value value representing representing aa fluctuation fluctuation in in background background will be activity will activity be entered entered as as sample sample activity activity in in such such an an instance.
instance.
Measured Measured valuesvalues for for the the activities activities of of specific specific radionuclides, radionuclides, such such as as the the man-made man-made gamma-emitting radionuclides gamma-emitting radionuclides beryllium-7 beryllium-7 and and cesium-137, cesium-137, only only appear appear in in the the following tables following tables forfor each each specific specific medium medium when when the the levels levels that that areare measured measured exceedexceed thethe MDC values MDC values for for those those measurements measurements and and those those radionuclides radionuclides are are actually actually identified identified as as present in present in the the samples.
samples. Measured Measured valuesvalues for for the the analyses analyses thatthat are are not not radionuclide radionuclide specific, such specific, such asas gross gross alpha and beta alpha and beta analyses, analyses, alsoalso are are presented presented in in the the tables tables for for media only specific media specific only when when the the levels levels that that are are measured measured actually actually exceed exceed the the MDCs.
MDCs.
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report 1-2 1-2
c c (.
TABLE TABLE 1-11-1 c
c ENVIRONMENTAL TIIERMOLUMINESCENT ENVIRONMENTAL TIIERMOLUMINESCENT DOSIMETRY DOSIMETRY RESULTS RESULTS SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECfRIC ELECfRIC STATION STATION -- 20032003 ::
Results (I)
Results are in (I) are in mRlstd.
mRlstd. qtr qtr (2) +/- 2S (2) +/- 2S (3)
(3)
Flnt Quarter Flnt Quarter Second Quarter Second Quarter Third Quarter Third Quarter Fourth Fourth Quarter Quarter 01129103 01129103 toto 05101/03 05101/03 04129/03 04129/03 toto 07124103 07124103 07121103 07121103 to to 10123103 10123103 10121103 10121103 to to 01130104 01130104 Location Location ONSITE ONSITE IS2 23.6 +/- 1.4 24.3 +/- 1.9 23.6 +/- 1.2 26.5 +/- 2.1 2S2 17.5 +/- 1.8 15.8 +/- 1.3 20.5 +/- 0.8 17.9 +/- 1.1 2S3 20.4+/- 0.8 20.5 +/- 1.5 23.6 +/- 0.4 23.2 +/- 2.3 3S2 17.6 +/- 1.4 16.0 +/- 1.1 19.5 +/- 1.2 18.4 +/- 1.5 3S3 17.0 +/- 1.6 15.0 +/- 1.3 19.1 +/- 2.6 18.1 +/- 0.9 3S4 17.2 +/- 1.4 (4) 19.4 +/- 1.8 18.3 ::I: 1.1 4S3 22.0 +/- 1.2 21.0 +/- 1.1 24.2 +/- 1.0 23.5 +/- 1.9 4S6" " ..
j , ' I, 17.8 +/- 1.6 16.9 +/- 1.3 20.8 +/- 1.2 18.4 +/- 1.3
..- - .... 5S4- .- ......... 16.1"+/-*1.0 14.9 -+/- 1.3' "18.4 +/- 1.6' '17.2"+/- 0.9' 5'Si'j 1iJf"+/- '1.8"- 16:6' +/- '1.1 . 19.6"::1: '1.4 1s::f +/- '1.5:
6S4'; 23.8':;: '1.2';" 2~Lf*+/-2.1 27:9 +/-"1.2'* 26.,3' +/-' 0.9 6S9" 22.6'10.6* 23.2:;: '1.'1 r: 27:6 +/- 1.S" 25.i'+/- 0.8 '
7S6 22.9+/- '1.8" 23.3 +/- 1.3 ,26.7 +/-1.2 25.S +/- 1.3 '
7S7 1i.3+/-"1.0" 15.9'+/- '1.5 19.9:::1: 1.2 19:1 +/- 0.9 '
8S2' 22.9 ::I: 1.4 22.5 +/- 1.7 . 27.4 +/- 3.0' 25.5 ::1:0.9 9S2 31.7 +/- 1.8 " 41.9 +/- 6.4 44.7 +/- 2.6 44.1 +/- 3.0 lOSt 17.1 '+/- '1.8 15.9 +/- 1.7 19.1 +/- 2.4 18.1 +/- 1.1 10S2 26.6 +/-1.2 29.2 +/- 1.1 33.3 +/- 2.4 31.6 +/- 1.9 10S3 16.3 +/-'O.6 15.1 +/- 1.3 18.6 +/- 1.4 16.8+/- 0.9 I1S3 24.8 +/- 1.6 24.6 +/- 1.1 28.1 +/- 1.4 27.4 +/- 0.9 lis7 18.0 '+/- 1:2 16.9 '+/- 1.1 20.8 +/- 2.4 20.1 +/- 1.3 1-3 1-3
TABLE 1*1 ENVIRONMENTAL THERMOLUMINESCENT DOSIMETRY ENVIRONMENTAL THERMOLUMINESCENT DOSIMETRY RESULTS RESULTS SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION STATION -- 20032003 Results (1)
Results (1) arc arc in in mRistd.
mRistd. qtr qtr (2) +/- 2S (2) +/- 2S (3)
(3)
First Quarter First Quarter Second Quarter Second Quarter Third Quarter Third Quarter Fourth Quarter Fourth Quarter 01129/03 01129/03 to 05101/03 to 05101/03 04/29/03 04/29/03 to 07124/03 to 07124/03 07122103 07122103 to 10123/03 to 10123/03 10121103 10121103 to 0]130/04 to 0]130/04 Location 12S1 19.0 :l: 1.2 17.4 :I: 1.1 21.5 :I: 1.4 19.6 ;/; 1.3 12S3 24.2 :l: 1.2 22.8 :I: 1.5 25.9 :I: 0.8 24.3 :I: 1.7 1254 24.9 :l: 1.0 23.0 :I: 2.1 26.5 :I: 2.0 24.9 ;/; 0.9 12S5 21.0 ':l: 0.6 20.3 :I: 1.3 22.6 ;/; 1.6 21.S ;/; 0.9 12S6 21.4 :l: 1.0 19.9 ;/; 1.7 23.6 :I: 1.4 21.8 :I: 1.7 12S7 16.S :l: 1.2 14.9 ;/; 0.9 17.7 ;/; 1.S 17.2 :I: 0.6 13S2 23.4 :l: 1.2 21.7 ;/; 1.7 26.1 ;/; 1.4 24.3 :I: O.S 13S4 22.9 :l: 1.6 20.7 :I: 1.1 25.9 :I: 1.6 22.S*:!: 0.6 13S5 24.5 :l: 2.4 22.4 :I: 2.6 27.1 ;/; 1.4 25.4 ;/; 1.7 13S6 22.5 :l: 2..0 21.1 ;/; 1.3 24.2 :I: 1.8 23.0 ;/; 1.5 14S5 21.4 :l: 1.2 20.6 ;/; 1.7 23.5 :I: 1.4 21.2 ;/; 1.5 14S6 19.9 :l: 1.0 19.1 :I: 1.5 22.7 :I: 0.4 20.3 ;/; 1.5 15S5 19.5 :I: 1.0 17.8 :I: 0.6 21.8 :I: 1.0 21.2 :I: 4.5 16S1 22.3 :l: 1.S 22.2 :I: 1.1 24.4 :I: 1.0 23.S :I: 1.3 16S2 23.3 :I: 1.2 21.1 :I: 1.5 25.3 ;/; 1.4 23.9 :I: 1.5 See the comments at the end of this table.
1-4 1-4
((
TABLE I*!
TABLE ENVIRONMENTAL ENVIRONMENTAL Til Til ERMOLUMI ERMOLUMI NESCENT NESCENT DOSIMETRY DOSIMETRY RESULTS RESULTS SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION STATION -- 2003 2003 -.-.
Results (l)
Results are in (l) are in mRlstd. qtr (2) mRlstd. qtr +/- 2S (2) +/- 2S (3)
(3)
--t'
--t' .
. ;; I
I First Quarter First Quarter Second Quarter Second Quarter Third Quarter Third Quarter Fourth Quarter Fourth Quarter
- 01129/03 01129/03 __ to_ 05101103 to_ 05101103 04129103 04129103 07124/03 to. 07124/03 to. 07122/03 07122/03 ,to. 10123103,
,to. 10123103, 10121103 10121103 to to 01130104 01130104 Location Location 0-1 MILE OFFSITE 6A4. 20.7 :I: 1.6 18.7:1: 1.3 22.7 :I: 1.2 21.1 :I: 0.9 8A3 17.5 :I: 0.8 15.4 :I: 1.7 ' 19.2 :I: 1.6 ' 18.3 :I: 0.7 15A3 ' 18.9:1: 2.0 17.7 :I: 1.9 20.9 :I: 1.4 19.4 :I: 1.7
- ,16A2, ,. 16.4 :I: 1.6 14.3 :I: 1.3 18.6 :I: 1.2 17.1 :I: 0.9 1-2 MILES OFFSITE lBI' 17.7 +/- 1.8 16.1 :1:1.1 21.3 :I: 1.4 19.0 ':I: 1.1 2B3 IS.9 :I: 0.8 . 16.6 :I: 0.9 ' 20.S :I: 0.4 18.8 :I: 0.6 2B4 17.5':1: 0.2 16.4 :I: 0.9' 2f.4 +/- 1.8' 19.1 :I: 1.1 5B3! 16.2::1: 1.4 14.6 ::1:'1.1 " 17.5 '+/- 1.2"
- 16.5 :1:2.2 "
7B2 : 17.3 ;:1:' 0.8 ' 15.7 :I: 0.9 18.7'+/- 1.0 ; 17.4";: cO:6 8B2 16.9 :I: '1.2" 15.1 :I: 1.1 18.1 ~:I: :1.4' 17.3 :1:'0.7' 9BI ~ 16.7 :1:'0.6, 15.6 :I: 1.3 18.9:1: '1.6 17.8':1:"1.5
- 10B2 14.8 :I: 1.6 12.7 :I: 1.3 16.7 :I: 0.8 14.9 :I: 1.5 lOB3 17.5 :I: 1.2 15.2 :I: 0.4 19.2 :I: 1.0 (4) 10B4 ' 18.0 :I: 1.6 18.0 :I: 1.5 20.4 :I: 1.0 20.4 :I: 1.1 '
12B4 18.3 :I: 1.0, 17.0 :I: 1.5 20.1 :I: 1.0 18.6 :I: 0.7 13Bl 18.4:1: 1.6 16.4 :I: 1.5 19.1 :I: 1.6 18.3 :1:,1.7' 14B3 IS.7 :I: 1.8 16.4 :I: 1.5 19.9 :I: 1.0 (4) 15Bl 17.1 :1:*1.8 16.0 :I: 1.1 18.9 :I: 1.4 18.0 :I: 2.4 16B2: 16.1,*:1:*0.8 15.4 :I: 1.9, 19.2 :I: 0.4 17.3:1: 0.7 t * .*
. i 2-3 MILES OFFSITE Hel 21.2 :I: 1.6 19.4 :I: 0.9 22.4 :I: 1.0 21.7 :I: 0.7 See the comments at the end of this table.
1-5 1-5
TABLE 1*1 TABLE 1-1 ENVIRONMENTAL THERMOLUMINESCENT ENVIRONMENTAL THERMOLUMINESCENT DOSIMETRY DOSIMETRY RESULTS RESULTS SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECIRIC ELECIRIC STATION STATION -- 2003 2003 Results (I)
Results (I) areare in in mR/std. qtr (2) mR/std. qtr +/- 2S (2) +/- 2S (3)
(3) .
Flnt Quarter Flnt Quarter Second Quarter Second Quarter Third Quarter Third Quarter . Fourtb Quarter Fourtb Quarter 01119/0J 01119/0J to to OSlO 1103 OSlO 1103 04119/03 04119/03 to to 07124/03 07124/03 0711210J 0711210J to to 101lJ/03 101lJ/03 101ll/OJ 101ll/OJ to to 01130104 01130104 Location Location 3-4 MILES 3-4 MILES OFFSITE OFFSITE 105 105 19.9 :!:
19.9 :!: 0.8 0.8 18.6 18.6 :!:
- !: 0.9 0.9 :!: 0.0 22.5 :!: 0.0 20.3 :!: l.1 20.3 :!: l.1 601 601 18.9 :!:
18.9 :!: 1.4 1.4 17.9 17.9 :!:
- !: 1.3 1.3 21.3 21.3 :!:
- !: 1.2 1.2 19.8 :!:
19.8 :!: '0.6
'0.6 803 803 18.6 :!:
18.6 :!: 1.2 1.2 17.3 17.3 :!:
- !: 0.6 0.6 19.1 19.1 :!:
- !: 0.8 0.8 18.1 :!:
18.1 :!: 1.11.1 904 904 18.4 :!:
18.4 :!: 1.6 1.6 17.7 17.7 :!:
- !: 1.1 1.1 20.4 20.4 :!:
- !: 2.6 2.6 18.8 :!:
18.8 :!: 1.31.3 1001 1001 18.5 :!:
18.5 :!: 1.2 1.2 16.7 16.7 :!:
- !: 1.3 1.3 19.9 19.9 :!:
- !: 1.2 1.2 :!: 2.4 18.3 :!:
18.3 2.4 1+02 1+02 21.2 :!:
21.2 :!: 1.8 1.8 19.9 19.9 :!:
- !: 1.1 1.1 22.0 22.0 :!:
- !: 2.4 2.4 21.5 :!:
21.5 :!: 0.90.9 1401 1401 19.9.:!:
19.9.:!: 1.2 1.2 17.9 17.9 :!:
- !: 1.5 1.5 20.7 20.7 :!:
- !: 2.4 2.4 20.3*:!: 1.7 1.7 4-5 MILES 4-5 MILES OFFSITE OFFSITE 3EI 3EI 15.7 15.7 :!:
- !: 0.6 0.6 14.9 +/-
14.9 +/- 1.71.7 18.6 18.6 :!: 1.5
- !: 1.5 16.2 16.2 +/- 0.6
+/- 0.6 4E2 4E2 19.2 19.2 :!:
- !: 1.6 1.6 18.8 +/-
18.8 +/- 0.60.6 21.7 21.7 +/- 1.4
+/- 1.4 ,, 19.6 19.6 +/- 0.7
+/- 0.7 5E2 5E2 18.0 18.0 :!:
- !: 1.4 1.4 16.3' +/-
16.3' +/- 1.5 1.5 20.9 20.9 +/- 2.0
+/- 2.0 18.9 18.9 +/- 0.7
+/- 0.7 6El 6El 20.5 20.5 :!:
- !: 2.2 2.2 20.1 20.1 +/-
+/- 0.6 0.6 21.6 21.6 :!: 1.0
- !: 1.0 20.7 20.7 :!: 1.7
- !: 1.7 7Et 7Et 18.7 18.7 :!:
- !: 2.0 2.0 17.5 17.5 :!:
- !: 0.6 0.6 20.5 20.5 +/- 1.0
+/- 1.0 IS.9 IS.9 :!: 1.3
- !: 1.3 llEt llEt 16.0 16.0 :!:
- !: 0.8 0.8 14.3 14.3 +/-
+/- 0.9 0.9 17.4 17.4 +/- 1.0
+/- 1.0 16.1 16.1 :!: 0.7
- !: 0.7 12El 12El 17.4 17.4 :!:
- !: 1.8 1.8 16.1 16.1 +/-
+/- 1.3 1.3 IS.6 IS.6 +/- 0.6
+/- 0.6 17.8 17.8 :!: 1.1
- !: 1.1 13E4 13E4 20.5 :!:
20.5 :!: 1.6 1.6 20.1 20.1 :!:
- !: 1.1 1.1 22.9 22.9 +/- 1.6
+/- 1.6 22.3 22.3 :!: 1.1
- !: 1.1 5-10 MILES 5-10 MILES OFFSITE OFFSITE 2Fl 2Fl 17.0 17.0 +/- 1.6
+/- 1.6 17.0 17.0 :!: 1.5
- !: 1.5 20.2 20.2 :!: 0.4
- !: 0.4 18.4 18.4 +/- 1.7
+/- 1.7 8F2 8F2 17.4 17.4 +/- 0.8
+/- 0.8 16.4 16.4 +/- 1.1
+/- 1.1 18.6 18.6 :!: 1.0
- !: 1.0 17.5 17.5 :!:
- !: 0.7 0.7 12F2 12F2 19.1 19.1 :!: 1.2
- !: 1.2 17.9 17.9 +/- 1.1
+/- 1.1 20.8 20.8 :!: 1.2
- !: 1.2 20.4 20.4 :!:
- !: 0.7 0.7 15Ft 15Ft 19.1 19.1 :!: 1.2
- !: 1.2 lS.7 lS.7 :!: 1.3
- !: 1.3 21.9 21.9 :!: ~.O
- !: 20.9 20.9 +/-
+/- 1.7 1.7 16Fl 16Fl 20.8 20.8 +/- 0.6
+/- 0.6 19.8 19.8 +/- 1.5
+/- 1.5 22.2 22.2 +/- 1.8
+/- 1.8 20.9 20.9 :!:
- !: 1.9 1.9 Sec the Sec the comments comments at at the the end end of of this this table.
table.
1-6 1-6
c c ENVIRONMENTAL ENVIRONMENTAL TIIERMOLUMINESCENT
('.
TABLEI-I TABLEI-I TIIERMOLUMINESCENT DOSIMETRY DOSIMETRY RESULTS II RESULTS SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRICELECTRIC STATION 20031 STATION -- 20031 Results (1)
Results (1) are are in in mRlstd.
mRlstd. qtr qtr (2) +/-2S (2) +/- 2S (3)
(3) ,
Fint Quarter Fint Quarter Second Quarter Second Quarter ThIrd Quarter ThIrd Quarter I Fourth Quarter Fourth Quarter II ii ;;
01129103 01129103 to 05/01103 to 05/01103 04129103 04129103 to to 07124103 07124103 07122103 07122103 to to 10113103 10113103 10121103 10121103 toto 01130/04 01130/04 Location Location
- l 1' 1 ';
10-20 MILES 10-20 MILES 3G4-3G4- 19.9 :f: '1.2 19.7 :f: 1.7 21.2 :f:
21.2 :f: 0.6 0.6 21.2 21.2 :f:
- f: 0.0 0.0 4Gl:
4Gl: 20.0 :f: *1.4 19.9 :f: 0.6 . 21.7 :f:
21.7 :f: 1.8 1.8 21.3 21.3 :f:
- f: 0.6 0.6 6Gl 6Gl 19.5 :f: 2.0 20.2 :f: 1.7 23.6 :f:
23.6 :f: 1.0 1.0 21.9 21.9 :f:
- f: 0.6 0.6 7G1.
7G1. 17.L:f: 1.2 16.5 :f: 0.9 19.1 :f:
19.1 :f: 1.0 1.0 18.5 18.5 :f:
- f: 0.6 0.6 7Gi 7Gi t:7.3~ +/-,1.0 , . 16.9 :f:. .' 0.4 20.2 :f:
20.2 :f: 0.7 0.7 18.8 18.8 :f:
- f: 1.9 1.9 8Gl 8Gl 15.9 :f: *1.0 .., 14.1 :f: 1.1 17.3 :f:
17.3 :f: 1.8 1.8 16.9 16.9 :f:
- f: 0.7 0.7 12GI 12GI 17.2 :f: 2.0 15.2 :f: 1.1 17.8 :f:
17.8 :f: 0.8 0.8 18.0 18.0 :f:
- f: 0.7 0.7 12G4 12G4 20.3 :f: 1.4 17.8 +/-*0.9 21.3*:f: 1.4 1.4 20.4 20.4 :f:
- f: 0.4 0.4
,: See the comments at the end ofthis table. U ! ....
'I. -. ,:.. ~
i'~ J',:1 !' !.: .~: ~ " .. " .
Location
. : Indicator
,. 'Average (5) ;i9:6'+/-' 11.8 :-"; 18.6 :f:', 12.9 . . 21.9 :f: 12.9 20.7 :f: 12.2
, t . ~ if ' " .:,~;
. Control
, Average (5) 18.4 :f: 4.1 17.5 :f:. 3.2 20.3 :f: 3.5 19.6 :f: 2.4 COMMENTS ". . . I (I) Individual mtmitor loCation resitt~'~re nonnallythe average of the elementai:d~ses of six calcium elements from the two liDs assigned to each monitoring loCation. ' . ~ f . . i (2) A standard (std.) quarter (qtr.) is considered to be 91.25 days. Results obtained fOT monitoring periods of other durations ate nonnalized by mUltiplying them x
. by 91.25/](, \Vheie is the actual dumtion in days ofthe period. " . I (3) Uncertainties 'fori~diVidual fu6nfioring location results are two standard deviations of the elemental doses of silt calcium elements from the two TLOs assigned to each monitoring location; representing the variability between the elemental doses of each of the six TLO eleml:nts.
, . " , .'.. " :.' .
I (5) Uncertainties assoCiated with quarterly indicator and control avemgeS are two standard deviations, representing the variability between the results of
. - the individual monitoring locations. . . . . . . . ,--.. - _. _..... . . , .. " -. . .,.! . ., . .
1-7
TABLE 1-2 TABLE 1-2 GROSS BETA, GROSS BETA, TRITIUM, TRITIUM, AND AND GAMMA GAMMA SPECTROSCOPIC SPECTROSCOPIC ANALYSES ANALYSES OF OF SURFACE SURFACE W~T~R SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION STATION -- 2003 2003 Results in Results +/- 2S in pC~itcr +/- 2S LOCATION LOCATION COLLECTION DATE COLLECTION DATE TRITIUM TRITIUM GR-BETA GR-BETA OTHER ACTIVITY OTHER ACTIVITY COMMENTS COMMENTS 6S6 6S6 12130/02 12130/02 01127/03 01127/03 <129
<129 1.9 1.9 +/-
+/- 1.2 1.2 2S7 2S7 12130/02 12130/02 01127/03 01127/03 170+/- 87.3 170+/- 87.3 15.9 15.9 +/-
+/- 2.9 2.9 6S5 6S5 01106/03 '
01106/03 01/27/03 01/27/03 <126
<126 3.2 3.2 +/-
+/- 1.4 1.4 LTAW' LTAW' 01l2qJ03 .
01l2qJ03 <149
<149 4.6 4.6 +/-
+/- 1.6 1.6 6S6 6S6 01127/03 01127/03 03/03/03 03/03/03 <135
<135 <2.01
<2.01 2S7 2S7 01127103 01127103 03/03/03 03/03/03 4770+/-
4770+/- 177177 8.3 8.3 +/-+/- 2.4 2.4 685 685 02103/03* 03/03/03 03/03/03 1310 +/-
1310 +/- 114 114 4.5 +/-
4.5 +/- 1.8 1.8 LTAWtt LTAW 02118103 02118103 246+/-90.1 246+/-90.1 3.7 +/-
3.7 +/- 1.6 1.6 6S6 6S6 . 03/03/03 03/03/03 03/31103 03/31103 <146
<146 4.3 4.3 +/-
+/- 1.5 1.5
- 287 287 03/03/03 03/03/03 03/31103 03/31103 16600 +/-307 16600 +/-307 9.9 9.9 +/-
+/- 2.2 2.2 685 685 03110/03 03110/03 03/31103 03/31103 < 149
< 149 3.2 3.2 +/-
+/- 1.4 1.4 LTAW LTAW 03117/03 03117/03 <147
<147 4.0 4.0 +/-
+/- 1.4 1.4 686 686 03/31103 03/31103 04128/03 04128/03 <134
<134 <1.87
<1.87 687 687 , 03/31103 03/31103 04128/03 04128/03 293 +/-91.7 293 +/-91.7 7.2 7.2 +/-+/- 2.1 2.1 685' 685' 04/07/03 04/07/03 04/28/03 04/28/03 <123
<123 2.6 +/-
2.6 +/- 1.4 1.4 LTAW LTAW 04/14/03 04/14/03 244 +/-
244 87.5
+/- 87.5 2.6 +/-
2.6 +/- 1.4 1.4 6S6 6S6 04/28/03 04/28/03 06/02103 06/02103 <141
<141 <1.76
<1.76 287 287 04/28/03 04/28/03 06/02103 06/02103 261 +/- 95.3 261 +/- 95.3 10.9 10.9 +/-+/- 2.4 2.4 685 685 05/05/03 05/05/03 06/02103 06/02103 <142
<142 3.9 .+/- 1.4 3.9 .+/- 1.4 LTAW LTAW 05112/03 05112/03 225 +/-
225 +/- 92.7 92.7 3.7 +/-
3.7 1.6
+/- 1.6 6S6 6S6 06/02103 06/02103 06130/03 06130/03 <134
<134 <1.88
<1.88 2S7 2S7 06/02103 06/02103 06/30/03 06/30/03 3790 3790 +/-+/- 166 166 7.1 7.1 +/-+/- 2.1 2.1 6SS 06/09/03 06/09/03 06/30/03 06/30/03 <140
<140 3.1 +/-
3.1 +/- 1.4 1.4 LTAW LTAW 06/09/03 06/09/03 192 +/-
192 +/- 95.7 95.7 3.6 +/-
3.6 1.6
+/- 1.6 Comments:
Comments:
Appendix F
- Rer~ jj Appendix F of of this this report report for for additional additional details details regarding regarding except(
except( to to SSES SSES Technical Technical Requirements Requirements for for sampling sampling and and analyses.
analyses. C C 1-8 1-8
.. C C ,,;
TABLE 1-2 TABLE 1-2
((
GROSS BETA, GROSS BETA, TRITIUM, TRITIUM, AND AND GAMMA GAMMA SPECTROSCOPIC SPECTROSCOPIC ANALYSES ANALYSES OF OF SURFACE SURFACE WATER WATER SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELEcrRiC ELEcrRiC STATION STATION -- 2003 2003 ii Results in Results in pCilliter +/-2S pCilliter +/-2S j
~ . .:
((
~ ,,
LOCATION LOCATION COLLECTION DATE COLLECTION DATE ' TRITIUM TRITIUM GR-BETA GR-BETA OTHER ACTIVITY OTHER ACTIVITY COMMENTS COMMENTS 6S6 6S6 06130/03 06130/03 07128103 07128103 <146 3.0 3.0 +/-
+/- 1.5 1.5 2S7 2S7 06/30/03 06/30/03 07128103 07128103 182 +/-97.6 11.8 11.8 +/-
+/- 2.5 2.5 6SS ,
6SS 07/07/03 07/07/03 .. 07128103 07128103 ,: <150 2.8 2.8 +/-
+/- 1.5 1.5 LTAW . ,
LTAW 07114/03 07114/03 - I
- I JJ --
' :. <129 2.8 2.8 +/-
+/- 1.3 1.3 6S6 6S6 07128/03 07128/03 08125103 08125103 <132
<132 4.2 +/-
4.2 +/- 1.6 1.6 2S7 2S7 07/28/03 07/28/03 08125103* 9800 9800 +/-257 +/-257 11.8 11.8 +/-.2.S+/-.2.S 6SS 6SS 08/04/03 08/04/03 08125103 08125103 <128* 4.2 4.2 +/- +/- 1.6 1.6 LTAW, LTAW, 081l 1/03 081l 1/03 . , : .! 'i 163 +/- 94.2 4.1,+/- 1.6 4.1,+/- 1.6
'. t' J.'" 1 6S6 6S6 08/25/03 08/25/03 ' 09129103 ' . ! . ' : 137 +/- 71.2 J 2.8 2.8 +/-
+/- 1.3 1.3 2S7 '....
2S7 08125103 _ 09129/03 ,,135 +/- 72.2 08125103 )) 1.9 1.9 +/-
+/- 2.3 2.3 6S5 6S5 09/02103 ir,~ '09i2'9/03 .,:: ,': 'J <:114 09/02103
- I " - i _. ~ - ( ,/ , * '
3.8,,
3.8 +/-,,
+/-
1.4 1.4 LTAW,' . I' 09/08/03 ".: :,;,,':, ", 213+/-94.2 09/08/03 '4.7
'4.7 +/-
+/- 1.5 1.5
'" * . J.'
6S6 6S6 09129/03 09129/03 11103/03 11103/03 <122
<122 ~.2 +/-+/- 1.4 1.4 I;:
2S7 2S7 '"
09129/03 09129/03 11103/03' 11103/03' '~ 15800 15800 +/- +/- 268 268 13.7 13.7 +/- +/- 2.6 2.6 6S5 6S5 10/06/03 10/06/03 11103/03 11103/03 <114
<114 4.2+/- 1.5 4.2+/- 1.5 LTAW LTAW 10/13/03 10/13/03 147+/-82.8 147+/-82.8 3.9 +/-
3.9 +/- 1.5 1.5 6S6 6S6 11103/03 11103/03 12101103 12101103 <124
<124 2.7 2.7 +/-
+/- 1.3 1.3 2S7 2S7 tt tl03/03 tl03/03 12101103 12101103 231 231 +/- +/- 89.3 89.3 )) 1.8 1.8 +/-
+/- 2.4 2.4 6S5 6S5 11110/03 11110/03 12101103 12101103 <123
<123 3.1 3.1 +/-
+/- 1.3 1.3 LTAW* 11110/03 11110/03 293 +/-
293 +/- 86.7 86.7 3.9 3.9 +/-
+/- 1.3 1.3 6S6 6S6 12101103 12101103 12129/03 12129/03 <132
<132 2.2 2.2 +/-
+/- 1.2 1.2 2S7 2S7 1210tl03 1210tl03 12129/03 12129/03 <128
<128 12.2 12.2 +/-
+/- 2.4 2.4 6S5 6S5 12108/03 12108/03 12129103 12129103 <134
<134 2.4 2.4 +/-
+/- 1.3 1.3 LTAW LTAW 12115103 12115103 <120
<120 3.3 3.3 +/-
+/- 1.4 1.4
. I Comments:
Comments:
"Refer to "Refer to Appendix Appendix F F of of this this report report for for additional additional details regarding exception~'to SSES details regarding TechnIcal Requlr~ments for SSES TechnIcal for sampling sampling and and analyses.
analyses. 1-9 1-9
TABLE TABLE 1-3 1-3 IODlNE-131 ANALYSES IODlNE-131 ANALYSES OF OF SURFACE SURFACE WATER WATER SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECTRICELECTRIC STATION STATION -- 2003 2003 Results in Results in pCiIliter +/- 2S pCiIliter +/- 2S
. I LOCATION LOCATION COLLECTION DATE COLLECTION DATE 1-131 1-131 COMMENTS COMMENTS 6S6 6S6 12/30/02 -- 01113/03 12/30/02 01113/03 .01 :i: .15
.01 :i: .15 2S7 2S7 12130/02 -- 01113/03 12130/02 01113/03 .21 :i:
.21 :i: .29
.29 6S5 6S5 01106/03 &
01106/03 01/13/03
& 01/13/03 .24:i: .25
.24:i: .25 6S6 6S6 01127/03 01113/03 -- 01127/03 01113/03 .33 :i: .31
.33 :i: .31 2S7 2S7 01113/03 -- 01127/03 01113/03 01127/03 .21 :i:
.21 :i: .29
.29 6S5 6S5 01/20/03 &
01/20/03 01127/0J
& 01127/0J .25:i: .23
.25:i: .23 LTAW LTAW 1120/2003 1120/2003 -.01 :i:.ll
-.01 :i:.ll 6S6 6S6 01/27/03 -- 02110103 01/27/03 02110103 .11 :i:
.11 :i: .21
.21 2S7 2S7 01127/03 -- 02110/03 01127/03 02110/03 1.33:i:
1.33:i: .58 .58 6S5 6S5 02l0J/03 &
02l0J/03 02110/03
& 02110/03 .J9:i: .33
.J9:i: .33 LTAW LTAW 211812003 211812003 .1O:i:.12
.1O:i:.12 6S6 6S6 02110/03 -- 02124/03 02110/03 02124/03 .72:i: .30
.72:i: .30 2S7 2S7 02110/03 -- 02124/03 02110/03 02124/03 1.61 :i:.46 1.61 :i:.46 6S5 6S5 02118/03 &
02118/03 & 02124/0J 02124/0J .31 :i:
.31 :i: .29
.29 6S6 6S6 03/1 O/OJ 02124/03 -- 03/1 02124/03 O/OJ .64:i: .41
.64:i: .41 2S7 2S7 02124/03 -- 03/10/03 02124/03 03/10/03 1.24:i:
1.24:i: .53 .53 6S5 6S5 03/0J/03. &
03/0J/03. 03/10/03
& 03/10/03 .80:i: .39
.80:i: .39 LTAW LTAW 3/17/2003 3/17/2003 <0.18
<0.18 6S6 6S6 03/10/03 -- 03/24/03 03/10/03 03/24/03 .16:i:
.16:i: .21.21 2S7 2S7 03/10103 -- 03/24/03 03/10103 03/24/03 .77:i: .42
.77:i: .42 6S5 6S5 03/17/03 &
03/17/03 & 03/24/03 03/24/03 .30:i: .29
.30:i: .29 6S6 6S6 03/24/03 -- 04107103 03/24/03 04107103 .05:i:
.05:i: .12.12 6S7 6S7 03124/03 -- 04107/03 03124/03 04107/03 .52:i: .32
.52:i: .32 6S5* 04/07i03 03/31/03*'& 04/07i03 <0.43
<0.43 LTAW LTAW 4/14/2003 4/14/2003 .05:i: .15
.05:i: .15 Comments:
Comments:
- Re('1 Appendix
- Re('1 F of Appendix F of this this report report for for additional additional details details regarding regarding exceptr-exceptr- to to SSES SSES Technical Technical Requirements Requirements for for sampling sampling and and analyses.
analyses. (( 1-10 1-10
c .C',)
TABLE 1-3 TABLE 1-3 IODlNE-131 ANALYSES OF IODlNE-131 ANALYSES OF SURFACE SURFACE WATER WATER SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECfruCELECfruC STATION* 2003 2003 Results in Results in pCilliter +/- 2S pCilliter +/- 2S LOCATION LOCATION COLLECTION DATE COLLECTION DATE 1-131 1-131 COMMENTS COMMENTS 6S6 6S6 04/07/03 -- 04/21103 04/07/03 04/21103 .06:1:
.06:1: .17.17 2S7'"
2S7'" 04/07/03 -- 04121103 04/07/03 04121103 .59:1: .36
.59:1: .36 6S5 6S5 04114/03 &
04114/03 & 0412 1103.
0412 1103. 0:1: .21
.1 0:1:
.1 .21 6S6 6S6 04/21103 -- 05105103 04/21103 05105103 .32:1: .32
.32:1: .32 2ST 04/21103 -- 05/05/03 04/21103 05/05/03 .53 +/-,41 ..
.53 +/-,41 6S5 6S5 04128103 &
04128103 05/05/03
& 05/05/03 .14:1: .20
.14:1: .20 LTAW LTAW ,, '511212003
'511212003 O.OO:l:.t 11 O.OO:l:.t
~. :
6S6 6S6 05105103- 05119103 05105103- 05119103 .50:1: .39
.50:1: .39 2S7 2S7 05/05/03 -- 05119103 05/05/03 05119103 1.19:1:
1.19:1: .60 .60 6S5,', ,',., 05112103 '&:05119/03 05112103 '&:05119/03 .06 :1:'.20
.06 :1:'.20 6S6' 6S6' 05/19/03'- 06/02103' 05/19/03'- 06/02103' .61':1: .38"
.61':1: .38" 2S7:
2S7: 05/19103;. 06/02/03 05/19103;. 06/02/03 Un'+/-.50 Un'+/-.50 6S5 6S5 05127/03 &
05127/03 06/02103
& 06/02103 .30:1: .24
.30:1: .24 6S6 6S6 06/02/03- 06/16103; 06/02/03- 06/16103; .18 :1:.26
.18 :1:.26 6S7 6S7 06/02/03 -- 06/16/03 06/02/03 06/16/03 .48 +/-
.48 .38
+/- .38 6S5 6S5 06/09/03 &
06/09/03 06/16/03
& 06/16/03 .28+/- .28
.28+/- .28 LTAW LTAW 61912003' ,,
61912003' .16:1: .25
.16:1: .25 6S6 6S6 06/16/03 -- 06130103 06/16/03 06130103 :: .47:1: .36
.47:1: .36 2S7' 2S7' 06/16/03 '.'. 06130103 06/16/03 06130103 Lt8 Lt8 +/- +/- .53 .53 6S5 6S5 06123/03 &.
06123/03 06/30/03
&. 06/30/03 .15:1: .19
.15:1: .19 6S6 6S6 06/30/03 06/30/03 '*07/14/03 .39:1:
.39:1: .33.33 2S7 2S7 06/30/03*07114/03 .91 :I:
.91 .50
- I: .50 6S5 6S5 07/07/03 &,07114/03 07/07/03 &,07114/03 .16:1: .23
.16:1: .23 .!
LTAW LTAW 711412003 711412003 .to+/- .22
.to+/- .22 , i Comments:
Comments: , I "Refer to "Refer to Appendix Appendix FF of of this this report report forfor additional additional details details regarding regarding exceptions exceptions to to SSES Technical Requlr~ments for SSES Technical for sampling sampling and and analyses.
analyses. 1-11 1-11
TABLE 1*3 TABLE IODlN~131 ANALYSES ANALYSES OF OF SURFACE SURFACE WATER WATER SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION STATION -- 2003 2003 Results in Results in pCiIliter +/- 2S pCiIliter +/- 2S LOCATION LOCATION COLLECTION DATE COLLECTION DATE 1-131 1-131 COMMENTS COMMENTS 6S6 6S6 07/14/03 07128103 07/14/03 -- 07128103 .27+/-.26
.27+/-.26 2S7 2S7 07/14/03*07/28/03 1.15 1.15 +/-+/- .51
.51 6S5 6S5 07/21103 &
07/21103 07/28/03
& 07/28/03 .9S+/- .52
.9S+/- .52 6S6 6S6 07128103 -- 08/11103 07128103 08/11103 .19+/-
.19+/- .23.23 2S7 2S7 07/28/03 -- 08111103 07/28/03 08111103 .40+/- .32
.40+/- .32 6S5 6S5 08/04/03 &
08/04/03 08/11103
& 08/11103 .19 +/-
.19 +/- .19
.19 LTAW LTAW 8/1112003 8/1112003 .12 +/-
.12 +/- .23
.23 656 656 08/11103 -- 08/25/03 08/11103 08/25/03 .04 +/-.19
.04 +/-.19 257 257 08111103 -- 08/25/03 08111103 08/25/03 .63 +/-
.63 +/- .38
.38 655 655 08/18/03 &
08/18/03 08125103
& 08125103 .09+/-.23
.09+/-.23 656 656 08/25103 -- 09/08/03 08/25103 09/08/03 .26+/- .29
.26+/- .29 2S7 2S7 08/25/03 -- 09/08/03 08/25/03 09/08/03 1.42+/-
1.42+/- .62 .62 6S5 6S5 09/02103 &
09/02103 09/08/03
& 09/08/03 .24+/-.24
.24+/-.24 LTAW LTAW 91812003 91812003 <0.24
<0.24 656 656 09/08103 -- 09/21J03 09/08103 09/21J03 .31 +/-
.31 +/- .29
.29 257 257 09/08/03 -- 09/21J03 09/08/03 09/21J03 .13
.13 +/-+/- .25
.25 655" 655" 09/15/03 &
09/15/03 09/21J03
& 09/21J03 .07 +/-.lS
.07 +/-.lS 6S6 6S6 09/21J03 -- 10/06/03 09/21J03 10/06/03 .15
.15 +/-+/- .25
.25 2S7 2S7 09121J03 -- 10/06103 09121J03 10/06103 <0.45
<0.45 685 685 09/29/03 &
09/29/03 10/06103
& 10/06103 .02+/-.l6
.02+/-.l6 6S6 6S6 10/6/03 -- J0/20/03 10/6/03 J0/20/03 <0.34
<0.34 257 257 JO/06/03 -- JO/20/03 JO/06/03 JO/20/03 .05+/-.22
.05+/-.22 655 655 10113/03 &
10113/03 10120/03
& 10120/03 <0040
<0040 LTAW LTAW 10/13/2003 10/13/2003 .19 +/-
.19 +/- .27
.27 comments:
comments:
- Retr t~ Appendix
- Retr Appendix F F of of this this report report for for additional additional details details regarding regarding exceptigpQ exceptigpQ to to SSES SSES Technical Technical Requirements Requirements for for sampling sampling and and analyses.
analyses. 1-12 1-12
-', .. ~ L L
TABLE 1-3 TABLE 1-3 IODINE-Ill ANALYSES IODINE-Ill ANALYSES OF OF SURFACE SURFACE WATER WATER SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRICELECTRIC STATION STATION -- 2003 2003
.'.' Rcsuhs Rcsuhs in in pCilliter +/- 2S pCilliter +/- 2S 1 .
LOCATION LOCATION COLLECTION DATE COLLECTION DATE 1-131 1-131 COMMENTS COMMENTS 6S6 6S6 10/20/03 -- 11103/03 10/20/03 11103/03 .15 :!:
.15 .27
- !: .27 2S7 2S7 10/20/03 -- tt 1103103 10/20/03 1103103 1.91 1.91 :!: :!: .70
.70 6SS 6SS 10127/03 &
10127/03 11103/03
& 11103/03 .26:!: .23
.26:!: .23 LTAW LTAW 1111012003 1111012003 <OAI
<OAI 6S6 6S6 11/03/03 -- 11/17/03 11/03/03 11/17/03 .31 :!: .51
.31 :!: .51 2S7 2S7 11103103 -- 11117/03 11103103 11117/03 .68:!: .60
.68:!: .60 6SS 6SS 11110/03 ..&
11110/03 11117103
& 11117103 .24:!: 044
.24:!:
6S6 6S6 .. : 1111'7/03 12101103 '
1111'7/03 -- 12101103 .14:!:
.14:!: .26.26
, 2S7 2S7 , 1111 7/03 1111 12101103 .
7/03 -- 12101103 .23:!: .29
.23:!: .29 11124/03\ && 12101103 t '/'
6SS 6SS " - 11124/03\ 12101103 . .01 :!:
.01 .IS
- !: .IS
- - ::-, 1'2101/03-12115/03 J: -- 1'2101/03-12115/03 6S6 6S6 " :': .21 :!:
.21 :!: .50
.50 2S7 2S7 12101103 -- 12115/03 12101103 12115/03 1.02+/-.64.
1.02+/-.64.
6SS 6SS 12108/03 &
12108/03 12115/03
& 12115/03 .32:!: AS
.32:!:
LTAW LTAW 1211512003 1211512003 .33:!: AS
.33:!:
6S6 6S6 .. 12115/03 12115/03 -- 12129/03 12129/03 .15:!: 046
.15:!: 046 2S7 2S7 12115103 -- 12129/03 12115103 12129/03 .92:!: .78
.92:!: .78 6S5 6S5 12122103 &
12122103 12129/03
& 12129/03 .27:!: .45
.27:!: .45 Comments:
Comments:
"'Refer to
"'Refer to Appendix Appendix FF of of this this report report for for additional additional details details regarding regarding exceptions exceptions to to SSES SSES Technical Technical Requirements Requirements for for sampling sampling and and analyses.
analyses. 1-13 1-13
TABLE 1-4 TABLE 1-4 GROSS ALPHA, GROSS ALPHA, GROSS GROSS BETA, BETA, TRITIUM, TRITIUM, IODlNE-t31 IODlNE-t31 GAMMA*
GAMMA* SPECTROSCOPIC SPECTROSCOPIC ANALYSES ANALYSES OF OF D.,.RINKING D.,.RINKING WATER WATER SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION STATION -- 2003 2003 Results in Results in pCiIliter pCiIliter ::I:: 2S
<1.24 +/-.9 1.86 +/-.9 1.86 <127
<127 12H2 12H2 01/27/03 -- 03/03/03 01/27/03 03/03/03 <1.62
<1.62 2.7:i: 1.4 2.7:i: 1.4 <135
<135 12H2 12H2 03/03/03 -- 03/31103 03/03/03 03/31103 . <1.30
<1.30 2.19:i: 1.3 2.19:i: 1.3 <142
<142 12H2 12H2 04/07/03 -- 04128103 04/07/03 04128103 <1.74
<1.74 <1.87
<1.87 <130
<130 **
12H2 12H2 04/28/03 -- 06/02103 04/28/03 06/02103 <1.87
<1.87 <1.90
<1.90 <141
<141 12H2 12H2 06/02/03 -- 06/30/03 06/02/03 06/30/03 <1.53
<1.53 2.04:i: 1.3 2.04:i: 1.3 <134
<134 12H2 12H2 06/30/03 -- 07/28/03 06/30/03 07/28/03 <1.90
<1.90 <2.01
<2.01 <133
<133 12H2 12H2 07/28/03 -- 08/28/03 07/28/03 08/28/03 <1.06
<1.06 3.54+/- 1.4 3.54+/- 1.4 <146
<146 12H2 12H2 08/25/03 -- 09/29/03 08/25/03 09/29/03 <1.07
<1.07 2.29:i: 1.3 2.29:i: 1.3 193 +/-72 193 +/-72 12H2 12H2 09/29/03 -- 11103103 09/29/03 11103103 <1.78
<1.78 4.26 +/-
4.26 +/- 1.4 1.4 <119
<119 12H2 12H2 11103/03 -- 12101103 11103/03 12101103 <1.55
<1.55 <1.57
<1.57 149 :i:
149 :i: 76 76 12H2 12H2 12101103 -- 12129/03 12101103 12129/03 <1.68
<1.68 2.01 +/-
2.01 +/- 1.2 1.2 <128
<128 Comments:
Comments:
- Refer Refer to to Appendix Appendix F F of of this this report report for for additional additional details details regarding regarding exceptions exceptions to to SSES SSES Technical Technical Requirements Requirements for for sampling sampling and and analyses.
analyses.
1-14 1-14
(
TABLE 1-5 TABLE 1-5 GROSS BETA GROSS BETA AND AND GAMMA GAMMA1r1r SPECTROSCOPIC SPECTROSCOPIC ANALYSES ANALYSES OF OF FISH FISH SUSQUEHANNA SUSQUEHANNA STEAMSTEAM ELECTRIC ELECTRIC STATION STATION -- 2003 2003 Results in Results in pCi/gm pCi/gm (wet) +/-2S (wet) +/-2S .
LOCATION LOCATION SAMPLE TYPE SAMPLE TYPE COLLECTION DATE COLLECTION DATE K-40 K-40 COMMENTS COMMENTS IND IND Smallmouth Bass Smallmouth Bass 04/28/03 -- 04128103 04/28/03 04128103 4.lS::!: .37 4.lS::!: .37 IND '
IND Shorthead Redhorse Shorthead Redhorse 04/28/03 -- 04/28/03 04/28/03 04/28/03 ~.39::!:.43 IND IND Channel Catfish Channel Catfish 04/29/03 04/30/03 04/29/03 -- 04/30/03 3.89:1:.33 3.89:1:.33 2H 2H Smallmouth Bass Smallmouth Bass 05/12/03 -- 05112103 05/12/03 05112103 3.92:1: .28 3.92:1: .28 2H 2H Shorthead Redhorse Shorthead Redhorse 05/12103 -- 05/12103 05/12103 05/12103 3.20:1:.26 3.20:1:.26 2H 2H Channel Catfish Channel Catfish 05112/03 -- 05/13/03 05112/03 05/13/03 3.49:1: .25 3.49:1: .25
,IND
,IND Channel Catfish Channel Catfish 10/07/03 -- 10108/03 10/07/03 10108/03 3.69:1:.33 3.69:1:.33 IND IND Smallmouth Bass Smallmouth Bass 10/08/03 10/08/03 10/08/03 -- 10/08/03 3.99:1:.37 3.99:1:.37 IND IND White Sucker, White Sucker, 10/08/03 -- 10/08/03 10/08/03 10/08/03 '1.30::!: .14
'1.30::!: .14 2H 2H Channel Catfish Channel Catfish 10115/03 -- 10116/03 10115/03 10116/03 3.44:1:.37 3.44:1:.37 2H 2H Smallmouth Bass Smallmouth Bass 10116/03 -- 10116/03 10116/03 10116/03 1.30::!: .24 1.30::!: .24 2H 2H White Sucker White Sucker 10116/03 -- 10116/03 10116/03 10116/03 3.58::!:.24 3.58::!:.24
,, LTAW LTAW , L~rge~outh Bass Bass 10/20/03 -- 10/20/03 10/20/03 10/20/03 3.67::!: .30 3.67::!: .30 -'-'
, ) , ,
I' ;!
1-15 1-15
TABLE 1-6 TABLE 1-6 GAMMA** SPECTROSCOPIC GAMMA SPECTROSCOPIC ANALYSES ANALYSES OF OF SHORELINE SHORELINE SEDIMENT SEDIMENT SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION STATION -- 2003 2003 Results in Results in pCi/gm pCi/gm (dry) +/- 2S (dry) +/- 2S LOCATION LOCATION COLLECTION DATE COLLECTION DATE K-4O K-4O Cs-137 Cs-137 Ra-226 Ra-226 TH-228 TH-228 OTHER ACTIVITY OTHER ACTIVITY 2B 2B 5/2012003 5/2012003 17.3 :!:.8 17.3 :!:.8 .11 :!: .03
.11 :!: .03 2.45:!: .65 2.45:!: .65 4.74:!: .67 4.74:!: .67 7B 7B 5/2012003 5/2012003 15.8:!: .5 15.8:!: .5 .1O:!: .02
.1O:!: .02 2.86+/-.59 2.86+/-.59 3.56:!: .54 3.56:!: .54 12F 12F 5/20/2003 5/20/2003 11.8 +/-.8 11.8 +/-.8 .09+/-.04
.09+/-.04 2.12+/-.85 2.12+/-.85 3.34 +/-.82 3.34 +/-.82 LTAW LTAW 512012003 512012003 15.8:!: .8 15.8:!: .8 <.03
<.03 1.96:!: .61 1.96:!: .61 3.21 +/-.60 3.21 +/-.60 2B 2B 10/27/2003 10/27/2003 7.22+/-.24 7.22+/-.24 .04
.04 +/-+/- .01
.01 .75+/-.16
.75+/-.16 1.28:!: .18 1.28:!: .18 7B 7B 10127/2003 10127/2003 13.6:!: .5 13.6:!: .5 .07:!: .02
.07:!: .02 2.36+/-.46 2.36+/-.46 3.47:!: .43 3.47:!: .43 12F 12F 10/27/2003 10/27/2003 lOA +/-.4 lOA +/-.4 <.02
<.02 2.17+/- .40 2.17+/- .40 2A6:!: .38 2A6:!: .38 LTAW LTAW 10127/2003 ..
10127/2003 14.7:!: A 14.7:!: A <.ot
<.ot 2.18+/- .37 2.18+/- .37 3.23 +/-.41 3.23 +/-.41 1-16 1-16
c TABLEI-7 TABLEI-7
(
TRITIUM AND TRITIUM GAMMA ** SPECTROSCOPIC AND GAMMA SPECTROSCOPIC ANALYSES ANALYSES OFOF GROUND GROUND WATER WATER SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECfRlC ELECfRlC STATION STATION -- 2003 2003 Results in Results in pCiniter +/-28 pCiniter +/-28 LOCATION LOCATION COLLECTION DATE COLLECTION DATE TRITIUM TRITIUM OTHER ACTIVITY OTHER ACTIVITY 12F3 12F3 1/2012003 1/2012003 <145
<145 282 282 112012003 112012003 <149
<149 484 Treated 484 Treated 1120/2003 1120/2003 <140
<140 12F3 12F3 2118/2003 2118/2003 <135
<135 282 282 2/18/2003 2/18/2003 <137
<137 484 Treated 484 Treated 2/18/2003 2/18/2003 178 +/-
178 +/- 87.3 87.3 12F3 12F3 311712003 311712003 <143
<143 282 282 311712003 311712003 <141
<141 484 Treated 484 Treated 3/17/2003 3/17/2003 <143
<143 12F3 12F3 4/14/2003 4/14/2003 <131
<131 282 282 411412003 411412003 167 167 +/-+/- 83.1 83.1 484 Treated 484 Treated 4114/2003 4114/2003
, .... , ., 142+/-83.2 142+/-83.2
\
i"t
-" '. ~ ;. .' ,'-:'
\.
12F3 12F3 5/12i2003 ' ,<136
,<136 ::
282
282 5/1212003
5/1212003 <136'
<136' 484 Treated 484 Treated 511212003 511212003 <137
<137 12F3 12F3 6/9/2003 6/9/2003 :~ <146
<146 282 282 6/9/2003 ..
6/9/2003 <145
<145 484 Treated 484 Treated 6/9/2003 6/9/2003 <146
<146 12F3 12F3 711412003 711412003 <147
<147 282 282 7114/2003 ..
7114/2003 <137
<137 484 Treated 484 Treated 7/14/2003 7/14/2003 <143
<143 12F3 12F3 811112003 811112003 <138
<138 282 282 8/1112003 8/1112003 <140
<140 484;Treated --
484;Treated 811112003 811112003 <139
<139 1-17 1-17
TABLE 1-7 TABLE 1-7 TRITIUM AND TRITIUM AND GAMMA* SPECTROSCOPIC SPECTROSCOPIC ANALYSESANALYSES OF OF GROUND GROUND WATER WATER SUSQUEHANNA STEAM ELECTRIC SUSQUEHANNA STEAM ELECTRIC STATION STATION -- 2003 2003 Results in
. Results in pCiltitcr +/- 2S pCiltitcr +/- 2S LOCATION LOCATION COLLECTION DATE COLLECTION DATE TRITIUM TRITIUM OTHER ACTIVITY OTHER ACTIVITY 12F3 12F3 9/8/2003 9/8/2003 <139
<139 2S2 2S2 91812003 91812003 <138
<138 4S4 Treated 4S4 Treated 9/8/2003 9/8/2003 193 +/-
193 89.6
+/- 89.6
'. ~ " .,.
12F3 12F3 10113i2003 101 13i2003 <125
<125 2S2 2S2 10113/2003 10113/2003 <124
<124 4S4 Treated 4S4 Treated 10/13/2003 10/13/2003 <122
<122 12F3 12F3 1111012003 1111012003 <127
<127 2S2 2S2 11110/2003 11110/2003 <122
<122 4S4 Treated 4S4 Treated 11110/2003 11110/2003 <125
<125 12F3 12F3 12/15/2003 12/15/2003 <121
<121 2S2 2S2 1211512003 1211512003 <120
<120 4S4 Treated 4S4 Treated 12115/2003 12115/2003 <126
<126 1-18 1-18
(~ ( (~
-,(
TABLE I~8 TABLE
/'i
'I GROSS BETA GROSS BETA ANALYSES ANALYSES OF OF AIRAIR PARTICULATE PARTICULATE FILTERS FILTERS SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATIONSTATION -- 2003:2003:
Results in Results in E-03 E-03 pCilCu.
pCilCu. M. +/- 2S M. +/- 2S ::
COLLECTION COLLECTION .. ..
MONTH DATE MONTH DATE 1'1"':
1'1"':
'6Gl
'6Gl 8Gl 8Gl 3S2 3S2 12El 12El 12S1 12S1 ii II
'13S6
'13S6 COMMENTS COMMENTS JAN 112103 ~ 'tl8/03 " 12.8 +/- 2.2 1l~1' +/- 2.3 14.6 +/- 2.8 13.6 +/- 2.5 1 ' 13J +/-2.6 10.8 +/- 2.3 118/03 - tl15/03 14.3 +/- 2.1 14.2 +/- 2.2 13.8 +/- 2.3 15.9 +/- 2.2 13.7 +/- 2.2 16.0 +/- 2.3 1IIS/03'~ i/22103 14 +/- 2.2 18.6.:l: 2.5 20.6 +/- 2.8 18.7 +/- 2.5 17:6 :!: 2.5 16.3 d:: 2.4 1122103 ',: 1129/03 14:1 +/-2.3 14.6:l: 2.3 17.3 +/- 2.6' 15.7 ~+/- 2.3 18.2 ':!: 2.5 17.1 +/- 2.4
. I; FEB 1129/03 ~'21si03 "
13:8 :!: 2.3 ' :
16.2 +/- 2.4 15.7 +/- 2.3 15.2 +/- 2.4 16.7 :!: 2~6 15.2 :!: 2.3 215/03 - 2/12103 :' 14.8 '+/- 2.2 16.2 :!: 2.4 17.8' ':!: 2.4 17.5 :!: 2.3 17.8 +/- 2.4 18.1 +/- 2.4 2/12/03 - 2119/03 9.9 +/- 2.0 12.2 +/- 2.1 14.2 +/- 2.2 14.2 +/- 2.2 14.9 +/- 2.2 14.1 +/- 2.2 2119/03 - 2126103 '" 12~6 +/- 2,3 , 17.7 '+/- 2.5 19:2 +/- 2.3 16.0 +/- 2.4 14:9 :!: 2.4 16. I :!: 2.4 MAR 2126/03 .; 3/5103 . 14:5 '+/- 2.3 ' 18.8 '+/- 2.6 19.7 +/- 2.6 17.9 +/- 2.5 18.1 ' +/- 2.5. i! 19.5 +/- 2.6
\ : ',3/5/03 - 3/12103'" 2 1'.6 '+/- 2.7 . 19.4 '+/- 2.5 25.9' '+/- 2.8 18.2 +/- 2.5' I 23~6+/- 2.8 : 18.6 +/- 2.5 3112103 - 3/19/03 18.3 +/- 2.5 17.8 +/- 2.4 17.6 :!: 2.4 17.9 +/-2.4 18.4 :!: 2.6 18.4 :!: 2.5 3/19/03\.2 3/26/03' ~ 100.4'+/- 2.1 10'.5 :l: 2.0 " 12.6 +/- 2.S" 9:8 ' *+/-2.0' 11.8 ':+/- 2.2 ) 11:' +/- 2.1 '
3126/03 .: 4/2103, ' ' 9:5 '+/- 2.0:.'
10:7 .. +/- 2.~
If.!> '+/- 2.0' 10.5 -+/- 2.0 12.6+/- 2.1'"
. , i ,1 10.4 '+/- 2.0 II '.',
APR" 412103 - 4/9/03 .~ 1 7.6"+/- 1.9 " 9:6 ':l: 2.0 ,: 9:5 +/- t() 1 "
10.0 . +/- 2.0 9.9 :!: 2.1 i 9.6 +/- 2.0 4/9/03 - 4116/03 13.0 +/- 2.2 15.9 +/- 2.3 14.3 +/- 2.1 14.7 :!: 2.2 12.7 :!: 2.1 14.3 :!: 2.2 4/16/03:' 4/23/03 10.5' +/- 2.0 13.6 +/- 2.1 IS.0+/- 2.3 12.8 +/- 2.1 14,3 +/- 2.2 13.3 +/- 2.1 4123/03 - 4/30/03 : 11.3 +/- 2.0 14.7 '+/- 2.2 15.3 :!: 2.3 11.4 +/- 2.0 13.3 +/- 2.2 12.8 :l: 2.1 MAY 4/30/03 ..: 517/03 9:4 ,.:!: 2.1 : 10.5 :!: '2.1 13.5+/- 2.4 10.5 +/- 2.2 11.1 :!: 2.3 I
11.2 +/- 2.2 517/03 '.,; 5114i03 9.3: +/- 2~1 : 7.3 +/-'1.9 11.2 +/- 2.2 8.9 +/- 2.0 9.3 +/- 2.1 7.5 '+/- 1.9 '
5/]4/03 - 5/21103 7.9 +/- 2.0 9.1 +/- 2.0 6.6 +/- 1.9 6.7 :!: 1.9 7.0 :!: 2.0 8.4 :!: 2.0 5/21103 .: 5128/03 ' 3.2 +/- I.S 4.l+/- 1.5 4.9 +/- 1.7' 3.6 +/- I.S 5.2 :!: 1.7 4.9 +/- 1.6 JUN 5128103 - 6/4ior 7.0' :!: 2.1 8.5 +/- 2.3' 10.6 :l: 2.3 8.7 +/- 2.1 9.2 :l: 2.2 8.5 +/- 2.1' 6/4/03 ;. 6/1 tl03 5.8 ':l: 2.2: 10.5 +/- 2.2 10.0 :!: 2.1 7.1 :!: 1.8 8.5 :!: 2.0. , 7.9 +/- 1.9
- 6/11103 - 6118/03 7.0 +/- 2.1 9.4 +/- 2.1 12.5 :!: 2.2 9.3 +/- 2.0 11.0 +/- 2.2 ! 10.3 +/- 2.0
, 6/18/03,- 6125103 ,10.5 +/- 2.1 11.4 +/-.2.2 9.7 +/- 2.1 10.6 :!: 2.1 10.4 :l: 2.1 11.7 +/- 2.2 6fi.S103 ~ 712103 16.9 +/- 2.6 23.5 +/-3.0 17.3 +/- 2.6 18.1 +/- 2.8 21.9 +/- 2.8 21.9 +/- 2.8
,- . ~ .... -.~.
Comments:
Comments: ,! I
,, I
- Refer toto Appendix Appendix F F ofof this this report report for for additional additional details details regarding regarding exceptions exceptions to to SSES SSES Technical Technical Requir~ments for for sampling sampling and and analyses.
analyses. 1*19
TABLE TABLE 1*8 GROSS BETA GROSS BETA ANALYSES ANALYSES OF OF AIR AIR PARTICULATE PARTICULATE FILTERS FILTERS SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELEcrRIC ELEcrRIC STATION* 2003 2003 Results in Results in E*03 pCilCu.
pCilCu. M. +/- 2S M. +/- 2S COLLECTION COLLECTION I MONTH MONTH DATE DATE 6Gl 6Gl 8Gl 8Gl 3S2 3S2 12El 12El 12S1 12S1 13S6 13S6 COMMENTS COMMENTS JUL 712103 -7/9/03 17.4 :+/- 2.6 17.7 :+/- 2.6 21.4 :+/- 2.7 20.8 :+/- 2.7 23.1 :+/- 2.9 20.4 :+/- 2.7 7/9103 -7116/03 9.2 +/-2.0 11.6 :+/- 2.1 11.5 :+/- 2.1 12.0 :+/- 2.1 10.1 :+/- 2.0 . 10.4 :+/- 2.0 7/16103 -7123/03 13.3 :+/- 2.5 8.4 :+/- 2.0 12.0 :+/- 2.3 13.6 :+/- 2.4 12.1 :+/- 2.5 : 11.5 :+/- 2.3 7/23103 ~ 7/30/03 12.4 +/- 2.4. 12.1 :+/- 2.2 14.9 :+/- 2.4 14.5 :I: 2.4 14.9 :I: 2.5 13.5 :I: 2.4 AUG 7/30/03 - 8/6103 9.3 ~ 2.1 8.9 :+/- 2.0 11.7 :+/- 2.2 9.4 :I: 2.1 12.4 :+/- 2.3 11.3 :+/- 2.2 8/6/03*8/13/03 10.8 :I: 2.3 H.8 :I: 2.3 . 12.4 :I: 2.3 13.2 :I: 2.3 11.2 :I: 2.6 , 11.2 ;.I: 2.3 S/13/03 - 8/20/03 15.3 :I: 2.4 19.4 +/- 2.6 16.7 ;.I: 2.4 17.9 ;.I: 2.5 16.8 :I: 2.5 ' 16.4 ;.I: 2.5 8120103 - 8127/03 . 19.9 +/- 2.7 20.7 +/- 2.8 22.8 :I: 2.8 21.9 ;.I: 2.7 20.4 +/- 2.9 ' 20.4 ;.I: 2.8 8/27/03 - 9/3103 10.2 :+/- 2.1 11.4 :I: 2.2 11.9 +/- 2.1 10.9 :I: 2.1 10.7 +/- 2.1 11.7 +/- 2.2 SEP 9/3/03 - 9/10/03 13.4 +/- 2.2 12.6 :I: 2.2 12.8 :I: 2.1 13.5 :I: 2.2 15.2 :I: 2.3 13.4 ;.I: 2.2 9/10/03 - 9/17/03 J 1.9 +/- 2.20 J 1.0 :I: 2.1 15.4 :I: 2.2 U.S :I: 2. J 12.5 ;.I: 2.2 . 13.2 ;.I: 2.2 9/17/03 - 9/24/03 16.7 +/- 2.8 16.7 +/- 2.7 13.2 +/- 2.5 17.4 :+/- 2.7 13.4 +/- 2.5 16.0 :I: 2.7
- 9/24/03 - 1011103 12.2 +/- 2.8 J 1.2 +/- 2.7 12.3 :+/- 2.7 13.3 :I: 2.7 12.9 :I: 2.7 13.2 +/- 2.8 ocr 10l1J03 - 10/8/03 13.3 +/- 2.4 12.0 +/- 2.2 12.1 :+/- 2.3 10.2 +/- 5.4 12.7 +/- 2.3 12.2 +/- 2.3
- 1018103 - 10115/03 30.9 :I: 3.6 31.0 +/- 3.5 30.2 +/- 3.4 29.9 +/- 3.3 31.7 :I: 3.5 26.6 ;.I: 3.3 10/15103 - 10122103 16.3 +/- 2.6 16.8 +/- 2.5 18.0 :I: 2.6 17.3 :I: 2.5 19.1 :I: 2.6 ' 20.7 ;.I: 2.8 10122103
- 10/29/03 12.6 +/- 2.2 10.0 ;.I: 2.0 11.9 :1:2.1 14.6 :I: 2.5 14.5 +/- 2.2 14.3 ;.I: 2.3 NOV 10/29/03 - 1115103 21.1 +/- 2.8 23.3 +/- 2.8 30.0 +/- 3.' 24.6 :I: 2.8 22.0 :+/- 2.7 . 24.1 :+/- 2.9 1115/03 - 11112103 10.7 :+/- 2.2 14.1 +/- 2.4 15.3 +/- 2.2 15.3 :I: 2.3 16.3 +/- 2.4 15.1 ;.1:2.4 11112103 - 11119/03 13.2 +/- 2.4 21.1 :I: 2.7 19.0 :I: 2.5 16.1 :I: 2.4 17.2 :I: 2.6 17.2 :I: 2.5 11119103 - 11/26/03 19.3 +/- 2.8 18.9 :I: 2.7 24.1 +/- 2.8 23.3 :I: 2.7 25.0 +/- 2.9 22.4 +/- 2.9 11126/03 ~ 1213/03 11.1 :I: 2.3 12.S +/- 2.3 13.4 :I: 2.5 14.3 +/- 2.3 12.8 :I: 2.3 12.8 :I: 2.4 DEC 1213/03 - 12110/03 10.1 :+/- 2.1 12.1 :I: 2.1 11.3 :I: 2.1 11.7 :+/- 2.0 12.4 ;.I: 2.1 10.1 :I: 2.0 12110/03* 12116/03 9.1 :+/- 2.3 9.0 +/- 2.1 )).0 +/- 2.3 9.3 :I: 2.1 9.5 :I: 2.3 ' 9.5 +/- 2.2 12116/03:. 12123/03 13.7 '+/- 2.3 13.0 ':I: 2.2 13.5 ;.I: 2.3 13.6 :I: 2.2 14.9 :I: 2.3 15.8 :I: 2.4 12123103 - 12130/03 14.1 +/- 2.3 13.4 +/- 2.1 IS.5 :I: 2.5 16.8 :I: 2.3 16.9 :I: 2.3 ! 18.3 :I: 2.4 Comments:
Comments:
'Re(' '0
'Re(' Appendix F
'0 Appendix F of of this this report report forfor additional additional details details regarding regarding exceptic* to to SSES SSES Technical Technical Requirements Requirements for for sampling sampling and and analyses.
analyses. 1-20 1-20
c TABLE 1*9 TABLE GAMMA*
GAMMA
- SPECTROSCOPIC SPECTROSCOPIC ANALYSES ANALYSES OF OF COMPOSITED COMPOSITED AIR AIR PARTICULATE PARTICULATE FILTERS FILTERS SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION* 20032003 Results in Results in E-03 E-03 pCUCu.
pCUCu. M. +/- 2S M. +/- 2S LOCATION LOCATION COLLECTION DATE COLLECTION DATE Be*7 K*40 OTHER ACTIVITY OTHER ACTIVITY 601 601 01/02103 -- 04/02103 01/02103 04/02103 91.1 +/-1O.3 91.1 +/-1O.3 <5.01
<5.01 Sal Sal 01102103 04102103 01102103 -- 04102103 93.4+/- 7.03 93.4+/- 7.03 <1.97
<1.97 3S2 3S2 01102103 04102103 01102103 -- 04102103 106+/- 8.29 106+/- 8.29 <3.05
<3.05 12EI 12EI 01102103 .... 04;62103 01102103 04;62103 109+/- 8.69 109+/- 8.69 <1.78
<1.78 12S1 12S1 01102103 04102103 01102103 -- 04102103 106 +/-
106 7.54
+/- 7.54 <6.66
<6.66 13S6 13S6 01102103 -- 04;02103 01102103 04;02103 99.1 +/-
99.1 +/- 7.15 7.15 <6.30
<6.30
~ ,:'
,'. t 601 601 04/02103 -- 07m03 04/02103 07m03 74.7 74.7 +/-+/- 9.41 9.41 4.16 +/- 2.31 4.16 +/- 2.31 SOl SOl 04/02103 -- 07 04/02103 m03 07m03 88.5 +/-9.42 88.5 +/-9.42 <1.78
<1.78 3S2 3S2 04/02103 -- 07 04/02103 m03 07m03 86.6+/- 10.4 86.6+/- 10.4 <3.40
<3.40 12E1 12E1 04/02103. ~ '07'o/~3 04/02103. 91.4 +/-
91.4 +/- 8.50 8.50 <2.03
<2.03 12S1 , '
12S1 04/02103,- 0712103 04/02103,- 0712103 83.2+/- 12.2' 83.2+/- 12.2' <1.99
<1.99 1356 1356 04/02103 -- Oii2i03 04/02103 Oii2i03 'UI+/-11.l
'UI+/-11.l <5.17
<5.17
- "fl.l
'*"t 601 601 07/02103 10/01103 07/02103 ~ 10/01103 89.2+/- 8.23:
89.2+/- 8.23: <2.81
<2.81 801 801 07/02103 -10/01103 07/02103 -10/01103 83.8 +/-
83.8 +/- 7.33 7.33 <7.31
<7.31 3S2 3S2 07/02103 -- 10/01103 07/02103 10/01103 101 +/-
101 +/- 2.47 2.47 <.794
<.794 12El 12El 07/02103 -- 10101103 07/02103 10101103 86.7+/-9.03 86.7+/-9.03 <3.27
<3.27 12S1 12S1 07/02103 -- 10/01103 07/02103 10/01103 97.7 +/-
97.7 +/- 8.28 8.28 <2.22
<2.22 13S6 13S6 07/02103 -- 10/01103 07/02103 10/01103 85.5 +/-9.95 85.5 +/-9.95 <S.26
<S.26 I,';
601 601 10/01103 -- 12130/03 10/01103 12130/03 70.3 +/- 6.57' 70.3 +/- 6.57' <2.80
<2.80 SOl SOl 10/01103 -;12130/03 10/01103 -;12130/03 66.3+/-7.22 66.3+/-7.22 <7.83
<7.83 3S2 3S2 10/01103 -- 12130/03 10/01103 12130/03 69.3 +/-
69.3 +/- 5.85 5.85 <2.02
<2.02 12EI 12EI 10/01103 -- 12130/03 10/01103 12130/03 74.9 +/-7.l0 74.9 +/-7.l0 <2.60
<2.60 12S1 12S1 10/01103 -- 12130/03 10/01103 12130/03 76.5 +/-4.33 76.5 +/-4.33 <1.38
<1.38 13S6 13S6 10/01103 -- 12130/03 10/01103 12130/03 ! ' 67.0 +/-6.96 67.0 +/-6.96 <1.60
<1.60 1*21
TABLE 1*10 TABLE IODlN~131, AND GAMMA*
AND GAMMA* SPECfROSCOPIC SPECfROSCOPIC ANALYSES ANALYSES OF OF MILK MILK SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECfRIC ELECfRIC STATION* 2003 2003 Results in Results in pCiIliter +/-2S pCiIliter +/-2S LOCATION LOCATION COLLECTION DATE COLLECTION DATE K-40 K-40 OTHER ACfIVITY OTHER ACfIVITY COMMENTS COMMENTS 10Gl 10Gl 01107/03 01107/03 1480+/-
1480+/- 120120 1001 1001 01106/03 01106/03 1470 +/-
1470 +/- 120 120 1002 1002 01106/03 01106/03 1410+/- 120 1410+/- 120 12B2 12B2 01106/03 01106/03 1390 +/-
1390 +/- 130 130 10Gl 10Gl 02103/03 02103/03 IS20+/- 110 IS20+/- 110 1001 1001 02103/03.
02103/03. 1540 +/- 130 1540 +/- 130 1002 1002 02103/03 02103/03 1280+/- 140 1280+/- 140 12B2 12B2 02l03i03 02l03i03 1400 +/-
1400 +/- ISO ISO 10G1 10G1 03/03/03 1390+/- 110 1390+/- 110 1001 1001 03/03/03 1330 +/-
1330 +/- 130 130 1002 1002 03/03/03 03/03/03 1420 +/-
1420 +/- 110 110 12B2 12B2 03/03/03 1400+/- 110 1400+/- 110 10Gl 10Gl 04/07/03 1530+/-
1530+/- 110 110 1001 1001 04/07/03 04/07/03 1360+/-
1360+/- 130 130 1002 1002 04/07103 04/07103 1220 +/-
1220 +/- 140 140 12B2 12B2 04/07/03 1330 +/-
1330 +/- 150 150 10Gl 10Gl 04121/03 04121/03 1480 1480 +/-+/- 110 110 1001 1001 04/21103 04/21103 1350+/-
1350+/- 130 130 1002 1002 04/21103 1440+/-
1440+/- 160 160 12B2 12B2 04/21103 1360 +/-
1360 +/- 150 150 10GI 10GI 05/05/03 05/05/03 1470+/- 110 1470+/- 110 1001 1001 05/0S/03 1430+/-
1430+/- 160160 1002 1002 05105/03 13IO+/- 110 13IO+/- 110 12B2 12B2 OS/05/03 1530 +/-
1530 +/- 140 140
. 10Gl 10Gl 05119103 1470+/- 130 1470+/- 130 1001 1001 05/19/03 1460 +/-
1460 +/- 110 110 1-21 1-21
(.
(,
TABLE 1-10 TABLE 1-10 IODINE-131, AND IODINE-131, AND GAMMA""
GAMMA"" SPECTROSCOPIC SPECTROSCOPIC ANALYSESANALYSES OF OF MILK MILK SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECfRIC ELECfRIC STATION STATION -- 2003 2003 Results in Results in pCilIiter +/- 2S pCilIiter +/- 2S I.
LOCATION LOCATION COLLECTION DATE COLLECTION DATE K-40 K-40 OTHER ACTIVITY OTHER ACTIVITY COMMENTS COMMENTS 1002 1002 05/19/03 05/19/03 1480+/- 110 1480+/- 110 1282 1282 05/19/03 05/19/03 1350+/- 110 1350+/- 110 10GI 10GI 06/04/03 06/04/03 1340+/- ltO 1340+/- ltO lOot lOot 06/04/03 "
06/04/03 1390+/-
1390+/- 140 140 1002 1002 ' 06/04103' 06/04103' t190+/- 160 t190+/- 160 12B2 12B2 06/04/03, 06/04/03, 1390+/- 120 1390+/- 120 10Gl 10Gl 06/J9/03 06/J9/03 1400+/-
1400+/- 160 160 1001 1001 06/19/03" 06/19/03" 1460+/-
1460+/- 160 160 1002 1002 06lt9/03' ' 1400+/-
1400+/- 150 150 12B2' 12B2' 06/1'9/03'.:
06/1'9/03'.: 1350 d::
1350 d:: 150,~
, ,*i dq "" ;-: J ,,;. ~ ~ * ~ ,
'f'-/'
- n n .... r'; ""'. 1 :n -- ! II, 10Gl --
10Gl 07/06/03';
07/06/03'; 1350+/- 130 1350+/- 130 1001, 1001, 07/06/03 07/06/03 1340:!:: 130, 1340:!:: 130, 1002 1002 07/66103 ::
07/66103 J420+/- JJ10,\
J420+/- 10,\
12B2 12B2 0?~06/~3-! 1500+/-
1500+/- 1 1 ~O:,
10Gl 10Gl 07121103 07121103 1470:!::
1470:!:: 110 110 1001 1001 07121103 07121103 1340 +/-
1340 150
+/- 150 1002 1002 07/21103, 07/21103, 1550+/- 160 1550+/- 160 12B2 12B2 07/21103 07/21103 IS20:!:: 170 IS20:!:: 170 ii ,I
,I
, i I '
1-23 1-23
TABLE 1-10 TABLE 1-10 IODINE-131, AND IODINE-131, AND GAMMA*
GAMMA* SPECTROSCOPIC SPECTROSCOPIC ANALYSES ANALYSES OF OF MILK MILK SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECTRIC ELECTRIC STATION STATION -- 2003 2003 Results in Results in pCilliter +/- 2S pCilliter +/- 2S LOCATION LOCATION COLLECTION DATE COLLECTION DATE K-4O K-4O OTHER ACTIVITY OTHER ACTIVITY COMMENTS COMMENTS lOG II lOG 08/04/03 08/04/03 1360:1: 180 1360:1: 180 1001 1001 08/04/03 08/04/03 1330:1: 110 1330:1: 110 1002 1002 08104103 08104103 1500:1: 120 1500:1: 120 12B2 12B2 08/04/03 08/04/03 1410:1: 170 1410:1: 170 10Gl 10Gl 08/18/03 08/18/03 )420:1: 160
)420:1: 160 1001 1001 08118103 08118103 1340:1: 150 1340:1: 150 1002 1002 08118/03 08118/03 1410:1: 110 1410:1: 110 12B2 12B2 08118103 08118103 1330:1: 1'10 1330:1: 1'10 10GI 10GI 09/03/03 09/03/03 1484:1: 94 1484:1: 94 100) 100) 09/03/03 09/03/03 1380:1: 160 1380:1: 160 1002 1002 09/03/03 09/03/03 1380:1: 110 1380:1: 110 12B2 12B2 09/03/03 09/03/03 1471 :I:
1471 95
- I: 95 10GI 10GI 09/18/03 09/18/03 1490 1490 ~ 110110 1001 1001 09/18/03 09/18/03 1410:1: 14Q 1410:1: 14Q 1002 1002 09/18/03 09/18/03 1390:1: 110 1390:1: 110 12B2 12B2 09118103 09118103 1370:1: 110 1370:1: 110 1001 1001 10/05103 10/05103 1470:1: 110 1470:1: 110 1001 1001 10/05/03 10/05/03 1330:1: 130 1330:1: 130 1002 1002 10/05/03 10/05/03 1350:1: 150 1350:1: 150 12B2 12B2 10/05/03 10/05/03 1200:1: 150 1200:1: 150 cc 1-24 1-24
c:c: TABLE I*tO TABLE :
IODINE-t31, AND GAMMA*
IODINE-t31, AND GAMMA* SPECTROSCOPIC SPECTROSCOPIC ANALYSES ANALYSES,,OF OF MILK MILK SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECTRICELECTRIC STATIONSTATION -- 2003 2003 Results in Results in pCiIliter pCiIliter +/- +/- 2S 2S 1 I
I LOCATION LOCATION COLLECTION DATE COLLECTION DATE K-40 K-40 OTHER ACTIVITY OTHER ACTIVITY COMMENTS COMMENTS 10G1 10G1 10120/03 10120/03 1420:1: 120 1420:1: 120 1001 1001 10120/03 10120/03 1450:1: 140 1450:1: 140 1002 1002 10120/03 10120/03 1380:1: 160 1380:1: 160 12B2 12B2 10120/03 10120/03 1250:1: 150 1250:1: 150 10Gt 10Gt 11103/03 11103/03 1350:1: 110 1350:1: 110 1001 1001 11103/03 11103/03 1550:1: 160 1550:1: 160 1002 1002 11103/03 11103/03 1360:1: 150 1360:1: 150 12B2 12B2 11103/03 11103/03 1380:1: 150 1380:1: 150 10Gl" 10Gl" 12108/03 12108/03 819:1: 86 819:1: 86 1001 1001 12108/03 "
12108/03 1361 :1:58 1361 :1:58 1002 1002 12108/03 12108/03 1452:1: 62 1452:1: 62 12B2 12B2 12108/03 12108/03 940:1: 94 940:1: 94
"[
I,
. I,'
i
, t "
I"
- , ,<
- y
~
1*25
TABLE 1-11 TABLE 1-11 GAMMA*
GAMMA
- SPECTROSCOPIC SPECTROSCOPIC ANALYSESANALYSES OF OF SOIL SOIL SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION STATION -- 2003 2003 Results in Results in pCi/gm pCi/gm (dry) +/- 2S (dry) +/- 2S LOCATION LOCATION COLLECTION DATE COLLECTION DATE K-40 K-40 Cs-137 Cs-137 Th-228 Th-228 801 TOP 801 TOP 9115/2003 9115/2003 11.0 +/-
11.0 1.1
+/- 1.1 0.17 +/-.OS 0.17 +/-.OS 0.90 +/-.14 0.90 +/-.14 801 BOT 801 BOT 9/15/2003 9/15/2003 10.2+/-
10.2+/- 1.11.1 0.097+/-.053 0.097+/-.053 0.73 +/-.13 0.73 +/-.13 3S2TOP 3S2TOP 9/1512003 9/1512003 14.7 14.7 +/- 1.1
+/- 1.1 0.030+/- .035 0.030+/- .035 .. 1.04 1.04 +/-.13
+/-.13 3S2BOT 3S2BOT 9/15/2003 9/15/2003 16.2 +/-
16.2 +/- 1.2 1.2 0.049+/-
0.049+/- .039.039 1.00+/-.13 1.00+/-.13 12S1 TOP 12S1 TOP 9/15/2003 9/15/2003 10.3 +/-
10.3 +/- 1.0 1.0 0.096+/-
0.096+/- .047.047 0.82+/-.12 0.82+/-.12 12S1 BOT 12S1 BOT 9/1512003 9/1512003 12.5 +/-0.8 12.5 +/-0.8 0.076+/-.029 0.076+/-.029 .. 0.84 0.84 :I: .85
- I: .85 13S6TOP 13S6TOP 9/15/2003 9/15/2003 18.2:1: 0.9 18.2:1: 0.9 <0.042
<0.042 1.04+/-.95 1.04+/-.95 13S6 BOT 13S6 BOT 9/15/2003 9/15/2003 14.3 +/- 1.0 14.3 +/- 1.0 0.027 .024
- I: .024 0.027 :I: 0.95:1: .11 0.95:1: .11
(~ cc 1-26 1-26
TABLE 1-11 TABLE 1-11 GAMMA*
GAMMA
- SPECTROSCOPIC SPECTROSCOPIC ANALYSESANALYSES OF OF SOIL SOIL SUSQUEHANNA STEAM SUSQUEHANNA STEAM ELECTRIC ELECTRIC STATION STATION -- 2003 2003 Results in Results in pCi/gm pCi/gm (dry) +/- 2S (dry) +/- 2S LOCATION LOCATION COLLECTION DATE COLLECTION DATE K-40 K-40 Cs-137 Cs-137 Th-228 Th-228 801 TOP 801 TOP 9115/2003 9115/2003 11.0 +/-
11.0 1.1
+/- 1.1 0.17 +/-.OS 0.17 +/-.OS 0.90 +/-.14 0.90 +/-.14 801 BOT 801 BOT 9/15/2003 9/15/2003 10.2+/-
10.2+/- 1.11.1 0.097+/-.053 0.097+/-.053 0.73 +/-.13 0.73 +/-.13 3S2TOP 3S2TOP 9/1512003 9/1512003 14.7 14.7 +/- 1.1
+/- 1.1 0.030+/- .035 0.030+/- .035 .. 1.04 1.04 +/-.13
+/-.13 3S2BOT 3S2BOT 9/15/2003 9/15/2003 16.2 +/-
16.2 +/- 1.2 1.2 0.049+/-
0.049+/- .039.039 1.00+/-.13 1.00+/-.13 12S1 TOP 12S1 TOP 9/15/2003 9/15/2003 10.3 +/-
10.3 +/- 1.0 1.0 0.096+/-
0.096+/- .047.047 0.82+/-.12 0.82+/-.12 12S1 BOT 12S1 BOT 9/1512003 9/1512003 12.5 +/-0.8 12.5 +/-0.8 0.076+/-.029 0.076+/-.029 .. 0.84 0.84 :I: .85
- I: .85 13S6TOP 13S6TOP 9/15/2003 9/15/2003 18.2:1: 0.9 18.2:1: 0.9 <0.042
<0.042 1.04+/-.95 1.04+/-.95 13S6 BOT 13S6 BOT 9/15/2003 9/15/2003 14.3 +/- 1.0 14.3 +/- 1.0 0.027 .024
- I: .024 0.027 :I: 0.95:1: .11 0.95:1: .11
(~ cc 1-26 1-26
cc GAMMA** SPECTROSCOPIC GAMMA SPECTROSCOPIC ANALYSES ANALYSES OF TA~r;I-ll OF FOOD FOOD PRODUCTS PRODUCTS (FRUITS (FRUITS AND AND VEGETABLES)
VEGETABLES)
((
SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECTRICELECTRIC STATION* 2003' 2003' Results in Results pCi/gm (wet) in pCi/gm +/- 2S (wet) +/- 2S ; .i LOCATION SAMPLE LOCATION SAMPLE TYPE TYPE COLLECTION DATE COLLECTION DATE K-40 K-40 OTHER ACTIVITY OTHER ACTIVITY Potato Potato 08/21103 4.66:1: .19 4.66:1: .19 1IF2 1IF2 Potato Potato 09/04/03 09/04/03 4.47:1: .29 4.47:1: .29 I: *
-:{.
Comments:
Comments:
- Refer Refer to to ~ppendix F F of of this this report report for, for, additional additional details details regarding regarding exceptions exceptions to to SSES SSES TechnlcCi' TechnlcCi' Requirements Requirements for.
for. sampling sampling and and analyses analyses..
1-27 1-27
TABLE 1-)3 TABLE 1-)3 TYPICAL" MINIMUM TYPICAL" MINIMUM DETECTABLE CONCENTRATIONS OF DETECTABLE CONCENTRATIONS OF NUCLIDES NUCLIDES SEARCHED SEARCHED FOR FOR BUT BUT NOT NOT FOUND FOUND BYBY G¥lMA G¥lMA SPECTROMETRY SPECTROMETRY TIlE VICINITY IN TIlE IN VICINITY OFOF SUSQUEHANNA SUSQUEHANNA STEAM STEAM ELECTRIC ELECTRIC STATION, STATION, 2003 2003 Fish Fish Sediment Sediment Surface Water Surface Water Ground Water Ground Water Potable Water Potable Water Nuclide Nuclide (pCilg wet)
(pCilg wet) (pCilg dry)
(pCilg dry) (pC ill)
(pC ill) (pCiJI)
(pCiJI) (pCill)
(pCill)
Mn-54 Mn-54 0.019 0.019 0.028 0.028 2.9 2.9 4.1 4.1 1.7 1.7 Co-58 Co-58 0.023 0.023 0.035 0.035 2.1 2.1 4.6 4.6 1.8 1.8 Fe-59 Fe-59 0.050 0.050 0.110 0.110 5.1 5.1 10.2 10.2 8.3 8.3 Co-60 Co-60 0.015 0.015 0.028 0.028 3.3 3.3 5.3 5.3 2.5 2.5 Zo-65 Zo-65 0.028 0.028 0.071 0.071 7.8 7.8 14.4 14.4 6.7 6.7 Zr-95 Zr-95 0.020 0.020 0.070 0.070 6.4 6.4 7.8 7.8 5.4 5.4 Nb-95 Nb-95 N/A N/A N/A N/A 4.3 4.3 5.8 5.8 3.2 3.2 Ru-103 Ru-103 N/A N/A N/A N/A 4.9 4.9 5.3 5.3 2.6 2.6 1-131 1-131 0.100 0.100 0.173 0.173 15.4 15.4 8.1 8.1 13.2 13.2 Cs-134 Cs-134 0.010 0.010 0.032 0.032 2.3 2.3 5.2 5.2 2.6 2.6 Cs-137 Cs-137 0.015 0.015 0.033 0.033 2.4 2.4 4.S 4.S 2.5 2.5 Ba-140 Ba-140 0.300 0.300 0.310 0.310 7.8 7.8 9.0 9.0 9.2 9.2 La-I40 La-I40 0.040 0.040 0.100 0.100 12.1 12.1 10.1 10.1 10.2 10.2 Ce-141 Ce-141 N/A N/A N/A N/A 6.8 6.8 7.8 7.8 6.8 6.8 Air Particulate Air Particulate Milk Milk Fruit/Veg.
Fruit/Veg. Soil Soil Nuclide Nuclide (10-3 pCilm3)
(10-3 pCilm3) (pCiJI)
(pCiJI) (pCilg wet)
(pCilg wet) (pCilg dry)
(pCilg dry)
Mn-54 Mn-54 0.33 0.33 5.5 5.5 0.008 0.008 0.037 0.037 Co-58 Co-58 0.51 0.51 5.1 5.1 0.008 0.008 0.039 0.039 Fc-59 Fc-59 2.31 2.31 12.4 12.4 0.032 0.032 0.993 0.993 Co-60 Co-60 0.28 0.28 5.7 5.7 0.009 0.009 0.055 0.055 Zo-65 Zo-65 0.75 0.75 13.4 13.4 0.025 0.025 0.176 0.176 Zr-95 Zr-95 0.88 0.88 7.7 7.7 0.016 0.016 0.995 0.995 Nb-95 Nb-95 N/A N/A 6.1 6.1 N/A N/A 0.071 0.071 Ru-I03 Ru-I03 N/A N/A 5.2 5.2 N/A N/A 0.051 0.051 1-131 1-131 70.3 70.3 8.2 8.2 0.019 0.019 0.097 0.097 Cs-134 Cs-134 0.27 0.27 4.8 4.8 0.007 0.007 0.057 0.057 Cs-137 Cs-137 0.29 0.29 4.4 4.4 O.OOS O.OOS 0.047 0.047 Ba-140* 36.2 36.2 6.7 6.7 0.055 0.055 0.255 0.255 La-I 40 La-I 40 11.5 11.5 7.8 7.8 0.016 0.016 0.11 0.11 Ce-141 Ce-141 N/A N/A 8.1 8.1 N/A N/A 0.078 0.078 1-28 1-28
(-'.
(-'.
)'
,, ",. I;' ( " . , !"
APPENDIX>J APPENDIX>J 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report" Report" J-l
,, J-l
II II AppendixJ AppendixJ The data in The data in the the tables tables that that follow follow show show howhow wenwen Framatome Framatome ANP ANP Environmental Environmental Laboratory Laboratory and and Teledyne Brown Teledyne Brown Engineering Engineering Environmental Environmental Services (TBE) performed Services (TBE) performed in in the the analysis analysis of of "~J
.. radioactively radioactively spiked spiked media.
media. Tables Tables J*l through through 1*5 provide provide the the performance performance results results for for ..
Framatome ANP.
Framatome ANP. Tables Tables 1-6 through 1-10 1-6 through provide the 1-10 provide the performance performance results results for for TBE.
TBE. In addition In addition to the to the Analytics' Analytics' spikes spikes analyzed analyzed as as part part ofPPL's ofPPL's REMP REMP Laboratory Laboratory Spike Spike Program Program (Tables (Tables 1-3 1-3 and 1-8),
and Framatome ANP 1-8), Framatome ANP and and TBE TBE analyzed analyzed spikes spikes procured procured independently independently from from Analytics Analytics as as part of part of their their respective respective Quality Quality Control Control Spike Spike Programs Programs (Tables (Tables 1-2 1-2 and and 1-7),
1-7), asas well well as as spikes spikes prepared as prepared as part of the part of the following following programs:
programs:
- 1. The
- 1. The Proficiency Proficiency Testing Testing Program Program of of Environmental Environmental Resource Resource Associates Associates (Tables (Tables I-I and 1-6)
I-I and 1-6)
- 2. The
- 2. Quality Assessment The Quality Assessment Program Program ofDDE's ofDDE's Environmental Environmental Measurements Measurements Laboratory Laboratory (EML)
(EML)
(Tables 1-4 (Tables 1-4 and and 1-9) 1-9)
-.. '~'fiie Mixed
-.. Mixed Analyte-Performance Analyte-Performance EvaliiationEvaliiation Pfogmm:-(MAPEPr Pfogmm:-(MAPEProf of the the DOE DOE (Tables-J.;.5 (Tables-J.;.5 and-'
and-' ,_.
1-10) 1-10)
It should be It should be noted noted that that program program #1 above oilly
- 1 above oilly provides provides spiked spiked water water for for analyses.
analyses. No No other other media are media are included included in in the the spikes spikes provided provided by by this this program.
program. Also, Also, it it should should be be noted noted that that the the levels of levels of activity activity in in spikes spikes of of different different media media prepared prepared for for program program #2 #2 tend tend to to bebe relatively relatively high.
high.
They are They are relatively relatively high high compared compared to to the the levels levels ofof activity activity in in the the spikes spikes prepared prepared by by Analytics Analytics as as part of part of its its EnvironmentarCross EnvironmentarCross Check Check Prognim Prognim and and for for PPL's PPL's REMP REMP Laboratory Laboratory Spike Spike Program.
Program.
The following The following characteristics characteristics are are impo~t for for the the spiked spiked enviro~ental media: media:
When practical,
- 1. When
- 1. practical, the the level level of of activity activity in,in, at at least,'
least,' some some ofof the the spiked spiked environmental environmental media media should should be be within within thethe range range between between required required analysis analysis sensitivities sensitivities for for the the SSES SSES REMP REMP and and the Reporting the Reporting Levels, Levels, if if applicable, applicable, o~ the the NRC.
NRC.
- 2. The
- 2. spikes should The spikes should be be preserved preserved in in aa manner manner as as similar similar asas possible possible to to the the way way that that actual actual samples of samples of those those media media areare prepared.
prepared. '.
- 3. The
- 3. variety of The variety of radio radio nuclides nuclides with with which which environmental environmental media media are are spiked spiked should should bebe as as extensive as extensive as practical, practical, including including as as many many as as ofof the the activation activation and and fission fission products products that that could could be detected be detected inin the the vicinity vicinity ofof the the SSES SSES as as reasonable.
reasonable.
The spiked environmental The spiked environmental media media prepared prepared by by Analytics Analytics according according to to the the requirements requirements ofPPL's ofPPL's REMP Laboratory REMP Laboratory Spike Spike Program Program are are intended intended to to incorporate incorporate characteristics characteristics # # 1, #2, and 1, #2, and #3#3 to to the the degree that greatest degree greatest that is is practical.
practical.
2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
Appendix!
Appendix!
\.../
\.../ The criteria for The criteria for the the acceptability acceptability ofof the the analyses analyses results results for for the the spikes spikes prepared prepared asas part part of of the the PPL PPL REMP Laboratory REMP Laboratory Spike Spike Program Program (Tables (Tables 1-3 & 1-8) 1-3 & 1-8) have have been been established established by by PPL.
PPL. They They are are based on based on criteria criteria that that were were originally originally developed developed by by the the NRC.
NRC. TheThe NRC NRC bases bases these these criteria criteria on on an an empirical relationship empirical relationship that that combines combines prior prior experience experience and and accuracy accuracy needs.
needs. As As the the resolution of resolution of the measurement the measurement process process improves improves (relative (relative measurement measurement uncertainty uncertainty becomes becomes smaller),
smaller), the the criteria for criteria for detennining detennining acceptability acceptability become become tighter.
tighter. Conversely, Conversely, asas the the resolution of the resolution of the process process qecomes poorer qecomes poorer (relative (relative measurement measurement uncertainty uncertainty becomes becomes bigger),
bigger), the the criteria criteria are are widened.
widened.
The criteria The criteria for for acceptability acceptability ofof DOE DOE programs programs (EML's (EML's andand MAPEP's MAPEP's programs programs -- Tables Tables 1-4, 1-4, 1-1-
5,1-9 and 1-10) 5,1-9 and 1-10) are are based based onon control control limits limits based based on on percentiles percentiles ofof historic historic data data distributions.
distributions.
Note that comment Note that comment numbers numbers at at the the extreme extreme right right side of the side of the tables tables denote denote unacceptable unacceptable results results in in Tables I-I Tables I-I through through 1-10.
1-10. Discussions Discussions relevant relevant to to these these comment comment numbers numbers follow follow the the presentations of presentations of the-data;-as -applicable.
the-data;-as -applicable. ~~------- ---------~~---
Radionuclide concentration results Radionuclide concentration results not not available available (due (due to to loss loss of of spectrum spectrum byby Analytics)
Analytics) andand therefore not therefore not included included inin Tables Tables 1-3 1-3 and and I-S I-S for for the the following:
following:
Analytics Sample Analytics Sample Numbers:
Numbers: E39S0-1S6 E39S0-1S6 and and E3976-1S6 E3976-1S6 (spiked (spiked milk).
milk).
J-3 J-3 2003 Radiological 2003 Radiological Environmental Environmental Monitoring Monitoring Report Report
ENVIRONMENTAL ENVIRONMENTAL RESOURCE TA(~J-1 RESOURCE ASSOCIATES ASSOCIATES (ERA) (ERA)
II II PROFICIENCY TESTING PROFICIENCY TESTING PROGRAM PROGRAM -- 2003 2003 II FRAMATOME ANP FRAMATOME ANP ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES LABORATORY LABORATORY (page 1 (page 1 of2) of2)
Identlncatlon Identlncatlon ERA Known ERA Known Framatome Framatome FramatomtlERA FramatomtlERA ERA ERA No.
No. MedIum MedIum Untl'l Untl'l NuclIde NuclIde Resu1t(a)
Resu1t(a) Resull'l (a)
Resull'l (a) Ratio Ratio Control Control LimIts LimIts (b)
(b) Evaluation Evaluation Rad-52 Rad-52 Water Water pCiII pCiII Gross Alpha Gross Alpha 37.6 37.6 28 28 0.74 0.74 1.3-53.9 1.3-53.9 Acceptable Acceptable pCiII pCiII Gross Deta Gross Deta 8.55 8.55 8.97 8.97 I.OS I.OS 0.00-17.2 0.00-17.2 Acceptable Acceptable pCiII pCiII St*89 15.9 15.9 13 13 0.82 0.82 7.24-24.6 7.24-24.6 Acceptable Acceptable pCiII pCiII Sr-90 Sr-90 9.03 9.03 8.74 8.74 0.97 0.97 0.37-17.7 0.37-17.7 Acceptable Acceptable pCtII pCtII Ba-133 Ba-133 19.5 19.5 17.9 17.9 0.92 0.92 1'0.S-28.2 1'0.S-28.2 Acceptable Acceptable pCiII pCiII Co-6O Co-6O 37.4 37.4 36.6 36.6 0.98 0.98 28.7-46.1 28.7-46.1 Acceptable Acceptable pCiII pCiII Cs-134 Cs-134 17.8 17.8 17.9 17.9 1.01 1.01 9.14-26.5 9.14-26.5 Acceptable Acceptable 1
1 pCtII pCtII Cs*t37 44.2 44.2 45.4 45.4 l.oJ l.oJ 35.5-52.9 35.5-52.9 Acceptable Acceptable pCiII pCiII Zn-65 Zn-65 60.3 60 60 1.00 1.00 49.9-70.7 49.9-70.7 Acceptable Acceptable pCtII pCtII Nat. Uranium Nat. Uranium 53.7 53.7 56 56 1.04 1.04 44.4-63.0 44.4-63.0 Acceptable Acceptable Rad-S3 Rad-S3 Water Water pCtII pCtII H-3 H-3 1250.0 1250.0 1080.0 1080.0 0.86 0.86 II 678-1820 678-1820 Acceptable Acceptable II pCiII pCiII 1*131 20.8 20.8 21.4 21.4 t.03 t.03 15.6-26.0 15.6-26.0 Acceptable Acceptable Rad-54 Rad-54 Water Water pCtII pCtII Gross Alpha Gross Alpha 65.1 65.1 70.4 70.4 1.08 1.08 II 36.9-93.3 36.9-93.3 Acceptable Acceptable pCtII pCtII Gross Beta Gross Beta 31.6 31.6 31.9 31.9 1.01 1.01 22.9-40.3 22.9-40.3 Acceptable Acceptable pCiII pCiII St*89 58.8 5S.S 5S.S 0.94 0.94 50.1-67.5 50.1-67.5 Acceptable Acceptable pCtII pCtII 5r-9O 5r-9O 20.6 20.6 18.7 18.7 0.91 0.91 1'1.9.29.3 1'1.9.29.3 Acceptable Acceptable
,, pCiII pCiII Da-133 Da-133 20.7 20.7 ,, 19.9 19.9 "" 0.96 0.96 12.0-29.4' ,,
12.0-29.4' .. ACctptable ACctptable
.. pCtII' pCtII' ,,co-6O
,,co-6O 37.4.
37.4. :37.4 ....
- 37.4 1.00 1.00 28.7-46.1 28.7-46.1 ACceptable ACceptable
.... ;' I
- pC-t11 pC-t11 .. Cr*134 32.6 32.6 31.0 31.0 0.95 0.95 23.9-41.3 23.9-41.3 Acceptable Acceptable pCiII pCiII Cs*137 .44.3
.44.3 47.0 47.0 ., 'co
., 'co t.()6 t.()6 35.6-53.0 ..
35.6-53.0 Acceptable Acceptable pC:t11 pC:t11 Zn-65 ..
Zn-65 .. 60.2 60.2 61.3 61.3 1.02 1.02 49.8.70.6 49.8.70.6 Acceptable Acceptable pCiII pCiII Nat. Uranium Nat. Uranium 11.4 11.4 1I.S 1I.S 1.01 1.01 ~20-16.6 .. Acceptable Acceptable Rad*55 Water, ""
Water, pCtII pCtII *1-131 28.2 ""
28.2 28': ..
28': 0.99 0.99 10-33.4' 10-33.4' Acceptable Acceptable pCiII pCiII Triiium Triiium 14300 14300 14800 14800 1.03 1.03 11800-16800 11800-16800 Acceptable Acceptable J-4 J-4 II (a) Results Results are are the the average average of of three three measurements, measurements, reported in units units of of pCiIJ.
uu .\ \
reported in pCiIJ. "" ..
(a) II Per guidelines (b) Per (b) guidelines of of the the EPA'S EPA'S National National Standards Standards forfor Water Water Proficiency Proficiency Testing Testing Criteria Criteria D~ument. December December 1998.
1998. II II II II
,,ii TABLEJ-l TABLEJ-l ii ENVIRONMENTAL ENVIRONMENTAL RESOURCE RESOURCE ASSOCIATES ASSOCIATES (ERA) (ERA) \\
PROFICIENCY TESTING PROFICIENCY TESTING PROGRAM PROGRAM -- 2003 2003 II FRAMATOME ANP FRAMATOME ANP ENVIRONMENT~ SERVICES SERVICES LABO~TORY (Page 22 of (Page of 2)
- 2) ii II 1
1 COMMENTS COMMENTS ,,
The equations used The equations t~
used calculate calculate the the sample sample activity activity were were all all independently independently verified verified to to be correct. No be correct. No problems problems were!ideillified were!ideillified with with sample sample documentation. The documentation. The chemists chemists were were trained trained to to process process strontium strontium samples samples expeditiously expeditiously and
' and 10 utilize the 10 utilize
'.. the full full IS-day IS-day )1trium-90 II
)1trium-90 in*growth period.
period.
22 Equipment problem Equipment problem with with iodide iodide probe probe identified.
identified. When When sample sample was was re-analyu:d re-analyu:d with with new new iodide iodide probe, probe, ~ resu1iresu1i w~ 14.5 14.5 pCiIL, pCiIL, aa bias bias of of -1.4%.
-1.4%.
3 3 No problems No problems identifed identifed via via test test data data evaluation evaluation using using internal internal calibrations.
calibrations. The The grand grand mean mean of of the the RAD*50 testtest comp'ared comp'ared favorably favorably (1 (1 % bias) with
% bias) with the Framatome ANP the Framatome ANP result result yet indicated aa signifi~ant bias yet indicated bias from from the the ERA ERA stated stated known.
known. NoNo actions actions were were taken taken based based on on the the favorable favorable QC history QC history
~~m .
J-5 C._
C._ c.-
c.-
((
ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVITY TA(~J.Z RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAM II PROGRAM -- 2003 2003
((
FRAMATOME ANP FRAMATOME ANP QUALITY QUALITY CONTROL CONTROL SPIKE SPIKE PROGRAM PROGRAM FRAMATOMEANPENVIRONMENTALLABORATORY FRAMATOMEANPENVIRONMENTALLABORATORY (Page 1 (Page 1 of of 4)
- 4) II I"
I" II II Analytlcs Analytlcs JdentincaUon JdentincaUon Calculated Calculated Framatome FramatomelAnalytlcs Framatome FramatomelAnalytlcs MonthlYear MonthlYear No.
No. Medium Medium Units Units Nuclide Nuclide Results Results II Results Results Ratio Ratio Marcb*03 83600-162 83600-162 Milk Milk pCiII pCiII 1*131U.* 74 74 72.S 72.S 0.98 0.98 pCiII pCiII j.t31 74 74 73 73 0.99 0.99 pCiII pCiII Ce~t41 173 173 170 170 0.98 0.98 pCiII pCiII Cr*SI 246 246 244 244 0.99 0.99 pCiII pCiII Cs*134 90 90 86 86 0.96 0.96 pCiII pCiII Cs~137 200 200 196 196 0.98 0.98 pCiII pCiII Co-58' 47 47 44 44 0.94 0.94 pCill pCill Mo*54 64' 64' 61 61 o.9S.
1 1 .:~.
"" pCiIi pCiIi Ft-59 i 47 47 47' 47' too' too' pCiII pCiII Zn*6S 93 ,,
93 96 96 1.03 1.03 p~iII Co-60 162 162 l~oo'
~ "'J
"'J ,i
,i .... 162 162 Marcb-03 Marcb-03 83597-162 83597-162 Water Water pCiII pCiII Or.Alpba 53 53 SS 1.04 1.04
'> ~; 83597-162 83597-162 Water Water pCiII pCiII Or. Beta 186
186 146 146 0.78' 0.78' 83598-162 83598-162 Water Water pCiII pCiII 1*131LV 70 70 67.7 67.7 0.97 0.97 pCiII pCiII 1*131' 70 70 68 68 0.97 0.97 pCiII pCiII Ce-141 16S 16S 163 163 0.97 0.97 pCiIl pCiIl Cr*SI 238 238 243 243 1.02 1.02 pCiII pCiII Cs-134 88 88 83 83 0.94 0.94 pCiIl pCiIl Cs*t37 195 195 188 188 0.96 0.96 pCill pCill Co-SS 42 42 44 44 1.05 1.05 pCiIl pCiIl Mn*S4 ' 63 63 61 61 0.97 0.97 pCiIl pCiIl Pe-59 46 46 48 48 1.04 1.04 pCiIl pCiIl Zn*6S 90 90 88 88 0.98 0.98 pCiIl pCiIl Co-60 157 ..
157 156 156 0.99 0.99
- r* t:n u. = radicx:hemicalscparation analysis analysis J*6 i'i' II!!
ii
TABLEJ-2 TABLEJ-2 I ANALYTlCS ANAL YTlCS ENVmONMENTAL ENVmONMENTAL RADIOACTIVITY RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM I
-- 2003 2003 FRAMATOME ANP FRAMATOME ANP QUALITY QUALITY CONTROL CONTROL SPIKESPIKE PROG¥M PROG¥M FRAMATOME ANP FRAMATOME ANP ENVmONMENTAL ENVmONMENTAL LABORATORYLABORATORY (Page 2 (Page 2 of of 4)
- 4) I I
Analyllcs Analyllcs JdentUkaUon JdentUkaUon Calculated Calculated l<'ramatome FramatomtlAnalylics l<'ramatome FramatomtlAnalylics MonthlVear MonthlVear No.
No. Medium Medium Units Units Nuclide Nuclide Results Results I Results Results Ratio Ratio March.oJ March.oJ ElS!}9*162 AP filter AP filter pCi pCi Gr. Alpha Gr. Alpha 49 49 52 52 1.06 1.06 pCi pCi Gr. Beta Gr. Beta 148 148 IS1 IS1 1.06 1.06 March.o3 March.o3 El60I*162 Milk Milk pCiIJ pCiIJ 5r*89 133 133 121 121 0.91 0.91 pCill pCill Sr*90 12 12 13 13 1.08 1.08 March.oJ March.oJ El60S*162 Water Water pCill pCill Sr-89 Sr-89 114 114 104 104 0.91 0.91 pCiIJ pCiIJ Sr-90 Sr-90 10 10 II 1.10 1.10 Junc.o3 Junc.o3 El704-162 El704-162 Waler Waler pCiIJ pCiIJ H*3 11953 11953 10643 10643 0.89 0.89 Junc.oJ Junc.oJ El705-162 El705-162 AP filter AP filter pCi pCi Gr. Alpha Gr. Alpha 21 21 20 20 0.95 0.95 pCi pCi Gr. Beta liS liS 116 1.01 1.01 Junc.oJ Junc.oJ El706-162 El706-162 AP filter AP filter pCi pCi Cc*141 l54 l54 149 149 0.97 0.97 pCi pCi er-Sl er-Sl 130 130 134 134 1.03 1.03 pCi pCi Cs-I34 Cs-I34 S6 S6 54 54 0.96 0.96 pCi pCi Cs*137 115 115 13S 13S 1.08 1.08 pCi pCi Co-5S Co-5S 50 50 53 53 1.06 1.06 pCi pCi MD*54 101 101 110 110 1.09 1.09 pCi pCi Fe-59 Fe-59 54 54 60 60 1.11 1.11 pCi pCi Zn-65 Zn-65 99 99 110 110 1.11 1.11 pCi pCi Co-6O 72 72 71 71 0.99 0.99 JUDe-OJ JUDe-OJ El707-162 El707-162 APfilter APfilter pCi pCi S,-89 S,-89 81 81 78 78 0.90 0.90 pCi pCi Sr-90 Sr-90 24 24 24 24 1.00 1.00 J.'
J.'
(.
c c ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVITY
((
TABLEJ-2 TABLEJ-2 RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAM II PROGRAM -- 2003 2003 FRAMATOME ANP FRAMATOME ANP QUALITY QUALITY CONfROL CONfROL SPIKESPIKE PROGRAM PROGRAM FRAMATOMEANPENVIRONMENTALLABORATORY FRAMATOMEANPENVIRONMENTALLABORATORY (Page 33 of (Page of 4)
- 4) !!
II II Analytl(S Analytl(S IIII IdentlncatIon IdentlncatIon Calculated Calculated Framatome FramatomelAnalytl(S Framatome FramatomelAnalytl(S MonthlYtar MonthlYtar No.
No. Medium Medium Unlts Unlts Nuclide Nuclide Results Results II ResultsResults Ratio Ratio June*03 El153*162 Milt Milt pCiII pCiII 1*131 103 103 109 109 1.06 1.06 pCiII pCiII 1*13IlL* 103 103 104 104 J.OI J.OI pCiII pCiII Ce*141 283 283 283 283 1.00 1.00 pClII pClII er*sl 239 239 239 239 1.00 1.00 pCiII pCiII Cs*134 103 103 98 98 0.9S 0.9S pCiII pCiII Cs*137 230 230 232 232 J.OI J.OI pCiII pCiII Co-58 93 93 92 92 0.99 0.99 pC-III pC-III Mn*54 186 186 186 186 1.00 1.00 pCiII pCiII Fe-S9 99 99 100 100 1.01 1.01
,, pCiII pCiII Zn-6S 181 181 181 181 1.00 1.00 pCiII ::
pCiII cQ:.6O' 132 ,,
132,,
134 134 1.02:
1.02:
September-03 September-03 El866-t62 Water Water pCiII
pCiII OrossAlpba 36 36 37 37 1:03, 1:03, pCiII' pCiII' OrossBeta 246' 246' 242 242 0.98 0.98 September*03 El867*162 Water Water pCiII pCiII 1*131'J 76 76 69 69 0.91 0.91 pCiII ,,
pCiII 1*I3ILL* 76 76 78 78 1.03 1.03 pCiII pCiII Ce*14t 81 81 78 78 0.96, 0.96, pCiII ,,
pCiII Cr*SI 221 221 198 198 0.90 0.90 pCiII pCiII Cs*134 113 113 108 108 0.96 0.96 pCiII, pCiII, Cs~137 84, 84, 85 85 1.01 1.01 pCiII pCiII Co-58 94 94 92 92 0.98 0.98 pCiII pCiII Mn*S4 88 88 93, 93, 1.06, 1.06, pCiII 75 74' pCiII Fe*59 75 74' 0.99 0.99 pCiII pCiII Zn*65 166 166 170 170 1.02 1.02 pCiII pCiII Co-60 .117
.117 118 118 1.01 1.01 September*03 El868*162 APFilter APFilter pCi pCi Or. Alpha 28 28 30 30 1.07 1.07 pCI pCI Or. Beta 189 189 197 197 1.04 1.04 II
- ,. 3 II lL
,. JJ3 lL == radiocbemical radiocbemical separation separation analysis analysis !! J*8 II
,, '.'. II
!! \\
TABLEJ-2 TABLEJ-2 ANALYTICS ENVmONMENTAL RADIOACTIVITY ANALYTICS ENVmONMENTAL RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 20032003 FRAMATOME ANP FRAMATOME ANP QUALITY QUALITY CONTROL CONTROL SPIKE SPIKE PROGRAM PROGRAM FRAMATOME ANP FRAMATOME ANP ENVIRONMENTAL ENVIRONMENTAL LABORATORYLABORATORY (Page 44 of (Page of 4) 4)
Analytla Analytla Identification Identification Calculated Calculated Framatome FramatomdAnalyUa Framatome FramatomdAnalyUa MonthlYear MonthlYear No.
No. Medium Medium Units Units Nuclide Nuclide Results Results ;; Results Results Ratio Ratio Seplember'()3 Seplember'()3 E3869*162 Milk Milk pCill pCill 1*131 74 74 66 66 0.89 0.89 pCiII pCiII 1*13ILL* 74 74 74 74 1.00 1.00 pCill pCill Ce*141 86 86 90 90 1.05 1.05 pCiIl pCiIl er*St 233 233 228 228 0.98 0.98 pCill pCill Cs*I34 119 119 123 123 1.03 1.03 pCiII pCiII Cs*137 88 88 94 94 1.07 1.07 pCiIl pCiIl Co-58 99 99 99 99 1.00 1.00 pCill pCill Mn*S4 93 93 101 101 1.09 1.09 pCill pCill Fe*S9 79 79 84 84 1.06 1.06 pCill pCill :zn.{jS 176 176 178 178 1.01 1.01 pCiIl pCiIl Co-GO 123 123 129 129 1.05 1.05 September*03 E387()'162 E387()'162 Milk Milk pCill pCill Sr*89 100 100 80 80 0.80 0.80 pCiIl pCiIl Sr*90 14 14 II II 0.79 0.79
- 1*131 LL=
LL= radiocbemicalseparauoo radiocbemicalseparauoo analysis analysis J.g J.g
(-
(- c c
(( ('
(' ((
.; TABt~J*3 PPL REMP LABORATORY PPL REMP LABORATORY SPIKE SPIKE PROGRAM PROGRAM ;;
ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACI1VITYRADIOACI1VITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2003 2003 FRAMATOME ANP FRAMATOME ANP ENVIRONMENTAL ENVIRONMENTAL LABORATORY LABORATORY (Page 11 of5)
(Page of5)
Identification Identification Analytlcs Analytlcs Framatome Framatome FramatomrlAnalytlcs FramatomrlAnalytlcs MonthIYtar MonthIYtar No.
No. Medium Medium Units Units Nuc:Ude Nuc:Ude Calc:nl.ted Results (a)
Calc:nl.ted Results (a) Results (a)
Results (a) Ratio Ratio Marcll-03 Marcll-03 IDS7)*J86 Sedimt:l1t Sedimt:l1t pC.1I:g pC.1I:g Ce-J41 358 :I: 18 358 :I: 18 351 :!: 14 351 :!: 14 0.98, 0.98, pC1I\g pC1I\g Cr*SI 508 508 :t :t 2S2S 511 :t:
511 :t: 4141 1.01 1.01 pC1I\g pC1I\g Cs-134 186 186 :t :t 9 9 189 :t 189 :t 6 6 1.02 1.02 pC1I\g pC1I\g Cs-131 497 497 :t :t 2S2S 536 :t 536 :t 9 9 1.08 1.08 pCiltg pCiltg Co.S8 96 :1:5 96 :1:5 97 :!:
97 :!: S 1.01 1.01 pCiltg pCiltg Mn-54 ' 133 133 :t :t 6565 132 :t 132 :t II II 0.99 ,,
0.99 pC1I\g pC1I\g Fe-59 98:5-98:5- 104 :t:
104 :t: 7 7 1.06 1.06 pC1I\g pC1I\g Zn-65 192 192 ;: ;: II 197 :tl0 197 :tl0 1.03 1.03 pCiltg pCiltg Co-60 335 335 :t :t 17 17 340: 6 340: 6 1.01 1.01 Marcll-03 Marcll-03 B3575*186 Mill:
Mill: pCiIl ,,
pCiIl 1*131 75:1:3' 75:1:3' 73 :t 9.
73 :t 9. 0.91.
0.91.
pCiIl pCiIl Cc-141 . , 188 ':1:17 188 ':1:17 193' 193' 7+/-
+/- 7 1.03 ..
1.03 pCiIl' pCiIl' Cr.51 261:t: 35 261:t: 35 244' :t:n 244' :t:n 0.91 ""
0.91 pan' pan' Cs-134 ' 98 :t 98 :t S 9S ::I:
- I: 44 0.9711,:,:
0.97 pCiIl pCiIl Cs-137 ' 211 :t 211 :t 2222 221:6 221:6 1.02 1.02 pC'II1' pC'II1' Co.58 51 '+/-'2
51 '+/-'2 50 3 50 +/-
+/- 3 0.98 0.98 pan pan Mn-54 70 70 :t 3
- t 3 ;; 70 :1:4 70 :1:4 1.00 1.00 pCt/I pCt/I Fe-59 51 :I:
51 :I: 22 51 :I:
51 :I: S 1.00 1.00 pCiIl pCiIl Zn-65 101 :t 101 :t 5 5 101 :: 88 101 1.00 1.00 pCt/I pCt/I Co-60 176 176 :t :t 16 16 .79:1: 4
.79:1: 4 1.02, 1.02, Marcll-03 Marcll-03 £3576*186 APFilter APFilter pCi pCi Ce-141 160:!:
160:!: 66 143 143 :2 :2 0.89 0.89 pCi pCi Cr.SI; 227:!:
227:!: 88 219 219 :I::I: 1111 0.96 0.96 pCi pCi CsJ34 83 :!:
83 :!: 33 78 :I:
78 :I: 22 0.94 0.94 pCi pCi Cs-137 185 185 :!: :!: 66 179 ':
179 ': 3 3 0.97 0.97 pCi pCi Co.S8 4j ':!:
4j ':!: 22 41 :I:
41 :I: 22 0.96 0.96 pCi pCi Mn*S4 S9 :t S9 :t 2 2 S9:1: 2 S9:1: 2 0.99 0.99 pCi pCi Fe-S9 44 :t:
44 :t: 22 4S :I:
4S :I: 22 "" 1.01 1.01
.... ,, pCi' pCi' Zn-65 86 :t:
86 :t: 33 87 :t:4 87 :t:4 1.01 1.01 pCi pCi C0-60 149 149 :t :t SS 133 :t:
133 :t: 22 0.89 0.89 J*I0
- J, '. .t.t (a) Counting (a) Counting error error is two standard is two standard deviations.
deviations.
TABLEJ*3 PPL REMP LABORATORY PPL REMP LABORATORY SPIKE SPIKE PROGRAM PROGRAM ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOAcrIVITY RADIOAcrIVITY CROSS CROSS CHECKCHECK PROGRAM PROGRAM -- 2003 2003 FRAMATOME ANP FRAMATOME ANP ENVIRONMENTAL ENVIRONMENTAL LABORATORY LABORATORY of5)
(Page 22 of5)
(Page IdenUDeaUon IdenUDeaUon Analyuc:s Analyuc:s Framatome Framatome Fnnu.tonltl AlIal)'Uc:s Fnnu.tonltlAlIal)'Uc:s MonthlVear MonthlVear No.
No. Mediunl Mediunl Units Units NUclide Calculated !al Results !al NUclide Calculated Results Results <al Results <al RaUo RaUo M.arch-OJ E.3S17*186 APFll!.c.r APFll!.c.r pCi pCi Ce.141 Ce.141 133 ::t S 133 S 121 ::t 22 121 0.91 0.91 pCi pCi Cr*S1 189 :t 189 :t 77 172 :t 172 :t 99 0.91 0.91 pCi pCi CsI34 CsI34 69 :t 69 :t 22 62;t 11 62;t 0.89 0.89 pCi pCi Cs-137 Cs-137 154 :t 154 :t 55 153 ;t 153 ;t 33 0.99 0.99 pCi pCi <:0.58
<:0.58 36 ::t 11 36 36 36 :t 22 0.99 0.99 pel Mn-54 Mn-54 50 :t 50 :t 2 2 50 :t 50 :t 2 2 1.01 1.01 pel Po-59 Po-59 36 :t 36 :t 1 1 40 :2 40 :2 1.11 1.11 pCi pCi Zn-65 Zn-65 72 :t 72 :t 33 71 :t 71 :t 44 0.98 0.98 pCi pCi <:0.60
<:0.60 125 :t 125 :t 44 113' ;t 113' ;t 22 0.90 0.90 M.arch-03 E3578*186 APFJl!.c.r APFJl!.c.r pel <:0.141
<:0.141 171 171 :t 6
- t 6 162: 22 162: 0.95 0.95 pCi pCi Cr*51 242 242 :t
- t 8 8 235 235 :t:t 11 11 0.97 0.97 pCi pCi CsI34 CsI34 89 89 :t 3
- t 3 82 :t 82 :t 2 2 0.93 0.93 pel Cs-137 Cs-137 197 197 :t 7
- t 7 200 :t 33 200 1.02 1.02 pCi pCi <:0.58
<:0.58 46 46 ;t
- t 22 44
- t 44 :t 2 2 0.96 0.96 pCi pCi Mn-S4 Mn-S4 63 63 :t
- t 2 2 68 :t 68 :t 22 1.08 1.08 pel Po-59 Po-59 41 :t 2 41 :t 2 53 :t 53 :t 2 2 1.12 1.12 pCi pCi Zn.6S Zn.6S 91 :: 33 91 95:1: 44 95:1: 1.05 1.05 pCi pCi <:0.60
<:0.60 159 :: 66 159 148:1: 22 148:1: 0.93 0.93 Juno-03 E3770-186 APFllter APFllter pel Ce.141 Ce.141 230:8 230:8 209:1:
209:1: 22 0.91 0.91 pel Cr*Sl 194 :I: 1 194 1 190 ::
190 11 11 0.98 0.98 pCi pCi CsI34 CsI34 84 :t 84 :t 33 78 :t 78 :t 22 0.93 0.93 pCi pCi Cs-137 Cs-137 188:7 188:7 191 ::
191 33 1.02 1.02 pCi pCi <:0.58
<:0.58 76 :: 33 76 74 74 :t 2 2 0.98 0.98 pel pel MIl*54 lSI :t; lSI 5
- t; 5 157 157 3
- t; 3
- t; 1.04 pCi pCi Fo-59 Fo-59 81 :t; 81 3
- t; 3 85 85 3
- t; 3
- t; 1.04 pCi pCi Zn.65 Zn.65 148 :t; 148 5
- t; 5 157 157 :t
- t 55 1.06 1.06 pCi pCi <:0.60
<:0.60 108 :t; 108 :t; 44 100 :t 100 :t 2 2 0.92 0.92 1*11 (a) Counting e.rroris (a) e.rroris two two standard standard deviations.
deviations.
C
c,c, TAnCr..J-3 TAnCr..J-3 cc PPL PPL REMP REMP LABORATORY LABORATORY SPIKESPIKE PROGRAM PROGRAM ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVITY RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2003 2003 --
FRAMATOME ANP FRAMATOME ANP ENVIRONMENTAL ENVIRONMENTAL LABORATORY LABORATORY (pnge30f5)
(pnge30f5)
I.'entmcation I.'entmcation Analytlc::9 Analytlc::9 Fnmltome Fnmltome Fnmatome! Anllytla Fnmatome!Anllytla MonO,/Yell" MonO,/Yell" No.
No. Mrdlum Mrdlum Units Units Nuclide Nuclide C.lrnJattd RfSIllts CI)
C.lrnJattd RfSIllts CI) RfSIlIts Ca)
RfSIlIts Ca) Ratio Ratio lunc-03 BJ77t*l86 APFiItet' pCi Ce-14 I 203 % 7 189 :t 2 0.93 pCi Cr*SI 171 % 6 170 % 10 0.99 pCi Csl34 74:3: 3 69:t 2 0.94 pCi Cs-137 1605 :t 6 170 :t 3 l.oo pCi Co.58 67:1: 2 66 :t 2 0.99 pCi MrrS4 133 +/- .5 142 % 3 1.06 pCi Pe-59 71 :t 2 78 = 3 1.09 pCi Zn-6S 130:1: S 138 = S 1.06 J~:' ,I \ .' .~
- , .' .~ ~,
pe;:i Co-60 95:1: 3 89 +/- 2 0.94 lune-03 BJ77Z*186 APPi1tet' pCi, Ce-141 225 :I: 8 203 :1:,2 0.90
~ '" l,', .~ " , ,
Po er.s'l' 190':!; t' 177:1: 10 0.93 pCi Cs134 82:1: 3 76'= 2 0.93
," 1.02 pCi Cs-137 183 % 6 186 = 3 pCi, Co.5! 74:1: 3 71:1: 2 0.96 pCi Mn.54 148 :t S 152 = 3 . 1.03 pCi Pe-59 "
79.+/- 3 84:1: 3 1.06 pCi Zn-6"S 144 :t S 154 +/- S. 1.07' pO Co-60 105 % 4 97 +/-.2 0.92 June-02 BJ713*186 Ol3rcoal Filtet' pel 1*131 66:1: 2 80:1: 7 1.22 BJ774*186 Ol3rcoal Filler fa 1*131 51 +/- 2. (1)
" BJ71S:is6 Ol3rcoal Filter pCi 1*131 59:t 2 68:t 6 1.15 J.ll J.ll
- J.'
" ' I Counting error (8) Counting (8) error is is two two staOOard staOOard deviatiOf'L'l.
deviatiOf'L'l.
TABLEJ*3 PPL REMP LABORATORY PPL REMP LABORATORY SPIKE SPIKE PROGRAM PROGRAM ::
ANALmcs ANAL mcs ENVIRONMENTAL ENVIRONMENTAL RADIOACflVITY RADIOACflVITY CROSS CROSS CHECK CHECK P~OGRAM ** 2003 2003 FRAMATOME ANP FRAMATOME ANP ENVIRONMENTAL ENVIRONMENTAL LABORATORY LABORATORY (Page 4 (Page 4 of of 5) 5)
Idenllftc:aUon Idenllftc:aUon AnalyUaI AnalyUaI Frllll1&tomt Frllll1&tomt FramatomtiAnalyUaI FramatomtiAnalyUaI MOIIUlIYear No. Medium Units NucUde Calculated Results (a) Results (a) RaUo Septc.mbe.r-03 83891*186 Milk pCiIl 1*131 7S ;t 2 83 ;t 8 1.10 pCiIl a,.141 188 :t 11 191 :I: 6 1.01 pCiIl Cr*SI SIO ;t 87 S43 ;t: 3S 1.06 pCiIl Cf.134 261 ;t: 23 24S:l:6 0.94 pCiIl Crl37 193 ;t 12 196:1: 5 1.02 pCiIl COOSS 216 :I: 15 I 214 ;t: 6 0.99 pCiIl M.n-.54 203 ;t 14 187 :t S 0.92 pCiIl Fc>S9 173:1: 10 173 :t 7 1.00 pCiIl Zn-6S 385:1: SO I 39S :I: 12 1.03 pCiIl <=0-60 270 :t 24 283.:1:5 1.0S Deeember-03 83977*186 Cwtoal Fllte.r pCi 1*131 76:1: 2.5 85 :t 6 1.12 83978*186 Cwtoal Fllla' pCi 1*131 68;t 2.3 78;t: 6 US E3979*186 Cwtoal Fllte.r pCi 1-131 86 ;t: 2.9 94:1: 6 1.09 J*13 (n) Counlinq (n) Counlinq etrOf C
C is two etrOf is stanJanl deviations.
two stanJanl deviations.
cc
c c PPL REMP LABORATORY PPL REMP TA(~~J.3 LABORATORY SPIKE SPIKE PROGRAM PROGRAM ..
ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVITY RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2003 2003 FRAMATOME ANP FRAMATOME ANP ENVIRONMENTAL ENVIRONMENTAL LABORATORY LABORATORY (page 55 of (page of 5) 5) ..
COMMENTS COMMENTS Framatome Framatome ANP unable ANP to a~alyze sample.
unable to sample. Charcoal Charcoal cartridge cartridge damaged damaged during during shipmentshipment from from Analytlcs.
Analytlcs.
- .. ('
(' ~
.. !! I..I.. .....
" . I.
I .
ii
+
+ .'
,, , 1
, 1 J*14 I*
TABLEJ-4 TABLEJ-4 DOE -- ENVlRONMENTAL DOE ENVlRONMENTAL MEASUREMENTS MEASUREMENTS LABORATORY LABORATORY (EML)
(EML)
QUALITY ASSESSMENT QUALITY ASSESSMENT PROGRAM PROGRAM (QAP)
(QAP)
~TOMEANPENVlRONMENTALLABORATO~Y (Page 1 (Page 1 of of 4) 4)
Identification Identification EMLKnown EMLKnown Fnunatome Fnunatome FnunatomdEML FnunatomdEML MonthIYear MonthIYear No.
No. Medium Medium Units Units Nuclide Nuclide Results Results Results Results Rallo Rallo March*03 QAP58 QAP58 AP Filler AP Filler Dq Dq Mn-S4 Mn-S4 43.8 43.8 43.2 43.2 0.99 0.99 Bq Bq Co-60 Co-60 33.5 33.5 33.5 33.5 1.00 1.00 Dq Dq 5r-90 5r-90 2.8 2.8 23 23 0.83 0.83 Dq Dq Cs-137 Cs-137 99.7 99.7 102.7 102.7 1.03 1.03 Dq Dq U-234 U-234 0.2 0.2 0.2 0.2 0.93 0.93 Dq Dq Pu*238 0.5 0.5 0.5 0.5 0.99 0.99 Dq Dq U-238 U-238 0.2 0.2 0.2 0.2 0.92 0.92 Dq Dq Pu-239 Pu-239 03 03 0.3 0.3 1.00 1.00 8q 8q Am-241 Am-241 03 03 0.3 0.3 0.98 0.98 Dq Dq Gross Alpha Gross Alpha 1.2 1.2 1.1 1.1 0.93 0.93 Bq Bq Gross Beta Gross Beta 1.5 1.5 1.4 1.4 0.94 0.94 March.Ql March.Ql QAP58 QAP58 Soil Soil Dqlkg Dqlkg K-40 K-40 636.0 636.0 65l.0 65l.0 1.03 1.03 Bqlkg Bqlkg Cs-137 Cs-137 1450.0 1450.0 1497.6 1497.6 1.03 1.03 Bqlkg Bqlkg Ae-228 Ae-228 51.6 51.6 54.9 54.9 0.95 0.95 Bqlkg Bqlkg U-234 U-234 120.0 120.0 IIS.7 IIS.7 0.96 0.96 Bqlkg Bqlkg Pu-238 Pu-238 21.9 21.9 23.5 23.5 1.07 1.07 Bqlkg Bqlkg U-238 U-238 125.0 125.0 122.9 122.9 0.98 0.98 Bqlkg Bqlkg Pu-239 Pu-239 23.4 23.4 24.4 24.4 1.04 1.04 Bqlkg Bqlkg Am-24 11 Am-24 IS.6 IS.6 12.4 12.4 0.79 0.79 (1)
(1)
March-OJ March-OJ QAP58 QAP58 Vegetati~ Dqlkg.
Dqlkg. K-40 K-40 1120 1120 1172 1172 1.05 1.05 Bqlkg Bqlkg Co-6O Co-6O 12.1 12.1 13.02 13.02 1.08 1.08 Bqlkg Bqlkg Sr-90 Sr-90 650 650 545.3 545.3 0.84 0.84 Bqlkg Bqlkg Cs*137 444 444 469.1 469.1 1.06 1.06 Dqlkg Dqlkg Pu-239 Pu-239 5.17 5.17 5.05 5.05 0.98 0.98 Dqlkg Dqlkg Am-241 Am-241 3.51 3.51 3.487 3.487 0.99 0.99 Bqlkg Bqlkg Cm-244 Cm-244 2.01 2.01 2.0S 1.02 1.02 I-IS I-IS
((
c* TA(~J.4 (_
(_
DOE -- ENVIRONMENTAL DOE ENVIRONMENTAL MEASUREMENTSMEASUREMENTS LABORATORY LABORATORY (EML)
(EML)
QUALITY ASSESSMENT QUALITY ASSESSMENT PROGRAM PROGRAM (QAP)
(QAP)
FRAMATOMEANPENVmONMENTALLABORATORY FRAMATOMEANPENVmONMENTALLABORATORY (Page 22 of (Page of 4) 4)
Identincation Identincation EMLKnown EMLKnown ~ Framatome Framatome Framatom<<1EML Framatom<<1EML MonthlYear MonthlYear No.
No. Medium Medium Units Units Nucllde Nucllde Results Results Results Results Ratio Ratio March*03 QAP58 QAP58 Water Water BqII BqII H-3 H-3 426.0 390.0 426.0 390.0 0.92 0.92 BqII BqII Co-60 Co-60 219.0 219.0 234.0 234.0 1.07 1.07 BqII BqII Sr*9O 4.1 4.1 4.3 4.3 1.07 1.07 DqII DqII Cs-134 Cs-134 29.4 29.4 30.5 30.5 1.04 1.04 BqII BqII Cs-137 Cs-137 59.6 59.6 63.8 63.8 1.07 1.07 BqII BqII U-234 U-234 2.3 2.3 2.'
2.' 0.90 0.90 DqII DqII Pu238 Pu238 3.7 3.7 3.3 3.3 0.91 0.91 BqII BqII U-238 U-238 2.1 2.1 2.2 2.2 1.02 1.02 BqII BqII Pu*239 4.2 4.2 3.9 3.9 0.92 0.92 BqII BqII Am-24 II Am-24 2.2 2.2 2.1 2.1 0.99 0.99 BqII BqII Or. Alpha Or. Alpha 418.1 418.1 3n.5 0.90 0.90 BqII BqII Gr. Dela Gr. Dela 682.4 682.4 627.5 627.5 0.92 0.92 September-03 September-03 QAP59 QAP59 AP filters AP filters Bq Bq Co-60 55.1 Co-60 55.1 56.0 56.0 1.02 1.02 Dq Dq Cs-137 Cs-137 54.8 54.8 57.1 57.1 1.04 1.04 Bq Bq Or. Alpha Or. Alpha 3.1 3.1 2.8 2.8 0.88 0.88 Bq Bq Gr. Beta Gr. Beta 3.9 3.9 3.1 3.1 0.80 0.80 (2)
(2)
Dq Dq Mn*S4 58.0 58.0 58.3 58.3 1.01 1.01 Sepiembei'-03 Sepiembei'-03 QAP59 QAP59 Soli ..
Soli nqlkg nqlkg AcTh-228 AcTh-228 50.8 50.8 51.7 51.7 1.02 1.02 Bqlkg Bqlkg Cs-137 Cs-137 1973.0 1973.0 2269.0 2269.0 I.lS Bqlkg Bqlkg K-40 K-40 488.0 488.0 547.0 547.0 1.12 1.12 J-lti J-lti II .'
TABLEJ4 TABLEJ4 DOE -- ENVIRONMENTAL DOE ENVIRONMENTAL MEASUREMENTS MEASUREMENTS LABORATORY LABORATORY (EML)
(EML)
QUALITY ASSESSMENT QUALITY ASSESSMENT PROGRAMPROGRAM (QAP)
(QAP)
FRAMATOME ANP FRAMATOME ANP ENVIRONMENTAL ENVIRONMENTAL LABORATORY LABORATORY (Page 33 of (Page of 4) 4)
Identification Identification El\lLKnown El\lLKnown Framatome Framatome Framatomc:lEML Framatomc:lEML MonlhIYear MonlhIYear No.
No. Medium Medium Units Units Nuclide Nuclide Results Results Results Results Ratio Ratio September"()3 September"()3 QAP59 QAP59 Water Water 8qIJ 8qIJ Co-60 469.4 513.0 Co-60 469.4 513.0 1.09 1.09 Bqll Bqll Cs*J34 60.1 60.1 63.0 63.0 1.05 1.05 Bqll Bqll Cs*137 73.9 73.9 80.3 80.3 1.09 1.09 Dqll Dqll Gross Alpha Gross Alpha 531.0 531.0 622.0 622.0 1.17 1.17 DqII DqII Gross Beta Gross Beta 1790.0 1790.0 1948.0 1948.0 1.09 1.09 Scptember"()3 Scptember"()3 QAP59 QAP59 Vegetation Vegetation Bqlkg Bqlkg (3)
(3) (3) (3)
(3) (3) (3)
(3)
J*17
(~
(( (( (.
(.
TABLEJ....44 TABLEJ !!
DOE -- ENVIRONMENTAL DOE ENVIRONMENTAL MEASUREMENTS MEASUREMENTS LABORATQRY LABORATQRY (EML) (EML)
QUALITY ASSESSMENT QUALITY ASSESSMENT PROGRAM PROGRAM (QAP)
(QAP) ii FRAMATOME ANP FRAMATOME ANP ENVIRONMENTAL ENVIRONMENTAL LABORAT9RYLABORAT9RY ,,
(page of 4)
(page 44 of 4)
COMMENTS COMMENTS 11 Low bias Low bias identified.
identified. Condition Report (~ No.
Condition Report No. 03-20) 03-20) generated generated by" by" Framatome Framatome Env.
Env. Lab Lab to:
to: investigate investigate Low Low Bias.
Bias.
22 Low bias Low bias identified.
identified. Condition Condition Report Report (CR (CR No.
No. 04-03) 04-03) generated generated by by Framatome Framatome Env.
Env. Lab Lab to to investigate II investigate LowLow Bias..
Bias.. ,,
33 ,i
, i :
- No vegetation s~triple was No vegetation was provided by DOEQAP provided by DOEQAP for for this this test period: ..
test period: II
.. !! "" ,\\
,\\
'., *t
- .,:., ,,)
,,)
J*18
TABLEJ....5 TABLEJ 5 DOE .... MAPEP DOE MAPEP ,,
N.UXEDANALYTEPERFORMANCEEVALUATIONPROq~
FRAMATOME ANP FRAMATOME ANP ENVIRONMENTAL ENVIRONMENTAL LABORATO~Y (Page 11 of (Page of 2)
- 2) ,,
Identification Identification MAPEP Known MAPEP Known Framatome Framatome Framatome/MAPEP Framatome/MAPEP MonthIYear MonthIYear No.
No. Medium Medium Units Units Nuclide Nuclide Results Results Results Results Ratio Ratio Evaluation Evaluation March-03 02*WIO Water Water BqIL BqIL 0.58 Am-24 1 0.58 0.58 0.58 1.00 1.00 Agreement Agreement BqIL BqIL Cs*134 421.00 421.00 398.12 398.12 0.95 0.95 Agreement Agreement BqIL BqIL Cs*U1 329.00 329.00 301.31 301.31 0.92 0.92 Agreement Agreement BqIL BqIL Co-51 51.00 51.00 52.44 52.44 0.92 0.92 Agreement Agreement 8qIL 8qIL Co-60 38.20 38.20 36.54 36.54 0.96 0.96 Agreement Agreement BqIL BqIL Fe-55 96.00 96.00 81.00 81.00 0.91 0.91 Agreement Agreement BqIL BqIL Mn*S4 32.90 32.90 31.53 31.53 0.96 0.96 Agreement Agreement BqIL BqIL Ni-63 136.50 136.50 126.00 126.00 0.92 0.92 Agreement Agreement BqIL BqIL Pu-238 0.83 0.83 0.85 0.85 1.03 1.03 Agreement Agreement BqIL BqIL Pu-239/40 0.03 0.03 False Positive False Positive (I)
(I)
BqIL BqIL Sr-90 12.31 12.31 11.09 11.09 0.90 0.90 Agreement Agreement DqIL DqIL U*233/234 1.54 1.54 1.63 1.63 1.06 1.06 Agreement Agreement BqIL BqIL U*238 1.60 1.60 1.63 1.63 1.02 1.02 Agreement Agreement DqIL DqIL Zn-65 516.00 516.00 509.10 509.10 0.99 0.99 Agreement Agreement March*03 03-S10 03-S10 Soil Soil DqlKg DqlKg Cs*134 238.00 238.00 248.60 248.60 1.04 1.04 Agreement Agreement 8q1Kg 8q1Kg Cs*131 832.00 832.00 848.80 848.80 1.02 1.02 Agreement Agreement 8q1Kg 8q1Kg Co-51 530.00 530.00 544.40 544.40 1.03 1.03 Agreement Agreement BqlKg BqlKg Co-6O 420.00 420.00 439.20 439.20 1.05 1.05 Agreement Agreement BqlKg BqlKg Mn*S4 131.00 131.00 143.10 143.10 1.05 1.05 Agreement Agreement BqlKg BqlKg Sr*90 714.00 714.00 626.60 626.60 0.88 0.88 Agreement Agreement 8q1Kg 8q1Kg K40 652.00 652.00 613.70 613.70 1.03 1.03 Agreement Agreement BqlKg BqlKg Zn-65 490.00 490.00 516.50 516.50 1.05 1.05 Agreement Agreement J*19 cc
c c TA[ ....
TA[
DOE-MAPEP DOE-MAPEP
.... J.S J.S MIXED ANALYfE MIXED ANALYfE PERFORMANCE PERFORMANCE (page 22 of (page of 2)2)
COMMENTS COMMENTS II False positive.
False positive. Condition Condition Report Report (CR (CR No.
No. CR CR 03-14) 03-14) generated generated by Framatome Env by Framatome Env Lab to investigate Lab to investigate and verify MDC and verify MDC ofof sample sample with with MAPEP.
MAPEP.
t .. ' f ,\ ,.
'/ ., ; ~.: 'I ~
- J . t
" r*,.
'" o~
" \
( ... :
1-20
- ;"'1. :'
TABLEJ-6 ENVIRONMENTAL RESOURCE ASSOCIATES (E~)
PROFICIENCY TESTING PROGRAM - 2003 j TELEDYNE BROWN ENGINEERING ENVIRONMENTAL SERYICES (TBE)
(Page 1 of2)
Identification ERA KoOWD THE ' THFJERA ERA MonthlYear No. Medium Units Nuclide Result (a) Results (a) Ratio Control Limits (b) EvaluatioD May-03 Rad-S3 Water pCiIl l-l3I 20.8 13.6 0.65 15.6-26.0 (1) pCiIl H-3 1200 0.96 678 - J820 Acceptable pCiIl Co-ro 63.8 69.9 1.10 55.1- 72.5 Acceptable pCiIl Cs-l34 75.7 73.5 0.97 67.0-84.4 Acceptable pCiIl Cs-137 ISO 165 1.10 141 - 159 (2) pCiIl Sr-89 31.3 37.0 1.18 22.6-40.0 Acceptable pCiIl Sf-90 27.4 23.5 0.86 18.7 - 36.1 Acccptable November.Q3 Rad-5S Water pCiIl 1-131 28.2 22.2 0.79 23.0-33.4 (3) pCiIl H-3 14300 1630 0.11 (4) pCiIl co-ro 27.7 28.4 1.03 19.0-36.4 Acceptable pCiIl Cs-134 23.4 21.7 0.93 14.7 - 32.1 Acceptable pCiIl Cs-137 64.2 63.6 0.99 55.S - 72.9 Acceptable pCiIl Sr-89 50.4 47.9 0.95 41.7- 59.1 Acceptable pCiIl Sr-9O 10.2 9.23 0.90 1.54 - 18.9 Acceptable pCiIl Or-Beta 168 161 0.96 124 -212 Acceptable (a) Results are the average of three measurements, reported in units of pCiIl.
(b) Per guidelines of the EPA'S National Standards for Water Proficiency Testing Criteria Document, December 1998.
J-21 c (~
cc ENVIRONMENTAL RESOURCE ENVIRONMENTAL TAl~J.6 RESOURCE ASSOCIATES ASSOCIATES (ERA) (ERA)
PROFICIENCY TESTING PROFICIENCY TESTING PROGRAM PROGRAM -- 2003 2003 !! II TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (TBE) (TBE)
(Page 2 (Page 2 of2) of2)
COMMENTS COMMENTS
" .. .' ': : .'.' .. .... ~
11 The stable iodine The stable iodine carrier carrier in in the the sample sample was was unaccounted unaccounted for for in in the the calculation.
calculation. When When recalculated, recalculated, the the correct correct result result of of 20.0 pCiIL 20.0 pCiIL was within acc~ptance criteria.
was within NCR 03~ 11 criteria. NCR 11 generated generated by by Teledyne toto Teledyne investigate:
investigate: condition. condition. ..::
.' 'I-'I-22 Although Cs-137 Although Cs-137 isis evaluated evaluated asas N, N, the the TBElERA TBElERA ratio ratio of of 1.10 1.10 faits faits within within limits limits of of 0.80 0.80 -- It20 It20 and and is is considered considered by by TBE TBE as as acceptable.
acceptable.
ii
. j ,
j , ,,
33 The decay correction The decay correction did did not not take take into into account account the the extended extended count count time. ~
time. When When recalculated,i,the recalculated,i,the correct
.. ~
correct result result of of 23.2 23.2 was was within within acceptance criteria.
acceptance criteria. NCR NCR 04-06 04-06 generated generated by by Teledyne Teledyne to to investigate investigate condition. condition. ';'; ..
!. t,' :',
t,' :', .1::
.1:: ,-I,-I .. :: :,1
- ,1 44 Due to recalculating Due to recalculating H-3 H-3 to to required required reporting units, itit decimal reporting units, place was decimal place was dropped.
dropped. The The co~~ct result result of 16300 isis within of 16300 within acceptance criteria.
acceptance criteria. NCR NCR 04-06 04-06 generated generated by by Teledyne Teledyne to to investigate investigate condition. condition. .;.; ..
- .~ tt J-22 J-22 11 ..
II
TABLEJ*7 ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVITY RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2003 2003 TELEDYNE QUALITY TELEDYNE QUALITY CONTROL CONTROL SPIKE SPIKE PROGRAM PROGRAM TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL S~RVICES (Page 11 o(5)
(Page o(5)
Analytles Analytles Identification Identification Calculated Calculated TBE TBE TBFJAnalyties TBFJAnalyties MonthlYear MonthlYear No.
No. Medium Medium Units Units Nuclide Nuclide Results Results Results Results Ratio Ratio March-OJ March-OJ £3585*396 Milk Milk pCill pCill Sr-89 133 80:
Sr-89 133 80: 0.60 0.60 (I)
(I) pCiJI pCiJI Sr-90 11.8 11.8 11.2 11.2 0.95 0.95 March-03 March-03 £3586-396 Milk Milk pCill pCill 74 J-131 74 75 75 1.01 1.01 pCill pCill Ce-141 173 173 168, 168, 0.91 0.91 pCill pCill Cr*Sl 246 246 243 243 0.99 0.99 pCiJI pCiJI Cs*134 90 90 83~ 0.92 0.92 pCiJI pCiJI Cs*131 200 200 201 201 1.04 1.04 pCill pCill Co-58 47 47 49:
49: 1.04 1.04 pCiJI pCiJI Mn-S4 64 64 65 ::
65 1.02 1.02 pCiIl pCiIl Fc-59 47 47 53 53 1.13 1.13 pCill pCill Zn-65 93 93 114 114 1.23 1.23 (4)
(4) pCiJI pCiJI Co-6O 162 162 169 169 1.04 1.04 March-OJ March-OJ £3588*J96 APFilter pCi pCi Ce-141 224 224 239 239 1.01 1.01 pCi pCi Cr-51 318 318 348 348 1.09 1.09 pCi pCi Cs*134 117 117 JOI JOI 0.86 0.86 pCi pCi Cs*137 259 259 217 217 1.01 1.01 tt pCi pCi Co-5S 60 60 66 66 1.10 1.10 pCi pCi Mn-S4 83 83 97 97 1.11 1.11 pCi pCi Fc-59 61 61 80j 80j 1.31 ..
1.31 (2)
(2) pCi pCi Zn-65 120 120 l52 l52 1.21 1.21 pCi pCi Co-60 209 209 223 223 1.07 1.07 pCi pCi Fe*55 106 106 138 138 l.lO l.lO (4)
(4)
March-Ol March-Ol £3587*396 Charcoal Filler Charcoal Filler pCi pCi I-Ill 74 74 68 68 0.92 0.92 J*23 c.c. ((
c-c- ((
TABLr.;J-7
((
ANALYTICS ANAL YTICS ENVmONMENT ENVmONMENTAL AL RADIOACTIVITY RADIOACTIVITY CROSSCROSS CHECKCHECK PROGRAM PROGRAM -- 2003 2003 TELEDYNE QUALITY TELEDYNE QUALITY CONTROL CONTROL SPIKESPIKE PROGRAM PROGRAM
"" TELEDYNE TELEDYNE BROWN BROWN ENGINEERING ENGINEERING ENVmONMENTAL ENVmONMENTAL SERVICES SERVICES (page 2 (page 2 of5) of5)
Analytlcs Analytlcs MonthlYear Identification Identification
- (( ',f
',f 1 1
Calculated Calculated THE THE TBFiAnaJytlcs TBFiAnaJytlcs No.
MonthlYear No. Medium Medium Units' Units' Nuclide Nuclide Results Results Resul'ts Resul'ts Ratto Ratto June-03 June-03 B3747-396 B3747-396 Milk Milk pClII pClII Sr-89 85 Sr-89 85 89j 89j 1.05 1.05 pCiII pCiII Sr-90 Sr-90 23 23 20:
20: 0.87 0.87 I*
June-03 B3748-396 June-03 B3748-396 Milk Milk pC'1II pC'1II 1-131 1-131 103 103 liS liS 1.12 1.12 pClIi pClIi Ce*141 283 283 285 285 1.01 1.01 pCiII pCiII Cr*SI 239 239 266,,
266 l.ll l.ll pClII pClII Cs*134 103 103 99; 99; 0.96 0.96 pClII pClII Cs*137 230 230 236 236 1.03 1.03 pClII pClII CO-58 pCui pCui CO-58 Mn.S4 93 93 106 106.. ,, 1.14 1.14 Mn.S4 186 186 190II 190 1.02 1.02 pClII pClII Fe-59' Fe-59' 99' 99' 108 108 1.09.
1.09.
r':. ,, "" ."~,
.' f' "" ~.'.' .... ,J 7:. :":"
7:. ~
pClII pClII Zn~6S 181 181 208 208 I.IS:
I.IS:
pClII r':.
f' ,J :: '- ~
- '- II pClII C0.60' C0.60' 132 132 142,,
142 1.08 1.08 June-03
-,,>- "" ii June-03 B37So.396 B37So.396 APFilter APFilter "" pCi' pCi' Ce-14'1 Ce-14'1 248 248 238 238 0.96 0.96 pCi' pCi' Cr-SI Cr-SI 209 209 239 239 1~14 pCi pCi Cs.t34 Cs.t34 91 91 79:
79: 0.87 0.87 pCi pCi Cs-137 Cs-137 202 202 189 189 0.94 0.94 pCi pCi Co-58 Co-58 81 81 71 ::
71 0.88 0.88 II pCi pCi Mn-54 Mn-54 163 163 164 164 1.01 1.01 pCi pCi Fe-59 Fe-59 87 87 91 ::II 91 1.05 1.05 pCi pCi Zn-6S Zn-6S 159 159 ISS 0.91 0.91 pCi pCi Co-60 Co-60 116 116 109 109 0.94 0.94 pCi pCi Fe-55 Fe-55 97 97 160 160 1.65 1.65 (3)
(3)
June-03 June-03 B3749*396 Charcoal Filter Charcoal Filter pCi pCi 1*131 62 62 78' 78' 1.26 1.26 (4)
(4)
"'i"
"'i" J*24 j,
j,
TABLEJ*7 ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACfIVITY RADIOACfIVITY CROSS CROSS CHECK CHECK :pROGRAM* 2003 2003 TELEDYNE QUALITY TELEDYNE QUALITY CONTROL CONTROL SPIKE SPIKE PROG~
TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES tt (Page 3 (Page 3 of5) of5)
Analyties Analyties Identification Identification Calculated Calculated TB~ TBFlAnalyUcs TBFlAnalyUcs Month/Year Month/Year No.
No. Medium Medium Units Units Nuclide Nuclide Results Results Results Results Ratio Ratio September-03 September-03 E3898*396 Milk Milk pCiJI pCiJI Sr*89 100 100 45:
45: 0.45 0.45 (l)
(l) pCill pCill Sr*90 14 14 13 ::
13 0.93 0.93 September-03 September-03 E3899*396 Milk Milk pCiJI pCiJI I-13l 74 74 73 73 0.99 0.99 pCill pCill Ce-141 86 86 85',,
85' 0.99 0.99 pCill pCill er*Sl 233 233 220 220 0.94 0.94 ii pCill pCill Cs*l34 119 119 l06 l06 0.89 0.89 pCiJI pCiJI Cs*137 88 88 90!
90! 1.02 1.02 pCiJI pCiJI Co-S8 99 99 96:
96: 0.97 0.97 pCiJI pCiJI Mn*54 93 93 95:
95: 1.02 1.02 pCiJI pCiJI Fe*59 79 79 84' 84' 1.06 1.06 pCiJI pCiJI ZO-6S 176 176 187, 187, 1.06 1.06 pCiJI pCiJI Co-60 123 123 132 132 1.07 1.07 September*03 E3901*396 APFiller APFiller pCi pCi Ce-141 77 77 79:
79: 1.03 1.03 pCi pCi er*51 210 210 227 227 1.08 1.08 pCi pCi Cs*134 108 108 93 93 0.86 0.86 pCi pCi Cs*137 79 79 70 70 0.89 0.89 pCi pCi Co-S8 89 89 80 ii 80 0.90 0.90 pCi pCi Mn-54 84 84 73 73 0.87 0.87 pCi pCi Fe-59 71 71 74, 74, 1.04 1.04 pCi pCi Zn-65 158 158 143 143 0.91 0.91 pCi pCi Co-60 III III 93' 93' 0.84 0.84 pCi pCi Fe-55 112 112 144 144 1.29 1.29 (4)
(4)
September.03 September.03 E3900-396 Charcoal Filter Charcoal Filter pCi pCi 1*131 86 86 74 74 0.86 0.86 November-03 November-03 E3790-396 Milk Milk pCill pCill Sr*89 168 168 185 185 1.10 1.10 pCill pCill Sr-90 17 17 19 19 1.12 1.12 J.2S J.2S c
c
((
TAUa..&lIJ*7
((
ANALYTICS ANAL YTICS ENVIRONMENTALENVIRONMENTAL RADIOACl1VITY RADIOACl1VITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2003 2003 TELEDYNE QUALITY TELEDYNE QUALITY CONTROL CONTROL SPIKE SPIKE PROGRAM PROGRAM TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (Page 44 of (Page of 5)
- 5) ,,ii AnalyUa AnalyUa II II Identification Identification Caltulated Caltulated THE THE THFJ Analytlcs THFJAnalytlcs MonthIVear MonthIVear No.
No. Medium Medium Units Units Nudlde Nudlde Results Results Resuits Resuits Ratio Ratio November*03 E3971*396 Milk Milk pCi/1 pCi/1 1*131 90 90 871 871 0.97 0.97 pCi/1 pCi/1 Ce-141 202 202 186 186 0.92 0.92
- pCi/1;
- pCi/1; Cr*SI 280 280 281 281 1.03 1.03
.... pCi/1 pCi/1 Cs-134 t3S t3S ,119
,119 0.88 0.88 pCi/1 pCi/1 Cs-137 129 129 116 116 0.90 0.90
-- pCi/1 pCi/1 Co-58 III III III III 1.00 1.00
"" "" ,, 'pCiI1"
'pCiI1" Mn-S4 173 173 17(;
17(; 1.02 1.02
,",1;" **
,",1;" .t
.t 7 ".
7 ". ~ **
.... pC"JII ,,
.. pC"JII Fe-S9 Fe-S9 ""102 102 941 941 '0.92
'0.92
.... ,". '~:
,". (( ,, pCi/1 pCi/1 Zn-6S* 197 197 190 190 ,'0.96
,'0.96
\
\
,I"
,I" pCi/1 pCi/1 C0-60 C0-60 ISS ISS 140 140 0.90 0.90 II c;, II November-03.;:
c;, November-03.;: p,,! E3973-396 E3973-396 ",,'<;:1 :,"APFilter ..
- ,"APFilter pCi' ,, "" ,)':.')
pCi' Ce-14f' r' r' !!
",,'<;:1 ,)':.') Ce-14f' "" 142 142 144 144 1.01 1.01 pCI pCI Cr-SI Cr-SI 198 198 203 203 1.03 1.03
~ :: .'"
,:. ,. ';i'
,. ';i' pCi pCi Cs-l34 Cs-l34 96 96 9O!
9O! 0.94 0.94 Cs-137
.... :: {-,,' "0,91,, .... ,,
pCi" pCi" Cs-137 "0,91,, ",0.93
",0.93 --
0'0'.. :: "" 00 '( ','
',' 8Sj
{-,,' ....-.
..-. ;' :~;, :y
- y '( 8Sj "" ii
.. ii,,":-,,
ii,,":-,,
,, 78'"
78'"
"f~
pCi' Co-S8" ;; 8O,'
pCi' Co-S8" II -"
- " 8O,' 1.03 1.03 II pCI pCI Mn-S4 Mn-S4 122 122 11S 11S 0.94 0.94
"" ,pCI
,pCI Fe-59 Fe-59 72 72 72:
72: 1.00 1.00 pCI pCI Zn-6S Zn-6S 139, 139, 121 0.87 k (+
(+ ,, ;;
,, 121 0.87 pCI pCI Co-60 Co-60 109 109 102 102 0.94 0.94 pCI pCI Fe-55 Fe-55 96 96 62:
62: 0.65 0.65 (5)
(5)
November-03 November-03 E3972*396 Charcoal Filter Charcoal Filter pCI' pCI' 1-131 1-131 77 77 67:
67: 0.87 0.87 J-26 J-26
',\,
',\, ,"
," ,, ii 1
1
TABLEJ*7 ANALYTICS ENVIRONMENTAL ANALYTICS ENVIRONMENTAL RADIOACTIVITY RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2003 2003 TELEDYNE QUALITY TELEDYNE QUALITY CONTROL CONTROL SPIKE SPIKE PROGRAM PROGRAM TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (Page 55 of (Page of 5) 5)
COMMENTS COMMENTS 1
1 Incorrectly calculated.
Incorrectly calculated. The The recalculated recalculated March March & September Sr*89 results
& September results ofof 138 138 & 95.8 pCUL.
& 95.8 respectively, are pCUL. respectively, are acceptable.
acceptable.
The efficiency required The efficiency required for for these these samples samples is is different different than than the the efficiency efficiency forfor regular regular samples.
samples.
NCR 04-02 NCR 04-02 generated generated byby Teledyne Teledyne to to investigate investigate conditon.
conditon.
2 2 Using only Using only the the results results from'the from'the 1099.2 1099.2 keYkeY photon, photon, the the Fe-59 Fe-59 would would ~e 71 71 pCi.
pCi. which which is is acceptab~e. Coincidental Coincidental summing summing occurs occurs only only with significant Fe-59 with significant Fe-59 activity activity levels.
levels. Therefore, Therefore, there there isis no no impact impact onon environmental environmental samples.
samples. ..
NCR 04-02 NCR 04-02 generated generated byby Teledyne Teledyne to to investigate investigate condition.
condition.
3 3 Reprocessed to Reprocessed to separate separate Fe-55 Fe-55 peak.
peak. Reprocessed Reprocessed result result ofof 103 103 total total pCi pCi isis acceptable.
acceptable. NCR NCR 04-Q2 04-Q2 generated generated byby Teledyne Teledyne toto investigate investigate the condition.
the condition.
4 4 Acceptable with Acceptable with warning.
warning. Reported Reported result result falls falls within within 0.70-0.80 0.70-0.80 or or 1.20-1.30.
1.20-1.30.
5 5 NCR 04-07 generated NCR 04-07 generated byby Teledyne Teledyne to to investigate investigate condition.
condition. The The mylar mylar film film (not (not aa filter) filter) from from Analytics Analytics is is not not typical typical of of samples samples received received from from Teledyne clients.
Teledyne clients. Since Since the the analytics analytics sample sample waswas mylar, mylar, thethe laboratory laboratory tried tried to to adjust adjust to to the the new new matrix matrix by by ashing ashing the the filter filter before before analysis.
analysis.
Analytics thought Analytics thought Teledyne Teledyne waswas performing performing aa direct direct count count of of the the mylar mylar (no (no preparation preparation or or chemical chemical separation).
separation).
Teledyne believes Teledyne believes that that some some of of the the Fe-55 Fe-55 was was lost lost during during ashing.
ashing.
Teledyne Teledyne hashas changed changed their their request request to to Analytics Analytics and and will will now now receive receive glass glass fiber fiber filters filters for for analysis.
analysis.
In addition, In addition, Teledyne Teledyne has has also also verified verified the the validity validity of of their their Fe-55 Fe-55 efficiencies efficiencies by comparing to by comparing to a a standard standard from from a a different different standards standards lot.
lot.
J-21 J-21
(~ cc
\\ :'
C C TA(~J-8 ((
PPL PPL REMP REMP LABORATORY LABORATORY SPIKE SPIKE PROGRAM PROGRAM ii ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVITY RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2003 2003 TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (page 10f5)
(page 10f5) ,, ,, ,, 1'-,
1'-,
MonthIYear Identlncatlon Identlncatlon Analytic!
Analytic! ii TBE, TBE, TBFJAnalytlcs TBFJAnalytlcs MonthIYear No.
No. Medium Medium Units Units Nuclide Nuclide Calculated Calculated Results Results (a) (a) II Results Results (a) (a) Ratio Ratio Marcb*03 83573-186 83573-186 Sediment Sediment pCiJkg pCiJkg Ce-141 Ce-141 358 :!: :!: 18 18 358 409:!: 17 409:!: 17 1.14 ""
1.14 pCiJkg pCiJkg Cr-SI Cr-SI 508 508 :!: :!: 25 25 576 :!: :!: 99 99 576 1.13 1.13 pcilkg pcilkg CS-134' CS-134' 186 :!:
186 :!: 99 180 180 :!: 99
- !: 0.97 0.97 pCineg pCineg Cs~lj7 497 :!:
497 :!: 2S 2S 598 598 :!: 19
- !: 19 1.20 1.20
,, "" pCiJkg pCiJkg Co-58 Co-58 96:!: S 96:!: S 116 116 :!: 13
- !: 13 1.21 1.21 pCiJkg pCiJkg Mn-54 Mn-54 133 :!:
133 :!: 65 65 157 157 :!: 13
- !: 13 ,, 1.18 1.18
- pCiJkg pCiJkg Pe-S9 Pe-S9 '98
- !
- 5
'98 :!:5 120 120 :!: 17
- !: 17 1.22 1.22 pCiJkg pCiJkg Zn*65 192 :!:
192 :!: II 271 271 :!: 23
- !: 23 1.41, 1.41, (I)
(I) pCiJkg pCiJkg Co-GO Co-GO 33S:!: 17 33S:!: 17 408 408 :!: 13
- !: 13 1.22 1.22
.. ~.' ",'
,~
March*03 83569-186 83569-186 Mille Mille pCiII pCiII 1~131: 75:!: 33 75:!: ,67.:!:-7,:
,67.:!:-7,: 0.89; 0.89; pCiIi pCiIi Ce~141; 188 188 17 +/-
+/- 17 188::t:
188::t: 8, 8, 1.00:
1.00:
pCin' pCin' Cr-SI Cr-SI 26?I':!: 3~
26?I':!: 262= 37 262= 37 0.98:
0.98:
pCiIi pCiIi Cs*134'"" 98:t: S 98:t: S 86 :!:
86 :!: 3, 3, 0.88, 0.88, pCW pCW Cs-i37' Cs-i37' 217 217 :!:--22
- !: 22.. 214 :!:
214 :!: 7. 7. 0.99.
0.99.
,. \\
pCiti pCiti C~~8 51:!: 2 51:!: 2 SO :t:4 SO :t:4 0.98,'
0.98,'
pCiIi pCiIi Mn-54 Mn-54 70:!: 33 70:!: 74 :t:
74 :t: 55 l.O5 l.O5 pCiII pCiII Pe*59 51 :!:
51 :!: 22 56 :!:6 56 :!:6 1.10 1.10 pCiII pCiII Zn-65 Zn-65 101,:!: S' 101,:!: S' 110 :t:
110 :t: 99 1.09 1.09 "" --
pCi/I pCi/I Co-GO Co-GO 176 =
176 = 16 16 173 :t:
173 :t: 55 0.98 0.98 March-03 March-03 83570-186 83570-186 APFilter APFilter pCi pCi Ce*141 151.:!: 55 153 = 77 151.:!: 153 = 1.01 1.01 pC(
pC( er-sl er-sl 215 215 :!: :!: 88 241 241 :!: 38
- !: 38 1.12, 1.12, pCi pCi CS-134 CS-134 79::t:3 79::t:3 67 67 :t:4.
- t:4. 0.84 0.84 pCi pCi Cs~137 175 :!:
175 :!: 66 180 180 = 99
= 1.03 1.03 pCi' pCi' C~S8 41 :!:
41 :!: II 4S:!: 6 4S:!: 6 1.09 1.09 pCi:
pCi: Mn~54 56:!: 22 56:!: 59.s:t:
59.s:t: 77 1.06 1.06
.pCL...
.pCL ... _. Pe-59
_. Pe-59 41:!: I*
41:!: 52.9:t:
52.9:t: 88 -- 1.29
1.29 (I)
(I) pCi ..
pCi Zn*6S 81 33 81 +/-
+/- 96.3:t:
96.3:t: 13 13 1.19 1.19
- ii ~ ,,
pCi pCi Co-GO 141 :!:'
141 :!:' S S 148:!:
148:!: 77 1.05 1.05 i!
i!
J*28
'; ~ :: t
- /,
/,
~ (.~.~*.~~i ,, "" ... ::
,, .. :: :: :: ... .... ,, l'l' II ~ .. IT, IT, Counting error (a) Counting (a) error is is two two standard standard deviations.
deviations.
TABLEJ*8 PPL REMP PPL REMP LABORATORY LABORATORY SPIKE SPIKE PROGRAM PROGRAM ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVITY RADIOACTIVITY CROSS CROSS CHEC~ PROGRAM PROGRAM -- 2003 2003 TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (Page 22 of (Page of 5) 5)
IdentificaUon IdentificaUon Aoalytics Aoalytics TDE TDE TDFJAoalyUcs TDFJAoalyUcs MonlblYear MonlblYear No.
No. Medium Medium Units Units Nuclide Nuclide Calculated Results (_)
Calculated Results (_) Results (II)
Results (II) Ratio Ratio March*03 El571*IB6 AP Filter AP Filter pCi pCi Cc-141 156 +/-
156 +/- 55 170 +/-
170 +/- 8 8 1.09 1.09 pCi pCi Cr*51 221 221 +/- +/- 88 255 255 +/-+/- 4646 US US pCi pCi Cs*134 81 +/-
81 +/- 33 65.3 +/-.5 65.3 +/-.5 0.81 0.81 pCi pCi Cs-137 180 180 +/- +/- 66 187 +/-
187 +/- 9 9 1.04 1.04 pCi pCi Co-58 42 42 +/- +/- 11 39.5 +/-
39.5 +/- 88 0.94 0.94 pCi pCi Mn*S4 58 +/-
58 +/- 22 59.1 +/-
59.1 +/- 77 1.02 1.02 pCi pCi Fe-59 43 +/-
43 +/- 22 51 +/-
51 +/- 99 1.19 1.19 pCi pCi Zn*65 84+/- 3 84+/- 3 110 +/-
110 +/- 13 13 1.31 1.31 (I)
(I) pCi pCi Co-60 146 +/-
146 +/- 55 148 +/-
148 +/- 11 1.01 1.01 March*03 E3572*186 Filter AP Filter AP pCi pCi Ce*141 182 182 +/- +/- 66 IBO +/-
IBO +/- 11 0.99 0.99 pCi pCi Cr*51 259 259 +/- +/- 9 9 240+/-
240+/- 40 40 0.93 0.93 pCi pCi Cs*134 9S +/-+/- 33 9S 76.3 +/-
76.3 +/- 44 0.80 0.80 pCi pCi Cs*137 211 :t 211 :t 77 217 +/-
217 +/- 99 1.03 1.03 pCi pCi Co-58 49 +/-
49 +/- 2 2 SIS:t 7 SIS:t 7 1.05 1.05 pCi pCi Mn*S4 68:t 2 68:t 2 75.5 +/-
75.5 +/- 77 1.11 1.11 pCi pCi Fe*59 50:t 2 50:t 2 60.3:t 9 60.3:t 9 1.21 1.21 pCi pCi Zn*65 98 +/-
98 +/- 33 IIS:t 14 IIS:t 14 1.17 1.17 pCi pCi Co-6O 170:t 6 170:t 6 173:t ,7 173:t ,7 1.02 1.02 March*03 El574*186 Water Water pCiIL pCiIL H*3 4463:t 230 4463:t 230 4840:t 176 4840:t 176 1.08 1.08 June*03 El776*186 Filter AP Filter AP pCi pCi Ce*141 152 +/-
152 +/- 55 157:t 157:t 17 17 1.03 1.03 pq pq Cr-SI 128:t 128:t 4 4 142 +/-
142 +/- 102 102 1.11 1.11 pCi pCi Cs-134 55 55 +/- +/- 22 58.3 +/-
58.3 +/- 88 1.06 1.06 pCi pCi Cs-137 123 :t 123 4
- t 4 147 +/-
147 +/- 14 14 1.20 1.20 pCi pCi CO-58 50 +/-
50 +/- 22 46.5:t 46.5:t 14 14 0.93 0.93 pCi pCi Mn*54 99:t 3 99:t 3 105:t 105:t 14 14 1.06 1.06 pCi pCi Fe*59 53 53 +/- +/- 22 63 +/-
63 +/- 19 19 1.19 1.19 pCi pCi Zn-65 97:t 3 97:t 3 IIS:t IIS:t 18 18 1.19 1.19 pCi pCi Co-60 71 :t 71 :t 22 87.9:t 87.9:t 10 10 1.24 1.24 J*29 (a) Counting (a) Counting error error is is two standard deviations.
two standard deviations.
C.C.
(( TAl.. J-8 TAl.. J-8 ((
PPL PPL REMP REMP LADORA LADORATORY TORY SPIKE SPIKE PROGRAM PROGRAM ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVITY RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAM PROGRAM -- 2003 2003 TELEDYNE DROWN TELEDYNE DROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (Page 33 of5)
(Page of5)
IdenUntation IdenUntation AnalyUcs TBE AnalyUcs TBE TBFJAnalytlcs TBFJAnalytlcs MonthIVear MonthIVear No.
No. Medlom Medlom Unlts Unlts Nuclide Calc:uJated ResultS (a)
(a)
Nuclide Calc:uJated ResultS Results (a)
Results (a) Ratio Ratio June-03 June-03 E3777A-186 E3777A-186 AP Filter AP Filter pCi pCi Ce-141, 238:!: 88 238:!: 267:!: 20 267:!: 20 1.12 1.12 pCi pCi er*51 201 :!: 77 201 :!: 112 176:!: 112 176:!: 0.88 0.88 pCi pCi Cs*134 87:!:
87:!: 33 91 :!:
91 :!: 8 8 1.05 1.05 pCi pCi Cs-137 194 %
194 % 77 219 %
219 % 1717 1.13 1.13 pCi pCi Co-58 78:!: 33 78:!: 13 84.3:!: 13 84.3:!: 1.08 1.08 pCi pCi Mn-S4 156 %
156 % 55 172:!: 17 172:!: 17 1.10 1.10 pCi pCi Fe*S9 83:!: 33 83:!: 107 %
107 % 2020 1.29 1.29 (1)
(1) pCi pCi Zn*65 IS3:!: 55 IS3:!: 23 179:!: 23 179:!: 1.17 1.17 pCi pCi Co-60 III %
III %4 4 II 127:!: II 127:!: 1.14 1.14
.. "I:'
"I:' ,, .. ,, ;; ~. II c.' ,.,. ::
c.' ~
June*03 E3778A.i86 E3778A.i86 APFilter APFilter pCi pCi Q-141 140:!:
140:!: 5 128 %
128 % 2020 0.91 0.91 ,,
.. --. .. "" ,t"
,t" :T"
- T" :..,;.,'
- ..,;.,' pCi, pCi, Cr-Sl: 118 £4:
118 £4: II 122'%; 89 122'%; 89 1.03'
II
,'" -~', 1.03' pCi pCi Cs-134 51:!: 2 51:!: 2 53.7:!: 66 53.7:!: 1.05, ii 1.05,
,~ . ,~' ':
': :: .,., pCi pCi Cs*137 1t4 %
1t4 '4'
%'4' 112~'12 0.98 0.98 1
1 pCi pCi Co-58 46:!: 22 46:!: 10 3S:!: 10 3S:!: 0.76 0.76
"" pCL* Mn-S4 92:!:3 92:!:3 96.2 :~/I'I 96.2 'LOS'
'LOS' pCi Fe-59 49:!: 2 49:!: 2 42.4:!: 18 42.4:!: 18 0:87, 0:87, pCL, Zn-65 89:!:'3 89:!:'3 74.1 %
74.1 % 1818 0.83, 0.83, pCi: Co-60 65% 2 65% 2 69.6:!: 7 69.6:!: 7 1.07 1.07 June-03 E3779-186 E3779-186 Charcoal Filter Charcoal Filter pCi pCi 1*131 66:!: 2;* 73.9:!: 3 73.9:!: 3 l.12 l.12 June-03 E3780-186 E3780-186 Charcoal Filter Charcoal Filter pCi pCi I- 131 59:!: 22 59:!: 68.6% 3 68.6% 3 1.16 1.16 June*03 E3781*186 Charcoal Filter.
Charcoal Filter. pCi' pCi' 1*131 ' 51 %2 51 %2 61.6:!: 44 61.6:!: 1.21 1.21
.. /'/' ....
,..;; ~ ,t
,t J*30 (a) Counting (a) Counting errorerror is two standard is two standard deviations.
deviations.
TABLEJ*8 PPL REMP LABORATORY PPL REMP LABORATORY SPIKE SPIKE PROGRAM PROGRAM ANALYTICS ENVIRONMENTAL ANALYTICS ENVIRONMENTAL RADIOAcnvITY TELEDYNE BROWN TELEDYNE RADIOAcnvITY CROSS BROWN ENGINEERING ENGINEERING ENVIRONMENTAL CROSS CHECKCHECK,, PROGRAM ENVIRONMENTAL ~ERVICES PROGRAM -- 2003 --
2003 (Page 44 of5)
(Page of5)
IdenUfication IdenUfication AnalyUcs AnalyUcs THE THE TBFJAnalytics TBFJAnalytics MontblYear MontblYear No.
No. Medium Medium Units Units Nuclide Nuclide Calculated Results Calculated Results (a)
(a) Results (a)
Results (a) Ratio Ratio September-03 E3889*186 Milk Milk pCiIl pCiIl 1-131 75:t:
75:t: 2 2 65.9 +/-
65.9 +/- 88 0.88 0.88 pCill pCill Ce*141 188 +/-
188 +/- 11 11 171 +/-
171 +/- 11 11 0.91 0.91 pCiIl pCiIl Cr-51 510 +/-
510 +/- 87 87 429 +/-
429 +/- 48 48 0.84 0.84 pCiIl pCiIl Cs-I34 261 +/-
261 +/- 23 23 212 +/-
212 +/- 55 O.SI O.SI pCiIl pCiIl Cs*137 193 +/-
193 +/- 12 12 181+/-
181+/- 88 0.94 0.94 pCiIl pCiIl Co-58 216 216 +/-
+/- IS 197 +/-
197 +/- 88 0.91 0.91 pCi/l pCi/l Mn-54 203 203 +/-
+/- 14 14 202+/-
202+/- 99 1.00 1.00 pCi/I pCi/I Fe*59 173 +/-
173 +/- 10 10 177 +/-
177 +/- IO IO 1.02 1.02 pCill pCill Zn*6S 385 +/-
385 +/- SO 368 +/-
368 +/- 16 16 0.96 0.96 pCi/l pCi/l Co-60 270 270 +/-
+/- 24 24 264 264 +/-
+/- 77 0.98 0.98 September*03 E3890*186 Water Water pCill pCill H-3 SOOO+/- 300 SOOO+/- 300 8240 +/-
8240 +/- 222 222 1.03 1.03 December-Ol E3981*186 Charcoal Filter Charcoal Filter pCi pCi l*ll1 77 +/-.
77 3
+/-. 3 83 +/-
83 +/- 33 1.07 1.07 December*03 E3982*186 Charcoal Filter Charcoal Filter pCi pCi 1*131 68 +/-
68 +/- 22 73 +/-
73 +/- 2 2 1.07 1.07 December-03 E398l*186 Charcoal Filter Charcoal Filter pCi pCi 1*131 86+/- 3 86+/- 3 92:t 55 92:t 1.07 1.07
)*31
(:(:
(a) Counting (a) Counting error error is two standard is two standard deviations.
deviations.
('
(' ((
TABLEJ-8 TABLEJ-8 PPL REMP PPL REMP LABORATORY LABORATORY SPIKE SPIKE PROGRAMi PROGRAMiII ANALYTICS ANAL YTICS ENVIRONMENTAL ENVIRONMENTAL RADIOACTIVITY RADIOACTIVITY CROSS CROSS CHECK CHECK PROGRAMPROGRAM -- 2Q03 2Q03 TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (Page 5 (Page 5 ofof 5) 5) :
j COMMENTS COMMENTS I"
i' 1
1 High Bias High Bias identified.
identified. Evaluation Evaluation of of results results requested requested by by PPL PPL via via email email on on April April 19, 2004.
19, 2004.
'I'"
I ',
j
'I
'I -:'
i i '
- i. '
I
'.. to ~ II ** .,
'!' to J*32
- I" I "t t tt !,
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'/" ,",
i . " '
TABLEJ-9 TABLEJ-9 DOE -- ENVIRONMENTAL DOE ENVIRONMENTAL MEASUREMENTS MEASUREMENTS LABORATORYLABORATORY (EML) (EML)
QUALITY ASSESSMENT QUALITY ASSESSMENT PROGRAM PROGRAM (QAP)
(QAP)
TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL S;ERVICES S;ERVICES (Page 11 of (Page of 4) 4)
II Identification Identification EMLKnown EMLKnown THE THE TBEJEML TBEJEML MonthlYear MonthlYear No.
No. Medium Medium Units Units Nuclide Nuclide Result Result Results Results Ratio Ratio March*03 QAP-S8 QAP-S8 AP Filter AP Filter Bq Bq Am*24 1 0.34 0.34 0.~4 1.00 1.00 Bq Bq Co-60 33.S 33.S 35:9 35:9 1.01 1.01 Bq Bq Cs*131 99.1 99.1 lQ.1 lQ.1 1.14 1.14 Bq Bq Or-Alpha 1.2 1.2 0.9II 0.9 0.73 0.73 (I)
(I)
Bq Bq Or-Beta 22 1.6 1.6 1.01 1.01 Bq Bq Mn-54 43.8 43.8 49.4 49.4 1.13 1.13 Bq Bq Pu*238 0.52 0.52 0.59 0.59 1.13 1.13 II Bq Bq Pu*239 0.3 0.3 0.4 0.4 1.06 1.06 8q 8q Sr-90 2.8 2.8 2.4 2.4 0.86 0.86 March*OJ QAP-58 QAP-58 Soil Soil Bqlkg Bqlkg Ac-228 57 57 70 70 1.23 1.23 (4)
(4)
Bqlkg Bqlkg Am-241 16 16 16 16 0.99 0.99 Bqlkg Bqlkg Bi*212 61 61 73 73 1.20 1.20 (4)
(4)
Bqlkg Bqlkg Bi*214 67 67 76 76 1.14 1.14 Bqlkg Bqlkg Cs-137 1450 1450 1883 1883 1.30 1.30 (2)
(2) 8q1kg 8q1kg K-40 636 636 80,6 80,6 1.27 1.27 (4)
(4)
Bqlkg Bqlkg Ph-212 58 58 75 75 l.29 l.29 (4)
(4)
Bqlkg Bqlkg Pb*214 71 71 79 79 1.11 1.11 Bqlkg Bqlkg Pu*239 23 23 2S 1.09 1.09 Bqlkg Bqlkg Sr-90 64 64 5t 5t 0.83 0.83 8q1kg 8q1kg Th-234 127 127 169 169 1.33 1.33 March-03 March-03 QAP-S8 QAP-S8 Vegetation Vegetation Bqlkg Bqlkg Co-60 12 12 It It 1.19 1.19 Bqlkg Bqlkg Cs-1"37 444 444 522 522 1.18 1.18 Bqlkg Bqlkg K-40 1120 1120 1360 1360 1.21 1.21 Bqlkg Bqlkg Sr-90 650 650 498 498 0.77 0.77 J*33
cc DOE -- ENVIRONMENTAL DOE ENVIRONMENTAL MEASUREMENTS
((
TABL~J*9 MEASUREMENTS LABORATORY LABORATORY (EML) (EML)
((
QUALITY ASSESSMENT QUALITY ASSESSMENT PROGRAM PROGRAM (QAP) (QAP) II TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (Page 2 (Page 2 of4) of4) !!
II IdenllflcntJon IdenllflcntJon EMLKnown EMLKnown TBE TBE TBFJEML TBFJEML MonthlYear MonthlYear No.
No. Medium Medium Units Units Nuclide Nuclide Result Result Reshlts Reshlts Ratio Ratio Marcb-03 Marcb-03 QAP*58 Water Water BqIl BqIl Am-24 I 2.13 2.13 ii 2.4 2.4 1.13 1.13 BqIl BqIl Co-60 234 234 252 252 1.08 1.08 BqIl BqIl Cs.134 , 31 31 31 31 ,, 1.02
1.02 BqIl BqIl Cs.137 64 64 72 72 1.12 1.12 BqIl BqIl Or*Alpha 378 378 484 484 1.28 1.28 (4)
(4)
BqIl BqIl Or-Beta ' 628 628 821 821 ,, 1.31
1.31 (4)
(4)
BqIl, BqIl, H*3, 390 390 418.
418. 1.07 ,,
1.07 BqIl BqIl Pu~238 . 3.3 3.3 4:0 4:0 1.20, 1.20, (3)
II BqIl BqIl Pu*239 3.9 3.9 4.6 4.6 1.16 1.16 4.3, 3.6, 3.6, J.',,
BqII.
BqII. Sr-90 4.3, 0,,84;.
0,,84;.
Sq,teinbei.03 ..
Sq,teinbei.03
~ 'I"r~'ir_""~ .", .,. :: """"
QAP59 QAP59
~ .... ~ ....
APFilter APFilter
"'-'" ~-, \~
Bq Bq Mn*S4
.;. J 58' 58' J.' 44
,, ff ,:
0.93 0.93 Bq ""
Bq Co-60 J
, 5S.l , 53.3, 53.3, 0.97.
0.97.
Sq,,,:
Sq,,,: Sr-gO,' . 2.1 ::
2.1 1:7 ..
1:7 0.81*
Bq~ Cs*137 , S4.8 si.2.
si.2. 0.93",
0.93",
Bq Bq U.234 . 0.4 0.4 0.4 0.4 0.92 0.92 B,q B,q Pii*238 0.2 0.2 0.2 0.2 1.00.. ,,
1.00 Bq Bq U-238 0.4 0.4 0.4 0.93 0.93 Bq Bq Pu*239 0.4 0.4 0.4 0.4 1.00 1.00 Bq ,,
Bq Am-241 0.4 0.4 0.4 0.4 0.90 0.90 Bq Bq Or-Alpha 3.1 3.1 3.1 3.1 1.00 1.00 Bq Bq Or-Beta 3.9 3.9 3.4 3.4 0.87 0.87 J*34 l.
l.
1" 1
.'.' j.'
j.'
\.
\ . .. ~ .. ,, (( ::
TABLEJ*9 DOE -- ENVIRONMENTAL DOE ENVIRONMENTAL MEASUREMENTS MEASUREMENTS LABORATO~Y (EML) (EML)
QUAUTY ASSESSMENT QUAUTY ASSESSMENT PROGRAM PROGRAM (QAP)
(QAP) !!
TELEDYNE BROWN TELEDYNE BROWN ENGINEERING ENGINEERING ENVIRONMENTAL ENVIRONMENTAL SERVICES SERVICES (Page 33 of4)
(Page of4)
Identification Identification EMLKnowD EMLKnowD TOE TOE TBElEML TBElEML MonthlYear MonthlYear No.
No. Medium Medium Units Units Nuclide Nuclide Result Result Resiaits Resiaits Ratio Ratio September-03 QAP59 Soil Soil Bqlkg Bqlkg K-40 488 488 511 511 1.06 1.06 Bqlkg Bqlkg Sf-90 80 80 10 10 0.81 0.81 Bqlkg Bqlkg Cs*137 1973 1973 2127 2127 1.08 1.08 Bqlkg Bqlkg Hi-212 S4 56 56 1.04 1.04 Bqlkg Bqlkg Pb-212 51 51 5~ 1.04 1.04 Bqlkg Bqlkg Bi-214 34 34 36 36 1.06 1.06 Bqlkg Bqlkg Pb-214 3S 3S 4~ 1.18 1.18 Bqlkg Bqlkg Ac-228 51 51 5~ 1.11 1.11 Bqlkg Bqlkg Th*234 116 116 145 145 1.2S 1.2S Bqlkg Bqlkg U-234 127 127 1~5 0.91 0.91 B.qlkg