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Independent Spent Fuel Storage Facility, Submittal of Annual Radioactive Effluent Release Report for 2015
	ML16130A656
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Site:	Oyster Creek
Issue date:	04/29/2016
From:	Stathes G L; Exelon Generation Co
To:	; Document Control Desk, Office of Nuclear Material Safety and Safeguards, Office of Nuclear Reactor Regulation
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ML16130A661	List: RA-16-039, Independent Spent Fuel Storage Facility, Submittal of Annual Radioactive Effluent Release Report for 2015;
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Exelon Generation RA-16-039 April 29, 2016 U.S. Nuclear Regulatory Commission Attn: Document Control Desk Washington , DC 20555 -0001 10 CFR 50.36a(a)(2) 10 CFR 72.44 ( d)(3) Technical Specification 6.9.1.d Oyster Creek Nuclear Generating Station Renewed Facility Operating License No. DPR-16 NRC Docket No. 50-219 lndependentSpent Fuel Storage Facility NRC Docket No. 72-15

Subject:

Annual Radioactive Effluent Release Report for 2015 Enclosed with this cover letter is the Annual Radioactive Effluent Release Report for the period January 1 to December 31 , 2015. This report includes the Oyster Creek Nuclear Generating Station Independent Spent Fuel Storage Facility.

If any further information or assistance i s needed , please contact John Renda , Chemistry Manager, at 609-971-2572.

Sincerely , Site Vice President Oyster Creek Nuclear Generating Station

Enclosure:

2015 Annual Radioactive Effluent Release Report cc: Administrator , USNRC Region I USNRC Senior Project Manager , Oyster Creek USNRC Senior Resident Inspector , Oyster Creek C r a i g Stewart , American Nuclear Insurers Exelon Generation Annual Radioactive Effluent Release Report 2015 Oyster Creek Generating Station Oyster Creek 2015 Annual Radioactive Effluent Release Report ANNUAL RADIOACTIVE EFFLUENT RELEASE REPORT January 1, 2015 through December 31, 2015 EXELON GENERATION COMPANY, llC OYSTER CREEK GENERATING STATION DOCKET NO. 50-219 (Oyster Creek Generating Station) DOCKET NO. 72-15 (Independent Spent Fuel Storage Facility)

Submitted to The United States Nuclear Regulatory Commission Pursuant to Renewed Facility Operating License DPR-16 Oyster Creek 2015 Annual Radioactive Effluent Release Report TABLE OF CONTENTS SECTION EXECUTIVE

SUMMARY

1. Sources of Rad i at i on Dose to the U.S. Populat i on 2. Exposure Pathways 3. Introduction

4. Supplemental Information A Regulatory Lim i ts B Effluent Concentration L i mits C Average Energy D Measurements and Approximations of Total Radioactivity E Batch Releases F Abnormal Releases G Revisions to the ODCM H Radiation Effluent Monitors Out of Service More Than 30 Days Releases from the Independent Spent Fuel Storage Facility J Program Dev i ations Appendix A -Effluent and Waste D i sposal Summary Appendix B -Solid Waste and Irradiated Fuel Sh i pments Appendix C -Radiological Impact to Man Appendix D -Meteorolog i ca l Data Appendix E -ODCM Rev i sions Appendix F -ERRATA ii PAGE 3 5 7 8 8 9 9 9 13 13 13 13 14 14 15 22 29 32 106 107 Oyster Creek 2015 Annual Radioactive Effluent Release Report (Page Intentionally Left B l ank) iii Oyster Creek 2015 Annual Radioactive Effluent Release Report EXECUTIVE

SUMMARY

Effluents are strictly monitored to ensure that radioactivity released to the env i ronment is as low as reasonably achievable and does not exceed regulatory limits. Effluent control includes the operation of monitoring systems , in-plant and environmental sampling and analyses programs , quality assurance programs for the effluent and environmental programs , and procedures covering all aspects of effluent and environmental mon i toring. Both radiological environmental and effluent monitoring indicate that the operation of Oyster Creek Generating Station (OCGS) does not result in significant rad i ation exposure to the people or the environment surrounding OCGS and is well below the applicable levels set by the Nuclear Regulatory Commission (NRC) and the Environmental Protection Agency (EPA). There were liquid radioactive effluent releases during 2015 of concentrations of trit i um too low to detect at an LLD of 200 picocuries per liter (pCi/L) at the New Jersey Pollution Discharge Elimination System (NJPDES) permitted main condenser outfall. The releases were part of nearly continuous pumping of groundwater at approximately 70 gpm containing low levels of tritium and no detectable gamma. Exelon and the State of New Jersey Department of Environmental Protection (NJDEP) agreed to this remediation action instead of natural attenuat i on to address concentrations of tritium in groundwater. Well 73 and supporting equipment and piping were installed to pump groundwater to the intake structure at the inlet of the main circulating water pumps. Provis i ons were established for both batch and continuous releases of groundwater. Continuous releases occurred approximately 277 days in 2015. The nearly continuous releases occurred from January 1 , 2015 through January 30 , 2015 and April 27 , 2015 through December 31 , 2015 with a total of 2. 78E+07 gallons of groundwater pumped resulting in 2.08E-01 Ci of tritium released to the discharge canal. The dose to the most limiting member of the public due to the release of groundwater was 9.86E-07 mrem. There were no liquid abnormal releases during 2015. There were no gaseous abnormal releases during 2015. The maximum calculated organ dose (Bone) from iodines , tritium , carbon-14 (C-14), and particulates to any individual due to gaseous effluents was 5.53E-01 mrem , which was approximately 3.69E+OO percent of the annual limit of 15 mrem. The majority of organ dose from gaseous effluents was due to C-14. The maximum calculated gamma air dose in the UNRESTRICTED AREA due to noble gas effluents was 4.86E-03 mrad , which was 4.86E-02 percent of the annual 10 CFR 50 Appendix I , As Low As Reasonably Achievable (ALARA) limit of 10 mrad. For comparison , the background radiation dose averages approximately 620 mrem per year to the average person in the United States. The Independent Spent Fuel Storage Installation (ISFSI) is a closed system and the only exposure is due to direct radiation. Based on offsite TLD readings , dose due to direct radiation from the ISFSI was less than 1 mrem for 2015. Because it is a sealed unit , no radioactive material was released. 1 Oyster Creek 2015 Annual Radioactive Effluent Release Report Comparison of environmental sampling results to iodine and particulate gaseous effluents released , showed no radioactivity attributable to the operation of OCGS. Both elevated and ground-level release paths were considered in this review , with total iodines released of 4.30E-03 Ci and total particulates with half-lives greater than 8 days less C-14 released of 2.69E-02 C i. Joint Frequency Tables of meteorological data , per Stability Classification Category , as well as for all stability classes , are included. All data was collected from the on-site Meteorological Facility. Data recoveries for the 380-foot data and the 33-foot data were 99.8 percent and 99.8 percent , respectively. The UFSAR commits to Regulatory Guide (RG) 1.23 for Meteorological Facility data recovery. RG 1.23 requires data recovery of at least 90% on an annual basis. 2 Oyster Creek 2015 Annual Radioactive Effluent Release Report 1 Sources of Radiation Dose to the U.S. Population Note: The information in th i s section is from the following NRC report: Radioactive Effluents from Nuclear Power Plants: Annual Report 2007 For comparison with Nuclear Power Plant (NPP) effluents , this section provides a perspective on the doses that Americans typically receive on average from natural and background rad i ation. In March 2009 , the National Council on Radiation Protection and Measurements (NCRP) published Report No. 160 as an update to the 1987 NCRP Report No. 93 , Ionizing Radiation Exposure of the Population of the United States (Refs. 28 , 29). Report No. 160 describes the doses to the U.S. population from all sources of ionizing radiation for 2006 , the most recent data available at the time the report was written. The report also includes information on the variability of those doses from one individual to another. The NCRP estimated that the average pe r son i n the United States receives the equivalent of about 620 mrem of radiation dose each year. NCRP Report No. 160 describes each of the sources of radiation that contr i bute to this dose , including: 1. naturally-occurring sources (natural background) such as cosmic rad i ation from space , terrestrial radiat i on from rad i oactive materials i n the earth , and naturally occurring radioactive materials in food people eat and air people breathe; 2. medical sources from diagnosis and treatment of health disorders using radioactive pharmaceuticals and radiation-producing equipment; 3. consumer products; 4. industrial processes , secur i ty devices , educational tools , and research activities

5. exposures of workers that result from their occupations. Figure 1.1 is a pie chart showing the relative contribut i ons of these sources to radiat i on dose to the U.S. popu l at i on. La r ge r r elat iv e cont ri butors to dose are represented by proportionally larger sl i ces of the pie. Doses to the publ i c from nuclear power generation are included in the industrial category; doses to workers from nuclear power generation are included in the category of occupational dose. Doses to the public due to effluents from NPPs are less than 0.1 % of what the average person rece i ves each year from all sources of radiation.

Doses to workers from occupational exposures , including those rece i ved from work at NPPs , also are less than 0.1 % of the average dose to a member of the public from all sources. 3 Oyste r Creek 2015 Annua l Radioact i ve Effluent Release Report FIGURE 1.1 Sou r ces of Rad i ation Exposure to the U.S. Population Indu s trial Ra don & th o ron (b a ck gr oun d) 37% inclu des doses to the public from nuclear power generation

<0.1% O ccup a ti o nal i ncludes doses to w orkers from nuclear power generation

<0.1% Con sume r 2% Conven ti ona l r ad iogr a phy I fluoroscopy (m ed ic a l) 5% Sp a ce (back g roun d) 5% l nte rv e n t i o n a l flouroscopy (med i caQ 7% In te rn al (bacf(ground) 5% T e rr e stri a l (b ackg round) 3% N ucl e ar m e dicine (m edical) 12% C ompu te d tomogr a phy (medical) 24% Percent contribut i on of various so u rces of exposure to the total collect i ve effective dose and the total effective dose per i ndividual in the U.S. population for 2006. Percent values have been rounded to the nearest 1 %, except fo r those <1 % [less than 1 %]. Credit: Mod i ficat i on to i mage courtesy of National Counc i l on Radia ti on Protection and Measurements. 4 Oyster Creek 2015 Annual Radioactive Effluent Release Report 2 Exposure Pathways Radiological exposure pathways define the methods by which people may become exposed to radioactive material.

The major pathways of concern are those which could cause the highest calculated radiation dose. These projected pathways are determined from the type and amount of radioactive material released , the environmental transport mechanism, and the use of the environment.

The e nvi ro n me n tal tra n sport mechan i sm includes consideration of physical factors , such as the hydrological (water) and meteorological (weather) characteristics of the area. An annual average of the water flow , wind speed , and wind direction are used to evaluate how the radionuclides will be distributed in an area for gaseous or liquid releases. An important factor in evaluating the exposure pathways is the use of the environment.

Many factors are considered such as dietary intake of residents, recreational use of the area , and the locations of homes and farms in the area. The external and internal exposure pathways considered are shown in Figure 2.1. The release of radioactive gaseous effluents involves pathways such as external whole body exposure , deposition of radioactive material on plants , deposition on soil , inhalation by animals destined for human consumption , and inhalation by humans. The release of radioactive material in liquid effluents involves pathways such as drinking water, fish , and direct exposure from the water at the shoreline while swimming. Although radionuclides can reach humans by many different pathways, some result in more dose than others. The critical pathway is the exposure route that will provide , for a specific radionuclide , the greatest dose to a population , or to a specific group of the population called the critical group. The critical group may vary depending on the radionuclides involved , the age and diet of the group, or other cultural factors. The dose may be delivered to the whole body or to a specific organ. The organ receiving the greatest fraction of the dose is called the critical organ. 5 Oyster Creek 2015 Annual Radioactive Effluent Release Report FIGURE 2.1 Exposure Pathways ,,,.. I nhalation.

tnlnspiralion and submersion D ri n king Surfac e W a t e r or G r oun-This simple diagram demonstrates some potential exposure pathways from Oyster Creek Generating Station. 6 Oyster Creek 2015 Annual Radioactive Effluent Release Report 3 Introduction In accordance with the reporting requirements of Technical Specification 6.9.1.d applicable during the reporting period, this report summarizes the effluent release data for OCGS for the period January 1, 2015 through December 31, 2015. This submittal complies with the format described in Regulatory Guide 1.21, "Measurin.Q, Evaluatin.Q and Reporting Radioactivity in Solid Wastes and Releases of Radioadiw Mafetiafs fn tfqufd and Gaseous Effluents from Water-Cooled Nuclear Power Plants", Revision 1, June 1974. Meteorological data was reported in the format specified in Regulatory Guide 1.23, Revision 1, "Meteorological Monitoring Programs for Nuclear Power Plants". All vendor results were received and included in the report calculations.

Therefore the 2015 report is complete.

7 Oyster Creek 2015 Annual Radioactive Effluent Release Report 4 Supplemental Information Oyster Creek Generating Station Exelon Generation Company, LLC A. Regulatory Limits: LimJt UnJts 1. Noble Gases: a. .::5.500 mrem/yr Total Body .::5.3000 mrem/yr Skin b. ,::5.5 mrad AirGamma .::: 10 mrad Air Beta c. .::: 10 mrad AirGamma ,::5.20 mrad Air Beta d. <5 mrem Total Body (Gamma) < 15 mrem Skin (Beta) 2. Iodines, Tritium, Particulates with Half Life > 8 days: ODCM and lO CFR 50, Appendix I Design Objective Limits ODCM Control 3.11.2.1 Quarterly air dose limits ODCM Control 3.11.2.2 Yearly air dose limits ODCM Control 3.11.2.2 10 CFR 50, Appendix I, Section ll.B.2(b)

a. .::, 1500 mrem/yr Any Organ ODCM Control 3.11.2.1 b. .::. 7.5 mrem Any Organ Quarterly dose limits ODCM Control 3.11.2.3 c. .::. 15 mrem Any Organ

Yearly dose limits ODCM Control 3.11.2.3 3. Liquid Effluents:

a. Concentration 1 O CFR 20, Appendix B, ODCM Control 3.11.1.1 Table 2 Column 2 b. .::. 1.5 mrem Total Body Quarterly dose limits .::5.5 mrem Any Organ ODCM Control 3.11.1.2

c. .::. 3 mrem Total Body Yearly dose limits .::. 10 mrem Any Organ ODCM Control 3.11.1.2 8

Oyster Creek 2015 Annual Radioactive Effluent Release Report B. Effluent Concentration Limits: Gaseous dose rates rather than effluent concentrations are used to calculate permissible release rates for gaseous releases.

The maximum permissible dose rates for gaseous releases are defined in ODCM Controls 3.11.2.1.

The Effluent Concentration limit {ECL) specified in 10 CFR 20, Appendix B, Table 2, Column 2 for identified nuclides, were used to calculate permissible release rates and concentrations for liquid release per ODCM Controls 3.11.1.1.

The total activity concentration at the Route 9 bridge for all dissolved or entrained gases was limited to < 2E-04 µCi/ml. C. Average Energy ( 'E ) : Ihe Oyster Creek ODCM limits the instantaneous dose equivalent rates due to the release of noble gases to less than or equal to 500 mrem/year to the total body and less than or equal to 3000 mrem/year to the skin. The average beta and gamma energies ( 'E ) of the radionuclide mixture in releases of fission and activation gases as described in Regulatory Guide 1.21, "Measuring, Evaluating and Reporting Radioactivity in Solid Wastes and Releases of Radioactive Materials in Liquid and Gaseous Effluents from Light-Water-Cooled Nuclear Power Plant", may be used to calculate doses in lieu of more sophisticated software.

The Oyster Creek radioactive effluent program employs the methodologies presented in U.S. NRC Regulatory Guide 1.109 "Calculation of Annual Doses to Man from Routine Releases of Reactor Effluents for the Purpose of Evaluating Compliance with 10 CFR Part 50, Appendix I," Revision 1, October 1977. Therefore, average energy ( 'E) as described in Regulatory Guide 1.21 is not applicable to Oyster Creek. D. Measurements and Approximations of Total Radioactivity:

1. Fission and Activation Gases The method used for Gamma Isotopic Analysis is the Canberra Gamma Spectroscopy System with a gas Marinelli beaker. Airborne effluent gaseous activity was continuously monitored and recorded in accordance with the Off Site Dose Calculation Manual (ODCM) Table 4.11.2.1.2-1.

Additional grab samples were taken from the stack Radioactive and Gaseous Effluent Monitoring System (RAGEMS) sample point and ground-level release sample points and analyzed at least monthly to determine the isotopic mixture of noble gas activity released for the month. If activity was found in the grab isotopic analysis, the results are entered into Simplified Environmental Effluent Dosimetry System (SEEDS) to calculate dose and dose rates. If no activity is detected in the stack grab samples, post treatment or Off Gas Isotopic Analysis data may be used. 2. Iodines The method used for Gamma Isotopic Analysis is the Canberra Gamma Spectroscopy System with a charcoal cartridge.

Iodine activity was continuously sampled and analyzed in with ODCM Table 4.11.2.1.2-1.

Charcoal samples are taken from the stack RAGEMS sample point and 9 Oyster Creek 2015 Annual Radioactive Effluent Release Report ground-level release sample points and analyzed at least weekly to determine the total activity released from the plant based on the average vent flow rates recorded for the sampling period. 3. Particulates (half-lives

> 8 days) The method used for Gamma Isotopic Analysis is the Canberra Gamma Spectroscopy System with a particulate filter (47 mm). Particulate activity was continuously sampled and analyzed in accordance with ODCM Table 4.11.2.1.2-1.

Particulate samples are taken from the stack RAGEMS sample point and ground-level release sample points and analyzed at least weekly to determine the total activity released from the plant based on the average vent flow rates recorded for the sampling period.

4. Tritium A. Gaseous Effluents Air from stack and vent effluents was passed through a desiccant column and distilled to the moisture collected.

An aliquot of the water from the distillate was analyzed for tritium using a liquid scintillation counter. B. Liquid Effluents Water from liquid effluents was analyzed for tritium using a liquid scintillation counter. 5. Gross Alpha Gross alpha was measured by an off-site vendor for both the gas and liquid effluent composite samples. 6. Hard-To-Detects

/ Hard-To-Detects was measured by an off-site vendor for one set of gas monthly composites.

The analysis included Fe-55, 1-129, Ni-59, Ni-63, Tc-99, Am-241, Cm-242, Cm-243/244, Pu-238, Pu-239/240 and Pu-241. Fe-55 and Ni-63 have been added to the routine monthly composite analysis schedule based on previous sample results for Detects. Only nuclides that have been detected are included in Table A-2 and/or Table A-3. 10 Oyster Creek 2015 Annual Radioactive Effluent Release Report 7. Carbon-14 (C-14) The amount of C-14 (Ci) released was estimated using the guidance from EPRI Technical Report 1021106, Estimation of Carbon-14 in Nuclear Power Plant Gaseous Effluents.

The C-14 was released primarily through the stack (97%) with a small amount (3%) released through plant vents. The activity in liquid effluents was determined to not be significant.

The offsite dose from C-14 was calculated using SEEDS, which uses approved ODCM methodologies.

The resulting annual dose to a child from gaseous releases of C-14 is about 5.27E-01 mrem to the bone. 8. Liquid Effluents Groundwater containing tritium was released during 2015. For continuous releases, tritium and principal gamma emitters were determined fbr a composite sample daily. The concentration of tritium is limited to ensure concentrations were less than 200 pCi/I in the discharge canal. The gamma emitters were limited to less than detectable concentrations.

Gross alpha and Hard-to-detect analyses (Fe-55, Ni-63, Sr-89 and Sr-90) were determined for monthly composite samples for each type of release (batch or continuous).

The leaks into the groundwater were reported in the 2009 Annual Radioactive Effluent Release Report as abnormal releases.

Estimates of the curies of the tritium releases were reported.

Doses due to the release of the groundwater to the discharge canal were included in the report. To ensure that the amount of activity discharge is accurate and limiting, the activity and doses as a result of discharges during 2015 from the groundwater remediation project are included in this report. 9. Estimated Total Error Present Procedure CY-AA-170-2100, Estimated Errors of Effluent Measurements, provides the methodology to obtain an overall estimate of the error associated with radioactive effluents.

11 Oyster Creek 2015 Annual Radioactive Effluent Release Report 10. Composite Samples and Lower Limit of Detection (LLD) Particulate air samples were composited monthly and analyzed for gross alpha, Sr-89, Sr-90, Fe-55 and Ni-63. Groundwater batch and continuous releases were composited at least monthly and analyzed for gross alpha, Sr-89, Sr-90, Fe-55 and Ni-63. These composites are submitted to an offsite vendor laboratory for analysis.

The ODCM required LLD for liquid and airborne releases are as follows: Liquid: Principal Gamma Emitters (Mn-54, Fe-59, Co-58, Co-60, Zn-65, Mo-99, 1-131, Ce-141, Cs-134, Cs-137) Principal Gamma Emitters (Ce-144) Dissolved and Entrained Gases H-3 Gross Alpha Sr-89 and Sr-90 Fe-55 and Ni-63 Airborne Principal Gamma Emitters (Kr-87, Kr-88, Xe-133, Xe-133m, Xe-135, Xe-138) H-3 1-131 1-133 Principal Gamma Emitters (Mn-54, Fe-59, Co-58, Co-60, Zn-65, Cs-134, Cs-137, Ce-141) Principal Gamma Emitters (Mo-99, Ce-144) Gross Alpha Sr-89, Sr-90 12 LLD 5E-07 µCi/ml 5E-06 µCi/ml 1 E-05 µCi/ml 1 E-05 µCi/ml 1 E-07 µCi/ml 5E-08 µCi/ml 1 E-06 µCi/ml LLD 1 E-04 µCi/ml 1 E-06 µCi/ml 1 E-12 µCi/ml 1E-10 µCi/ml 1 E-11 µCi/ml 1E-10 µCi/ml 1 E-11 µCi/ml 1 E-11 µCi/ml

( Oyster Creek 2015 Annual Radioactive Effluent Release Report E. Batch Releases:

1. Liquid There were no batch releases of liquid effluents during 2015. There were no batch releases of gaseous effluents during 2015. F. Abnormal Releases:

There were no abnormal liquid releases during 2015. There were no abnormal gaseous releases during 2015. G. Revisions to the ODCM: Revision 7 of the ODCM, CY-OC-170-301 was implemented 10/22/2015.

A list of the major changes is included below. See the complete copy of CY-OC-170-301 Revision 7 attached as part of this report.

Changed description of REMP Sample Station 9 from SW to WSW -Note, sample location was correct on Figure E-2.

Changed description of REMP Sample Stations 106 and 107 from NW to WNW -Note, sample location was correct on Figure E-2.

Changed REMP Sample Station 3 from an airborne background location to an airborne special interest location which was listed in error as a background location in the last revision.

Added REMP Sample Station 114 back into the REMP since it was accidently left off the list as a drinking water sample location in the last revision -Note, sample location 114 was still listed on Figure E-1 in the last revision.

Removed REMP Sample Station 39 from the REMP in the list as a background drinking water sample location and from Figure E-2. H. Radiation Effluent Monitors Out of Service More Than 30 Days Per ODCM Control 3.3.3.10, "Radioactive Liquid Effluent Monitoring Instrumentation" and 3.3.3.11, Radioactive Gaseous Effluent Monitoring Instrumentation requires:

With less than the minimum number of radioactive liquid/gaseous effluent monitoring instrumentation channels OPERABLE, take the ACTION shown in Table 3.3.3.10-1/3.3.3.11-1.

Make every reasonable effort to return the instrument to OPERABLE status within 30 days and, if unsuccessful, explain in the next 13 Oyster Creek 2015 Annual Radioactive Effluent Release Report Radioactive Effluent Release Report why .the inoperability was not corrected in a timely manner. The following is a discussion of instrumentation out of service for greater than 30 days: 1. There was no instrumentation out of service for greater than 30 days. I. Releases from the Independent Spent Fuel Storage The ISFSI is a closed system and the only exposure would be due to direct radiation.

This includes iodines, particulates, and noble gases. Based on offsite TLD readings, dose due to direct radiation from the ISFSI was less than 1 mrem for 2015. Because it is a sealed unit, no radioactive material was released.

J. Program Deviations:

1. There were no program deviations in 2015. 14 Oyster Creek 2015 Annual Radioactive Effluent Release Report Appendix A Effluent and Waste Disposal Summary 15 Oyster Creek 2015 Annual Radioactive Effluent Release Report LIST OF TABLES Table A-1 Gaseous Effluents-Summary of All Releases Table A -2 Gaseous Effluents Release Point: Elevated Release Table A-3 Gaseous Effluents Release Point: Ground Level Releases Table A-4 Liquid Effluents

-Summary of All Releases Table A -5 Liquid Release Point: Groundwater Remediation 16 PAGE 17 18 19 20 21 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table A-1: Gaseous Effluents

-Summary Of All Releases Period: January 1, 2015 through December 31, 2015 Unit: Oyster Creek Est. Total A. Fission & Activation Gases Units Quarter 1 Quarter 2 Quarter 3 Quarter 4 Error% 1. Total Release Ci 1.44E+01 1.53E+01 6.52E+OO 5.08E+OO 25.00% 2. A1.erage Release Rate for Period µCi/sec 1.85E+OO 1.94E+OO 8.21E-01 6.39E-01 3. Gamma Air Dose mrad 2.58E-04 4.57E-03 1.52E-04 1.14E-04 4. Beta Air Dose mrad 1.20E-04 4.26E-03 5.09E-05 1.95E-05 5. Percent of ODCM Limit -Gamma Air Dose % 5.16E-03 9.14E-02 3.04E-03 2.28E-03 -Beta Air Dose % 1.20E-03 4.26E-02 5.09E-04 1.95E-04 8. Iodines 1. Total 131 C i 1.99E-04 3.92E-04 3.33E-04 2.30E-04 25.00% 2. A1.erage Release Rate for Period µCi/sec 2.56E-05 4.98E-05 4.19E-05 2.90E-05 3. Percent of ODCM limit % * * *

c. Particulate

1. Particulates w i th T 1/2 > 8 days Ci 1.43E-02 5.63E-03 3.85E-03 3.12E-03 25.00% 2. A1.erage Release Rate for Period µCi/sec 1.83E-03 7.16E-04 4.85E-04 3.93E-04 3. Percent of ODCM l i mit % * * *

o. Tritium 1. Total Release Ci 7.07E+OO 1.13E+01 6.96E+OO 5.45E+OO 25.00% 2. A1.erage Re l ease Rate for Per i od µCi/sec 9.09E-01 1.44E+OO 8. 76E-01 6.86E-01 3. Percent of ODCM limit % * * *

E. Gross Alpha 1. Total Release Ci <LLD <LLD <LLD <LLD 25.00% 2. A1.erage Release Rate for Period µCi/sec <LLD <LLD <LLD <LLD

3. Percent of ODCM limit % * * *

F. Carbon-14

1. Total Release Ci 2.25E+OO 2.21E+OO 2.44E+OO 2.42E+OO 2. A1.erage Release Rate for Period µCi/sec 2.89E-01 2.81 E-01 3.0?E-01 3.05E-01 3. Percent of ODCM l i mit % * * *

G. Iodine 131 & 133, Tritium & Particulate

1. Organ Dose mrem 5.85E-02 8.63E-02 2.33E-01 1.80E-01 2. Percent of ODCM Limit % f.801::-01 1.151::+uu 3.111::+uu 2.4ut:+uu

ODCM Limit is for combined Iodine , tr i t i um , Carbon-14 and particulate only , which is shown i n Item G. 17 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table A-2: Gaseous Effluents Release Point: Elevated Release Period: January 1, 2015 through December 31, 2015 Unit: Oyster Creek Nuclides Released Continuous Mode Batch Mode 1. Fission gases_ Unit Quarter Quarter Quarter Quarter Quarter Quarter Quarter Quarter 1 2 J 4-1 2 3 4 Kr-85 Ci <LLD <LLD <LLD <LLD

<LLD <LLD <LLD <LLD Kr-85m Ci 2.10E-01 4.14 E-01 9.07E-01 1.19E+OO <LLD <LLD <LLD

<LLD K r-87 Ci <LLD <LLD <LLD <LLD

<LLD <LLD <LLD <LLD Kr-88 C i 1.38E-01 3.17E-01 7.07E-01 1.02E+OO <LLD <LLD <LLD <LLD Xe-133 Ci 3.12E-01 4.50E-01 1.03E+OO 1.25E+OO <LLD <LLD <LLD

<LLD Xe-135 Ci 1.37E+01 1.31E+01 3.88E+OO 1.62E+OO <LLD <LLD <LLD <LLD Xe-135m Ci <LLD <LLD <LLD

<LLD <LLD <LLD <LLD <LLD Xe-137 Ci <LLD <LLD

<LLD <LLD <LLD <LLD <LLD <LLD Xe-138 C i <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Ar-41 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LL D <L LD Total for Period Ci 1.44E+01 1.43E+01 6.52E+OO 5.08E+OO <LLD <LLD <LLD <LLD 2. Iodines 1-131 C i 1.99E-04 3.91E-04 3.32E-04 2.30E-04 <LLD <LLD <LLD <LLD 1-133 C i 3.38E-04 1.10E-03 9.86E-04 7.17E-04 <LLD <LL D <LLD <LLD 1-135 Ci <LLD <LLD <LLD <LLD <LLD <LLD

<LLD <LLD Total for Period Ci 5.37E-04 1.49E-03 1.32E-03 9.47E-04 <LLD <LLD <LLD <LL D 3. Particulates St-89 Ci 1.00E-03 3.18E-04 1.09E-04 1.42E-04 <LLD <LLD <LLD <LLD Sr-90 C i <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Cs-134 C i <LLD <LLD <LLD

<LLD <LLD <LLD <LLD <LLD Cs-137 Ci 6.64E-04 <LLD <LLD <LLD

<LLD <LLD <LLD

<LLD Ba-140 Ci 1.27E-03 5.25E-04 1.03E-04 1.37E-04 <LLD <LLD <LLD

<LLD La-140 Ci <LLD <LLD <LLD

<LLD <LLD <LLD <LLD <LLD Cr-51 Ci 3.29E-04 1.01 E-04 <LLD <LLD <LLD <LLD <LLD <LL D Mn-54 Ci 5.68E-04 4.83E-04 2.63E-04 2.05E-04 <LLD <LLD <LLD <LLD Co-58 Ci 4.93E-03 1.63E-03 1.31 E-03 9.71E-04 <LLD <LLD <LLD <LLD Co-60 Ci 4.26E-03 1.93E-03 1.71 E-03 1.41 E-03 <LLD <LLD <LLD <LLD Ni-63 Ci <LLD <LLD <LLD

<LLD <LLD <LLD <LLD <LLD Mo-99 Ci 1.92E-04 1.00E-04 5.01E-05 7.05E-06 <LLD <LLD <LLD <LLD Ag-110m C i <LLD <LLD <LLD <LLD

<LLD <LLD <LLD <LLD Ce-141 Ci <LLD <LLD <LLD

<LLD <LLD <LLD <LL D <LLD Ce-144 Ci <LLD <LLD <LLD <LLD

<LLD <LLD <LLD <LLD Fe-55 Ci <LLD <LLD <LLD <LLD

<LLD <LLD <LLD <LLD Fe-59 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Zn-65 Ci 1.04E-03 5.10E-04 2.59E-04 2.40E-04 <LLD <LL D <LLD <LLD Am-241 Ci <LLD <LLD <LLD <LLD

<LLD <LLD <LLD <LLD Total for Period Ci 1.43E-02 5.60E-03 3.80E-03 3.11E-03 <LLD <LLD <LLD <LLD

4. Tritium H-3 Ci 6.45E+OO 1.07E+01 6.48E+OO 4.96E+OO <LLD <LL D <LLD <LLD

5. Gross Alpha Gross Alpha C i <LLD <LLD <LLD <LLD

<LLD <LLD <LLD <LLD 6. Carbon-14 C-14 C i 2.18E+OO 2.14E+OO 2.37E+OO 2.35E+OO <LLD <LLD <LLD <L LD 18 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table A-3: Gaseous Effluent Release Point: Ground Level Releases Period: January 1 , 2015 through December 31 , 2015 Unit: Oyster Creek Nuclides Released Continuous Mode Batch Mode 1. Fission gases Unit Quarter Quarter Quarter Quarter Quarter Quarter Quarter Quarter 1 2 3 4 1 2 3 4 Kr-85 C i <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Kr-85m Ci <LLD 2.75 E-02 <LLD <LLD <LLD <LLD <LLD

<LLD Kr-87 Ci <LLD 3.68E-01 <LLD <LLD <LLD <LLD <LLD

<LLD Kr-88 Ci <LLD 6.56E-02 <LLD <LLD <LL D <LLD <LLD

<LLD Xe-133 Ci <L LD <LLD <LLD <LLD <LLD <LLD <LL D <LLD Xe-133 m C i <LLD <L LD <LLD <LLD <LLD <LLD <LL D <LLD Xe-135 C i <LLD 5.40E-01 <LLD <LLD <LL D <LLD <LLD <LLD Xe-135m C i <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Xe-138 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Ar-41 C i <LLD <LLD <LLD

<LLD <LLD <LLD <LLD <LLD Total for Period Ci <LLD 1.00E+OO <LLD <LLD <LL D <LLD <LLD

<LLD 2. I odines 1-131 Ci <LLD 7.17E-07 1.17E-06 3.39E-07 <LLD <LLD <LLD

<LLD 1-133 Ci <LLD 1.69E-06 1.52E-06 1.69E-08 <LLD <LLD <LLD <LLD 1-135 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD

<LLD Total for Per i od C i <LLD 2.41 E-06 2.69E-06 3.56E-07 <L LD <LLD <LLD <LLD

3. Particulates Sr-89 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD S r-90 C i <LLD <LLD <LLD <LLD

<LLD <LLD <LLD <LLD Cs-134 Ci <LLD <LLD <LLD <LLD

<LLD <LLD <LLD

<LLD Cs-137 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Ba-140 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD La-140 C i <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Cr-51 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Mn-54 Ci <LLD 1.09 E-0 6 <LLD <LLD <LLD <LLD <LLD <LLD Co-58 C i 6.18E-07 1.07E-05 1.91 E-05 3.00E-06 <LLD <LLD <LLD <LLD Co-60 C i 4.91E-06 2.29E-05 3.14E-05 5.31E-06 <LL D <LLD <LLD <LLD Ni-63 C i <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LL D Mo-99 C i <LLD <LLD <LLD <LLD <LLD <LLD <LLD

<LL D Ag-110m C i <LLD <LLD

<LLD <LLD <LLD <LLD <LLD <LLD Ce-141 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Ce-144 C i <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Fe-55 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD

<LLD Fe-59 Ci <LLD <LLD <LLD <L LD <LLD <LLD <LLD

<LLD Zn-65 Ci <LLD <L LD <LLD <L LD <L LD <LLD <LLD

<LL D Am-241 C i <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Total for Pe riod Ci 5.53E-06 3.47 E-05 5.05E-05 8.31E-06 <LLD <LLD <LLD <LLD

4. Tritium H-3 C i 6.20E-01 5.95E-01 4.82E-01 4.93E-01 <LLD <LLD <LLD <LLD 5. Gross Alpha Gross Alpha C i <LLD <LLD <LLD <LLD <LLD <LLD <LLD

<LLD 6. Carbon-14 C-14 Ci 6.76E-02 6.63E-02 7.32E-02 7.28E-02 <LLD <LLD

<LLD <LLD 19 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table A-4: Liquid Effluents

-Summary Of All Releases Period: January 1, 2015 through December 31 , 2015 Unit: Oyster Creek Est. Total A. Fission & Activation Products Units Quarter 1 Quarter 2 Quarter 3 Quarter 4 Error% . 1. Total Release not includin9 Q i <llD <UD <UD <LLD 25.00% ' frffi'um , gases , a l pha ' 2. Average Diluted concentration

µCi/ml <LLD during period <LLD <LLD

<LLD 3. Total Body Dose mrem 9.54E-08 2.35E-07 3.28E-07 3.28E-07 4. Organ Dose mrem 9.54E-08 2.35E-07 3.28E-07 3.28E-07 3. Percent of ODCM Limit -Total Body Dose % 6.36E-06 1.57E-05 2.19E-05 2.18E-05 -Organ Dose % 1.91 E-06 4.?0E-06 6.56E-06 6.55E-06 B. Tritium C::Sl. I Uli:ll Units Quarter 1 Quarter 2 Quarter 3 Quarter 4 Error% 1. Total Release Ci 2.04E-02 4.91E-02 7.01E-02 6.89E-02 25.00% 2. Average diluted concentration

µCi/ml 1.41E-10 1.44E-10 1.43E-10 1.42E-10 durina oeriod 3. Percent of 10CFR20 limit % 1.41 E-05 1.44E-05 1.43E-05 1.42E-05 c. Dissolved and Entrained Gases t:st. 1 otal Units Quarter 1 Quarter 2 Quarter 3 Quarter 4 Error% 1. Total Release Ci <LLD <LLD <LLD <LLD 25.00% 2. Average diluted concentration

µCi/ml <LLD <LLD <LLD <LLD 3. Percent of ODCM limit % <LLD <LLD <LLD

<LLD D. Gross Alpha Activity t:st. 1 otal Units Quarter 1 Quarter 2 Quarter 3 Quarter 4 Error% 1. Total Release Ci <LLD <LLD <LLD <LLD 25.00% E. Volume of Waste Released prior to dilution Liters 1.03E+07 2.48E+07 3.54E+07 3.48E+07 F. Volume of Dilution Water Used During Period Liters 1.44E+11 3.42E+11 4.91E+11 4.84E+11 20 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table A-5: Liquid Release Point: Groundwater Remediation Period: January 1 , 2015 through December 31, 2015 Unit: Oyster Creek Nuclides Released Continuous Mode Batch Mode Fission & Unit Activation Quarter Quarter Quarter Quarter Quarter Quarter *Quarter *Quarter Products 1 2 3 4 1 2 3 4 Sr-89 Ci <LLD <LL D <LLD <LLD <LLD <LLD <LLD <L LD Sr-90 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Cs-134 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Cs-137 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD 1-131 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Co-58 Ci <LLD <LLD <LLD <LLD <LLD

<LLD <LLD <LLD Co-60 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Ni-63 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Fe-59 Ci <LLD <LLD <LLD <LLD <LLD

<LLD <LLD <LLD Zn-65 Ci <LLD <LLD <L LD <LLD <LLD <LLD <LLD <LLD Mn-54 Ci <LLD <LL D <L LD <LLD <LLD <LLD <L LD <LLD Cr-5 1 Ci <LLD <LL D <LLD <LLD <LL D <LLD <LLD <LLD Zr-95 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Nb-95 C i <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Mo-99 C i <LLD <LLD <LLD <LLD

<LLD <LLD <LLD <LLD Tc-99m C i <LLD <LLD <LLD <LLD <LLD <LLD <LLD <L LD Ba-140 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD La-140 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Ce-141 Ci <LLD <L LD <LLD <LLD <LLD <L LD <LLD <LLD Ag-110m Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Fe-55 Ci <L LD <LL D <LLD <LLD <LLD <LLD <L LD <LLD Ce-144 Ci <LLD <L LD <L LD <LL D <LLD <LLD <LLD <LLD Total for Period <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Dissolved Entrained Gases Xe-133 Ci <LLD <L LD <LLD <LLD <LLD <LLD <LLD <LLD Xe-135 Ci <LLD <LLD <LLD <LLD <LLD <LLD <LLD <LLD Tritium H-3 Ci 2.04E-02 4.9 1 E-02 7.0 1 E-02 6.89E-02 <LLD <LLD <LLD <L LD Gross Alpha Gross Alpha C i <LLD <LLD <LLD <LLD <L LD <LLD <LLD <L LD 21 Oyster Creek 2015 Annual Radioactive Effluent Release Report A. Solid waste shipped offsite for burial or disposal (not irradiated fuel) 1. Type of waste Types of Waste Total Total Period Est. Total Quantity Activity Error°/o (m3) (Ci) a. Spent resins.filter sludQes , evaoorator bottom , etc 5.13E+01 2.12E+02 2015 2.50E+01 b. Dry compressible waste , contam i nated equip , etc 2.36E+02 1.68E-01 2015 2.50E+01 c. Irradiated components, control rods.etc O.OOE+OO O.OOE+OO 2015 2.50E+01 d. Other 1.53E+02 1.04E-01 2015 2.50E+01 23 Oyster Creek 2015 Annual Radioactive Effluent Release Report 1. Estimate of Major Nuclide Composition (By Waste Type) Category A -Spent Res i n , F i lters , S l udges , Evaporato r Bottoms , etc. Isotope Waste Class A Waste Class B Waste Class C Curies Percent Curies Percent Curies Percent H-3 1.96E-02 1.71E-02 9.20E-04 9.47E-04 C-14 2.06E-02 1.80E-02 2.94E-04 3.03E-04 Cr-51 P-32 5.31 E-08 4.63E-08 Mn-54 2.97E+OO 2.59E+OO 1.58E+OO 1.63E+OO Fe-55 7.61 E+01 6.63E+01 5.76E+01 5.93E+01 Fe-59 Co-57 Co-58 1.22E-01 1.06E-01 Co-60 3.12E+01 2.72E+01 2.73E+01 2.81E+01 Ni-59 1.21E-04 1.05E-04 9.22E-03 9.49E-03 Ni-63 1.01E+OO 8.80E-01 9.85E-01 1.01E+OO Zn-65 9.43E-01 8.22E-01 6.58E-01 6.77E-01 Sr-89 8.62E-04 7.51E-04 Sr-90 6.51 E-03 5.67E-03 2.86E-02 2.94E-02 Nb-95 Tc-99 4.91E-03 4.281:-03 3.85 1:-03 3.96 E-03 Ag-110m Sb-125 2.11E-03 1.84E-03 1-129 7.16E-04 6.24E-04 7.23E-05 7.44E-05 Cs-134 Cs-137 2.22E+OO 1.93E+OO 8.89E+OO 9.15E+OO Ce-144 7.16E-02 6.24E-02 7.08E-02 7.29E-02 Pu-238 4.61 E-04 4.02E-04 8.92E-04 9.18E-04 Pu-239 1.05E-04 9.15E-05 2.62E-04 2.70E-04 Pu-240 8.20E-05 7.15E-05 2.62E-04 2.70E-04 Pu-241 4.47E-02 3.90E-02 9.38E-03 9.66E-03 Am-241 5.35E-04 4.66E-04 1.20E-03 1.24E-03 Cm-242 2.49E-04 2.17E-04 6.04E-06 6.22E-06 Cm-243 4.30E-04 3.75E-04 7.14E-04 7.35E-04 Cm-244 3.60E-04 3.14E-04 7.02E-04 7.23E-04 Totals 1.15E+02 1.00E+02 9.71E+01 1.00E+02 O.OOE+OO O.OOE+OO Note: Grey fields are where results were not reported in the NRC Regulatory Guide 1.21 Report 24 Oyster Creek 2015 Annual Radioactive Effluent Release Report Category B -Dry Compressible Waste , Contaminated Equipment , etc. Isotope Waste Class A Curies Percent H-3 1.08E-02 5.79E+OO C-14 8.68E-07 4.65E-04 P-32

4.'83E-D3

Mn-54 5.68E-03 3.05E+OO Fe-55 1.17E-01 6.27E+01 Co-57 9.64E-06 5.17E-03 Co-58 2.05E-04 1.10E-01 Co-60 3.38E-02 1.81 E+01 Ni-59 4.22E-06 2.26E-03 Ni-63 1.15E-03 6.17E-01 Zn-65 2.92E-03 1.57E+OO Sb-125 Sr-89 1. 77E-05 9.49E-03 Sr-90 3.25E-05 1.74E-02 Tc-99 6.38E-03 3.42E+OO 1-129 8.01E-04 4.30E-01 Cs-137 7.50E-03 4.02E+OO Ce-144 1.44E-04 7.72E-02 Pu-238 1.04E-06 5.5 8E-04 Pu-239 3.11E-07 1.67E-04 Pu-240 1.20E-07 6.43E-05 Pu-241 2.66E-05 1.43E-02 Am-241 1.31 E--06 7.02E-04 Cm-242 1.48E-07 7.94E-05 Cm-243 5.80E-07 3.11E-04 Cm-244 5.81 E--07 3.12E-04 Totals 1.86E-01 1.00E+02 Note: Grey fields are where results were not reported in the NRC Regulatory Guide 1.21 Report 25 Oyster Creek 2015 Annual Radioactive Effluent Release Report Category C -Irradiated components , control rods , etc. Isotope Waste Class C Curies Percent -Abundance

% H-3 C-14 Cr-51 Mn-54 Fe-55 Fe-59 Co-58 Co-60 Ni-59 Ni-63 Zn-65 Sr-90 Zr-95 Nb-94 Mo-93 Tc-99 Sb-125 1-1 29 Cs-137 Ce-144 Hf-181 Ta-182 U-235 Np-237 Pu-238 Totals O.OOE+OO O.OOE+OO Note: Grey fields are where results were not reported in the NRC Regulatory Guide 1.21 Report 26 Oyster Creek 2015 Annual Radioactive Effluent Release Report Category D -Other -Scrap Metal Isotope Waste Class A Curies Percent H-3 9.51E-03 7.93E+OO C-14 6.48E-07 5.40E-04 P-32 *

3.93E-03

Mn-54 3.43E-03 2.86E+OO Fe-55 7.50E-02 6.25E+01 Co-57 7.59E-06 6.33E-03 Co-58 1.41E-04 1.18E-01 Co-60 1.93E-02 1.61 E+01 N i-59 9.22E-07 7.69E-04 N i-63 6.88E-04 5.74E-01 Zn-65 1.71E-03 1.43E+OO Sr-85 Sr-89 1.16E-05 9.67E-03 Sr-90 1.90E-05 1.58E-02 Y-88 Tc-99 5.64E-03 4.70E+OO Cd-109 Sn-113 1-1 29 7.0 7 E-04 5.89E-0 1 Cs-137 3. 71 E-03 3.09E+OO Ba-1 33 Ce-139 Ce-144 6.11E-05 5.09E-02 Hg-203 Pu-238 6.19E-07 5.16E-04 Pu-239 1.87E-07 1.56E-04 Pu-240 2.62E-08 2.18E-05 Pu-241 1.95E-05 1.63E-02 Am-241 7.59E-07 6.33E-04 Cm-242 1.04E-07 8.67E-05 Cm-243 2.80E-07 2.33E-04 Cm-244 2.79E-07 2.33E-04 Totals 1.20E-0 1 1.00E+02 Note: Grey fields are where results were not reported i n the NRC Regulatory Gu i de 1.21 Report 27 Oyster Creek 2015 Annual Radioactive Effluent Release Report 2. Solid Waste (Disposition)

Number of Shi 6 2 8 2 1 Solutions LLC. Solutions Services B. Irradiated Fuel Shipments (disposition). There were no irradiated fuel shipments. C. Changes to the Process Control Program Revision 11 of the Process Control Program, RW-AA-100 was implemented July 1 , 2015. See the complete copy of RW-AA-100 Revision 11 attached as part of this report.

Clarified the following definitions

Blending , Classification Controlling Nuclides , Concentration Averaging, Homogeneous Waste and Nuclides of Concern.

Updated the references to NRC-201 1-0022.

Added station specific UFSAR references.

28 Oyster Creek 2015 Annual Radioactive Effluent Release Report Appendix C Radiolog i cal Impact to Man 29 Oyster Creek 2015 Annual Radioactive Effluent Release Report Per ODCM Administrative Control 6.2 , an assessment of radiation doses to the likely most exposed MEMBER OF THE PUBLIC from reactor releases and other nearby uranium fuel cycle sources (including doses from primary effluent pathways and direct radiation) for the previous calendar year must be made to show conformance with 40 CFR Part 190 , Environmental Radiation Protection Standards for Nuclear Power Operation. For purposes of this calculat i on the following assumptions were made: Gaseous

Nearest member of the public was W sector at 483 meters.

Actual 2015 meteorology and measured gaseous effluent releases were used.

All significant pathways were assumed to be present.

Occupancy factor was considered 22.8% (40 hour4.62963e-4 days 0.0111 hours 6.613757e-5 weeks 1.522e-5 months s/week for 50 weeks).

Doses calculated in the discharge canal at the Route 9 Bridge.

Fish , shellfish and shoreline pathways doses calculated.

40 CFR Part 190 Compliance

Dosimetry measurements (minus average of control stations) measured direct radiation for the nearest member of the public. The nearest member of the public for direct radiation is considered an individual that works in the warehouse west of the site. As a worker , the individual is assumed to work 2 , 000 hours0 days 0 hours 0 weeks 0 months per year at this location. Note that for the warehouse worker total dose calculations the full year (8760 hours0.101 days 2.433 hours 0.0145 weeks 0.00333 months ) values fo r Nob l e Gas , Iodine , Particulate , Carbon-14 , Tr i tium and Liquid are used.

Nearest resident was at SE sector at 937 meters.

The highest calculated dose for gamma air dose and liquid total body were summed for total body dose.

The highest calculated dose for gamma air dose , child bone and liqu i d organ were summed for organ dose.

The limits for Kr-85 , 1-129 , Pu-239 and other alpha-emitting transuranic radionuclides with half-lives greater than one year were not exceeded. The ODCM does not requ i re total body doses to the population and average doses to i ndividuals in the population from gaseous effluents to a distance of 50 miles from the site to be calculated.

30 Oyster Creek 2015 Annual Radioactive Effluent Release Report A summary of gaseous and liquid rad i at i on doses to most likely exposed MEMBER OF THE PUBLIC was as follows: Location % of A pp lic ab l e Es ti mated Age Distance Direction App li cable Effluent Organ Dose Group (meters) (toward) Limit Limit Unit Gamma -Noble Gas Air Dose 4.86E-03 All 460 NNE 4.86E-02 10 m r ad Beta -Air Noble Gas Dose 4.32E-03 All 405 E 2.16E-02 20 mrad Total Body Noble Gas (Gamma) 1.18E-03 All 988 NNE 2.36E-02 5 mrem Noble Gas Sk i n (Beta) 2.48E-03 All 988 NNE 1.65E-02 15 mrem Iodine , Particulate , Bone 5.53E-01 Child 972 ESE 3.69E+OO 15 mrem Carbon-14

& Trit i um Liquid Total body 9.86E-07 All South Route 9 3.29E-05 3 mrem Liquid Organ 9.86E-07 All Bridge 9.86E-06 10 mrem Direct Radiation Total Body 8.45E+OO All 483 w 3.38E+01 25 mrem Direct Rad i ation Total Body <LLD All 937 SE <LLD 25 mrem '"' 40 CFR Part 190 Compliance Warehouse Worker Total Dose Total Body 8.45E+OO All 483 w 3.38E+01 25 mrem Total Dose Bone 9.01E+OO All 483 w 3.60E+01 25 mrem T o t a l Dose T hy r o i d 8.45E+OO All 483 w 1.1 3E+0 1 75 mre m Nearest Resident Total Dose Total Body 4.86E-03 All 937 SE 1.94E-02 25 mrem Total Dose Bone 5.58E-01 All 937 SE 2.23E+OO 25 mrem Total Dose 1nyroid 4.86E-03 All 937 SE 0.4tit:.-U-'

to mrem 31 Oyster Creek 2015 Annual Radioactive Effluent Release Report Append ix D Meteorolog i cal Data 32 Oyster 2015 Annual Radioactive Effluent Release Report LIST OF METEOROLOGICAL DATA TABLES PAGE Table D -1 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for 34 the Oyster Creek Generating Station, January-March, 2015 Table D -2 Wind Speed by Djrection Measured at 380 Feet for var.ious Classes .fo.r 4 g the Oyster Creek Generating Station, January-March, 201 S Table D -3 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for 48 the Oyster Creek Generating Station, April -June, 2015 Table D -4 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for 55 the Oyster Creek Generating Station, April -June, 2015 Table D -5 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for 62 the Oyster Creek Generating Station, July-September, 2015 Table D -6 Wind Speed by Dire.ction Measured at 380 Feet for various Stability Classes for 69 the Oyster Creek Generating Station, July-September, 2015 Table D -7 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for 76 the Oyster Creek Generating Station, October -December, 2015 Table D -8 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for 83 the Oyster Creek Generating Station, October -December, 2015 Table D -9 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for 90 the Oyster Creek Generating Station, January -December, 2015 Table D -10 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for 98 the Oyster Creek Generating Station, January -December, 2015 33 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-1 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, January -March, 2015 Oyster Creek Alpha Period of Record: January -March 2015 Stability Class -Extremely Unstable -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 3 4 0 0 0 7 NNE 0 0 8 0 0 0 8 NE 0 1 4 0 0 0 5 ENE 0 2 2 0 0 0 4 E 0 2 1 0 0 0 3 ESE 0 4 2 0 0 0 6 SE 0 11 10 0 0 0 21 SSE 0 1 3 0 0 0 4 s 0 1 4 1 0 0 6 SSW 0 2 4 0 0 0 6 SW 0 1 0 0 0 0 1 WSW 0 3 1 2 0 0 6 w 0 3 9 0 0 0 12 WNW 0 7 35 19 0 0 61 NW 0 7 40 18 0 0 65 NNW 0 3 7 6 0 0 16 Variable 0 0 0 0 0 0 0 Total 0 51 134 46 0 0 231 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 34 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-1 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, January -March, 2015 Oyster Creek Alpha Period of Record: January -March 2015 Stability Class -Moderately Unstable -150Ft-33Ft Delta-T. (F) Winds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24

> 24 Total ---------N 0 5 1 0 0 0 6 NNE 0 1 1 0 0 0 2 NE 0 2 0 0 0 0 2 ENE 0 2 1 0 0 0 3 E 0 0 0 0 0 0 0 ESE 0 1 0 0 0 0 1 SE 0 2 3 0 0 0 5 SSE 0 1 3 0 0 0 4 s 0 1 4 1 0 0 6 SSW 0 2 0 2 0 0 4 SW 0 0 1 0 0 0 1 WSW 0 1 5 0 0 0 6 w 0 7 8 3 0 0 18 WNW 0 4 9 3 0 0 16 NW 0 6 11 4 0 0 21 NNW 0 9 2 1 0 0 12 Variable 0 0 0 0 0 0 0 Total 0 44 49 14 0 0 107 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 35 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-1 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, January -March, 2015 Oyster Creek Alpha Period of Record: January-March 2015 Stability Class -Slightly Unstable -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 1 1 2 0 0 0 4 NNE 0 0 2 0 0 0 2 NE. 0 1 0 0 0 0 1 ENE 0 3 0 0 0 0 3 E 0 1 0 0 0 0 1 ESE 0 4 0 0 0 0 4 SE 0 4 0 0 0 0 4 SSE 0 0 1 0 0 0 1 s 0 1 3 0 0 0 4 SSW 0 3 1 0 0 0 4 SW 0 0 0 0 0 0 0 WSW 0 1 2 0 0 0 3 w 0 5 4 0 0 0 9 WNW 0 10 5 6 0 0 21 NW 0 2 6 *2 0 0 10 NNW 1 6 3 1 0 0 11 Variable 0 0 0 0 0 0 0 Total 2 42 29 9 0 0 82 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 36 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-1 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, January -March, 2015 Oyster Creek Alpha Period of Record: January -March 2015 Stability Class -Neutral -150Ft-33Ft Delta-T (F) Wrnds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 13 20 7 0 0 0 40 NNE 1 32 36 0 0 0 69 NE 2 13 26 0 0 0 41 ENE 4 5 1 0 0 0 10 E 0 4 0 0 0 0 4 ESE 2 6 0 0 0 0 8 SE 8 11 0 0 0 0 19 SSE 3 16 2 0 0 0 21 s 2 7 7 1 0 0 17 SSW 4 5 21 16 0 0 46 SW 1 16 15 1 0 0 33 WSW 5 15 8 0 0 0 28 w 7 18 8 1 0 0 34 WNW 14 32 31 17 0 0 94 NW 8 33 35 23 0 0 99 NNW 12 34 31 5 0 0 82 Variable 0 0 0 0 0 0 0 Total 86 267 228 64 0 0 645 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 1 Hours of missing stability measurements in all stability classes: 4 37 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-1 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, January -March, 2015 Oyster Creek Alpha Period of Record: January -March 2015 Stability Class -Slightly Stable -:150fl-.33F.tDelta-T

.(F,) Winds Measured' at 33* Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 2 19 1 0 0 0 22 NNE 0 4 0 0 *a 0 4 NE 3 8 4 0 0 0 15 ENE 5 4 0 0 0 0 9 E 2 1 1 0 0 0 4 ESE 3 3 0 0 0 0 6 SE 3 4 0 0 0 0 7 SSE 5 5 2 0 0 0 12 s 13 21 2 0 0 0 36 SSW 18 26 6 0 0 0 50 SW 22 31 2 0 0 0 55 WSW 19 36 1 0 0 0 56 w 9 40 3 0 0 0 52 WNW 5 46 47 0 0 0 98 NW 19 56 38 1 0 0 114 NNW 8 33 14 0 0 0 55 Variable 0 0 0 0 0 0 0 Total 136 337 121 1 0 0 595 Hours of calm in this stability class: 1 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 38 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-1 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, January -March, 2015 Oyster Creek Alpha Period of Record: January -March 2015 Stability Glass -Moderately Stable -150Ft-.3.3Ft DeLta-T fF) Wind's Measured' at 33' Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 2 0 0 0 0 2 NNE 1 0 0 0 0 0 1 NE 0 0 0 0 0 0 0 ENE 1 0 0 0 0 0 1 E 1 0 0 0 0 0 1 ESE 1 0 0 0 0 0 1 SE 1 0 0 0 0 0 1 SSE 0 0 0 0 0 0 0 s 1 1 1 0 0 0 3 SSW 6 3 0 0 0 0 9 SW 13 6 0 0 0 0 19 WSW 18 17 0 0 0 0 35 w 16 10 0 0 0 0 26 WNW 16 17 0 0 0 0 33 NW 23 8 0 0 0 0 31 NNW 5 3 0 0 0 0 8 Variable 0 0 0 0 0 0 0 Total 103 67 1 0 0 0 171 Hours of calm in this stability class: 2 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 39 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-1 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, January -March, 2015 Oyster Creek Alpha Period of Record: January -March 2015 Stabmty Class -.Extremely Stable -150Ft-33Ft Delta-T {F) Wmds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 2 0 0 0 0 0 2 NNE 0 0 0 0 0 0 0 NE 1 0 0 0 0 0 1 ENE 4 1 0 0 0 0 5 E 2 0 0 0 0 0 2 ESE 1 0 0 0 0 0 1 SE 0 0 0 0 0 0 0 SSE 2 0 0 0 0 0 2 s 2 0 0 0 0 0 2 SSW 6 0 0 0 0 0 6 SW 25 3 0 0 0 0 28 WSW 64 7 0 0 0 0 71 w 79 13 0 0 0 0 92 WNW 49 1 0 0 0 0 50 NW 31 8 0 0 0 0 39 NNW 7 3 0 0 0 0 10 Variable 0 0 0 0 0 0 0 Total 275 36 0 0 0 0 311 Hours of calm in this stability class: 10 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 40 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-2 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, January -March, 2015 Oyster Creek Alpha Period of Record: January -March 2015 Stability Class -Extremely Unstable -380Ft-33Ft Oelta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 0 1 0 0 0 1 NNE 0 0 0 0 1 0 1 NE 0 0 0 2 0 0 2 ENE 0 0 0 0 0 0 0 E 0 0 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE 0 0 0 0 0 0 0 s 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 w 0 0 0 0 0 0 0 WNW 0 0 0 1 3 1 5 NW 0 0 0 5 5 2 12 NNW 0 0 0 1 1 1 3 Variable 0 0 0 0 0 0 0 Total 0 0 1 9 10 4 24 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 41 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-2 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, January -March, 2015 Oyster Creek Alpha Period of Record: January -March 2015 Stability Class -Moderately Unstable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 0 1 1 0 0 2 NNE 0 0 0 2 1 0 3 NE 0 0 0 2 0 0 2 ENE 0 0 0 1 0 0 1 E 0 0 1 0 0 0 1 ESE 0 0 1 0 0 0 1 SE 0 0 1 0 0 0 1 SSE 0 0 1 0 0 0 1 s 0 0 0 1 0 0 1 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 w 0 0 1 4 2 0 7 WNW 0 0 0 7 5 8 20 NW 0 0 6 6 3 7 22 NNW 0 0 2 3 1 0 6 Variable 0 0 0 0 0 0 0 Total 0 0 14 27 12 15 68 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 2 Hours of missing stability measurements in all stability classes: 4 42 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-2 Wind Speed by Direction Measured at 380 Feet for various Stability .Classes for the Oyster Creek Generating Station, January -March, 2015 Oyster Creek Alpha Period of Record: January -March 2015 Stability Class -Slightly Unstable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 2 1 2 0 0 5 NNE 0 0 0 3 2 0 5 NE 0 0 1 0 0 0 1 ENE 0 1 0 1 0 0 2 E 0 0 0 0 0 0 0 ESE 0 1 1 0 0 0 2 SE 0 0 7 0 0 0 7 SSE 0 0 2 0 0 0 2 s 0 0 1 1 1 0 3 SSW 0 1 2 2 2 0 7 SW 0 0 0 0 0 0 0 WSW 0 0 1 1 1 2 5 w 0 1 3 2 4 1 11 WNW 0 1 3 16 9 16 45 NW 0 0 4 3 8 5 20 NNW 0 0 0 2 0 3 5 Variable 0 0 0 0 0 0 0 Total 0 7 26 33 27 27 120 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 6 Hours of missing stability measurements in all stability classes: 4 43 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-2 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, January -March, 2015 Oyster Creek Alpha Period of Record: January -March 2015 Stability Class -Neutral -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 6 15 14 4 0 39 NNE 0 4 15 53 10 1 83 NE 1 2 11 18 22 4 58 ENE 1 5 5 3 1 0 15 E 2 3 0 1 0 0 6 ESE 1 4 4 3 0 0 12 SE 0 4 4 4 0 0 12 SSE 0 6 14 3 1 0 24 s 1 6 15 6 3 0 31 SSW 0 4 14 11 9 12 50 SW 1 2 5 17 17 2 44 WSW 0 4 10 15 9 0 38 w 1 11 25 24 14 6 81 WNW 1 5 37 39 40 44 166 NW 0 7 15 28 48 46 144 NNW 0 7 22 31 31 17 108 Variable 0 0 0 0 0 0 0 Total 9 80 211 270 209 132 911 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 27 Hours of missing stability measurements in all stability classes: 4 44 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-2 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, January -March, 2015 Oyster Creek Alpha Period of Record: January -March 2015 Stability Class -Slightly Stable -380Ft-33Ft Delta-T (F) W!nds Measur-ed at-3.80 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 3 15 10 0 0 28 NNE 0 1 3 4 0 0 8 NE 0 1 0 8 3 0 12 ENE 0 0 1 4 1 0 6 E 0 1 1 1 3 0 6 ESE 0 0 3 2 0 0 5 SE 0 0 1 5 2 0 8 SSE 1 0 3 3 0 1 8 s 0 1 9 16 6 4 36 SSW 0 1 12 23 12 4 52 SW 1 2 9 19 19 1 51 WSW 0 1 8 21 16 6 52 w 0 7 11 21 32 2 73 WNW 1 2 7 30 27 8 75 NW 0 0 7 40 33 2 82 NNW 0 0 5 19 14 0 38 Variable 0 0 0 0 0 0 0 Total 3 20 95 226 168 28 540 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 11 Hours of missing stability measurements in all stability classes: 4 45 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-2 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, January -March, 2015 Oyster Creek Alpha Period of Record: January -March 2015 Stability Class -Moderately Stable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 1 3 12 5 0 21 NNE 0 0 3 4 0 0 7 NE 0 0 0 0 0 0 0 ENE 0 0 0 0 0 0 0 E 0 0 1 1 0 0 2 ESE 0 3 1 0 0 0 4 SE 1 2 2 1 0 0 6 SSE 0 2 0 0 0 0 2 s 0 1 3 4 0 0 8 SSW 0 0 1 7 0 0 8 SW 0 2 5 16 7 0 30 WSW 0 0 6 12 15 6 39 w 0 0 4 13 12 6 35 WNW 0 0 5 11 13 2 31 NW 0 1 1 7 9 0 18 NNW 0 1 2 20 11 3 37 Variable 0 0 0 0 0 0 0 Total 1 13 37 108 72 17 248 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 20 Hours of missing stability measurements in all stability classes: 4 46 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-2 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, January-March, 2015 Oyster Creek Alpha Period of Record: January -March 2015 Stability Class -Extremely Stable -380Ft-33Ft Delta-T (F) Winds Measured at -380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24

> 24 Total ---------N 1 2 6 7 2 0 18 NNE 0 0 1 0 0 0 1 NE 1 1 2 1 1 0 6 ENE 0 0 0 3 0 0 3 E 1 0 0 0 0 0 1 ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE 0 2 6 2 0 0 10 s 0 0 1 6 1 1 9 SSW 0 0 5 4 0 0 9 SW 0 1 3 11 2 0 17 WSW 0 2 8 5 1 2 18 w 1 5 9 7 11 2 35 WNW 1 5 2 13 6 0 27 NW 0 2 2 5 2 0 11 NNW 0 0 0 3 2 0 5 Variable 0 0 0 0 0 0 0 Total 5 20 45 67 28 5 170 Hours of calm in this stability class: 1 Hours of missing wind measurements in this stability class: 8 Hours of missing stability measurements in all stability classes: 4 47 Oyster Creek 2015 Anriual Radioactive Effluent Release Report Table D-3 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the

Oyster Creek Generating Station, April -June, 2015 Oyster Creek Alpha Period of Record: April -June 2015 Stability Class -Extremely Unstable -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 1 7 0 0 0 8 NNE 0 7 0 0 0 0 7 NE 0 9 15 0 0 0 24 ENE 0 12 34 0 0 0 46 E 0 11 9 2 0 0 22 ESE 0 17 10 0 0 0 27 SE 0 11 33 0 0 0 44 SSE 0 7 31 4 0 0 42 s 0 2 28 50 0 0 80 SSW 0 2 14 10 0 0 26 SW 1 7 18 2 0 0 28 WSW 0 5 17 4 0 0 26 w 0 3 14 2 0 0 19 WNW 0 6 17 3 0 0 26 NW 0 13 43 11 0 0 67 NNW 0 3 6 0 0 0 9 Variable 0 0 0 0 0 0 0 Total 1 116 296 88 0 0 501 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 48 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-3 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, April -June, 2015 Oyster Creek Alpha Period of Record: April -June 2015 Stability Class -Moderately Unstable -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 1 0 0 0 0 1 NNE 0 4 0 0 0 0 4 NE 0 5 6 0 0 0 11 ENE 0 4 6 0 0 0 10 E 0 5 2 0 0 0 7 ESE 0 7 2 0 0 0 9 SE 0 7 4 0 0 0 11 SSE 3 5 3 0 0 0 11 s 0 2 6 3 0 0 11 SSW 1 4 6 3 0 0 14 SW 0 '7 0 0 0 0 7 WSW 0 6 1 0 0 0 7 w 0 6 6 1 0 0 13 WNW 0 5 6 0 0 0 11 NW 1 4 6 1 0 0 12 NNW 0 3 2 0 0 0 5 Variable 0 0 0 0 0 0 0 Total 5 75 56 8 0 0 144 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 49 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-3 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, April -June, 2015 Oyster Creek Alpha Period of Record: April -June 2015 Stability Class -Slightly Unstable -150Ft-33Ft Delta-T (F) Wlnds Measured at .33 Fee! Wind Speed (in mph) Wind Direction 1-3, 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 0 0 0 0 0 0 NNE 0 3 0 0 0 0 3 NE 0 4 7 0 0 0 11 ENE 0 3 1 0 0 0 4 E 0 5 1 0 0 0 6 ESE 0 3 0 0 0 0 3 SE 0 3 0 0 0 0 3 SSE l 3 4 0 0 0 8 s 0 1 2 3 0 0 6 SSW 1 3 2 0 0 0 6 SW 0 1 3 0 0 0 4 WSW 1 3 1 0 0 0 5 w 0 1 3 0 0 0 4 WNW 0 0 2 0 0 0 2 NW 1 3 1 1 0 0 6 NNW 0 1 0 0 0 0 1 Variable 0 0 0 0 0 0 0 Total 4 37 27 4 0 0 72 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 50 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-3 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, April -June, 2015 Oyster Creek Alpha Period of Record: April -June 2015 Stability Class -Neutral -150Ft-33Ft Delta-T (F) WLnds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 5 4 0 0 0 0 9 NNE 6 24 3 0 0 0 33 NE 14 51 40 0 0 0 105 ENE 8 27 18 2 0 0 55 E 4 6 16 6 0 0 32 ESE 2 4 5 2 0 0 13 SE 2 34 1 0 0 0 37 SSE 3 23 4 1 0 0 31 s 6 20 20 1 0 0 47 SSW 3 13 14 16 0 0 46 SW 1 21 12 0 0 0 34 WSW 1 14 5 0 0 0 20 w 2 9 11 0 0 0 22 WNW 5 7 11 0 0 0 23 NW 1 5 11 0 0 0 17 NNW 6 6 3 0 0 0 15 Variable 0 0 0 0 0 0 0 Total 69 268 174 28 0 0 539 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 51 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-3 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, April -June, 2015 Oyster Creek Alpha Period of Record: April -June 2015 Stability Class -Slightly Stable -150Ft-33Ft Delta-T (F) Winds Measured at-33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 4 0 0 0 0 0 4 NNE 1 2 0 0 0 0 3 NE 11 18 2 0 0 0 31 ENE 4 8 1 0 0 0 13 E 5 4 1 1 0 0 11 ESE 4 5 0 0 0 0 9 SE 5 6 0 0 0 0 11 SSE 13 13 4 0 0 0 30 s 15 32 12 0 0 0 59 SSW 11 75 56 6 0 0 148 SW 13 44 9 0 0 0 66 WSW 6 26 2 0 0 0 34 w 9 19 0 0 0 0 28 WNW 6 24 1 0 0 0 31 NW 10 37 4 1 0 0 52 NNW 4 6 3 0 0 0 13 Variable 0 0 0 0 0 0 0 Total 121 319 95 8 0 0 543 Hours of calm in this stability class: 7 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 52 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-3 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, April -June, 2015 Oyster Creek Alpha Period of Record: April -June 2015 Stability Class -Moderately Stable -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 4 1 0 0 0 0 5 NNE 4 1 0 0 0 0 5 NE 2 1 0 0 0 0 3 ENE 3 0 0 0 0 0 3 E 2 1 0 0 0 0 3 ESE 4 0 0 0 0 0 4 SE 1 0 0 0 0 0 1 SSE 3 0 0 0 0 0 3 s 11 0 0 0 0 0 11 SSW 13 4 0 0 0 0 17 SW 11 11 0 0 0 0 22 WSW 10 20 0 0 0 0 30 w 9 7 0 0 0 0 16 WNW 11 6 1 0 0 0 18 NW 8 12 0 0 0 0 20 NNW 7 1 0 0 0 0 8 Variable 0 0 0 0 0 0 0 Total 103 65 1 0 0 0 169 Hours of calm in this stability class: 2 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 53 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-3 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, April -June, 2015 Oyster Creek Alpha Period of Record: April -June 2015 Stability Class -Extremely Stable -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24

> 24 Total ---------N 5 0 0 0 0 0 5 NNE 1 0 0 0 0 0 1 NE 0 0 0 0 0 0 0 ENE 0 0 0 0 0 0 0 E 0 0 0 0 0 0 0 ESE 1 0 0 0 0 0 1 SE 0 0 0 0 0 0 0 SSE 3 0 0 0 0 0 3 s 4 0 0 0 0 0 4 SSW 6 1 0 0 0 0 7 SW 13 4 0 0 0 0 17 WSW 30 11 0 0 0 0 41 w 42 3 0 0 0 0 45 WNW 25 6 0 0 0 0 31 NW 27 6 0 0 0 0 33 NNW 6 1 0 0 0 0 7 Variable 0 0 0 0 0 0 0 Total 163 32 0 0 0 0 195 Hours of calm in this stability class: 8 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 54 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-4 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, April -June, 2015 Oyster Creek Alpha Period of Record: April -June 2015 Stability Class -Extremely Unstable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 0 0 0 0 0 0 NNE 0 0 1 0 0 0 1 NE 0 0 0 2 2 0 4 ENE 0 0 4 8 1 0 13 E 0 0 2 '1 2 0 5 ESE 0 0 2 0 0 0 2 SE 0 0 1 0 0 0 1 SSE 0 2 1 1 1 0 5 s 0 0 2 9 8 2 21 SSW 0 0 0 3 7 3 13 SW 0 0 0 3 1 0 4 WSW 0 0 0 1 4 2 7 w 0 0 2 2 7 0 11 WNW 0 0 1 2 0 0 3 NW 0 0 0 7 13 5 25 NNW 0 0 0 0 0 0 0 Variable 0 0 0 0 0 0 0 Total 0 2 16 39 46 12 115 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 55 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-4 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, April -June, 2015 Oyster Creek Alpha Period of Record: April -June 2015 Stability Class -Moderately Unstable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 0 0 5 0 0 5 NNE 0 0 1 0 0 0 1 NE 0 1 2 4 1 0 8 ENE 0 0 3 9 4 0 16 E 0 0 3 3 2 0 8 ESE 0 1 8 0 0 0 9 SE 0 1 7 2 0 0 10 SSE 0 0 3 7 0 0 10 s 0 1 5 12 12 1 31 SSW 0 0 2 5 4 5 16 SW 1 0 1 7 1 0 10 WSW 0 0 0 7 1 1 9 w 0 0 0 1 1 1 3 WNW 0 0 2 4 5 0 11 NW 0 0 2 10 5 4 21 NNW 0 0 4 3 0 0 7 Variable 0 0 0 0 0 0 0 Total 1 4 43 79 36 12 175 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 56 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-4 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, April -June, 2015 Oyster Creek Alpha Period of Record: April -June 2015 Stability Class -Slightly Unstable -380Ft-33Ft Delta-T (F) Winds Measured at-380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 0 2 1 0 0 3 NNE 0 1 3 0 0 0 4 NE 0 1 5 7 4 0 17 ENE 0 4 1 2 3 0 10 E 0 1 4 2 0 0 7 ESE 0 3 3 1 0 0 7 SE 0 2 9 0 0 0 11 SSE 0 0 10 8 l 0 19 s 0 1 2 5 5 1 14 SSW 0 0 2 3 6 5 16 SW 0 0 4 6 0 0 10 WSW 0 0 2 9 1 1 13 w 0 0 1 1 5 1 8 WNW 0 1 3 5 5 2 16 NW 0 0 9 3 6 3 21 NNW 0 0 0 4 0 0 4 Variable 0 0 0 0 0 0 0 Total 0 14 60 57 36 13 180 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 57 Oyster Creek 2015 Annual Radioactive Effluent Release Report TableD-4 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, April -June, 2015 Oyster Creek Alpha Period of Record: April -June 2015 Stability Class -Neutral -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 1 3 3 1 1 0 9 NNE 1 6 12 11 0 0 30 NE 1 19 33 51 31 13 148 ENE 1 9 14 29 17 5 75 E 2 9 8 11 14 7 51 ESE 2 9 7 6 2 .0 26 SE 1 9 33 3 0 0 46 SSE 0 11 23 12 0 0 46 s 1 9 22 24 5 0 61 SSW 3 3 18 38 40 24 126 SW 1 5 11 31 9 0 57 WSW 0 7 9 13 7 1 37 w 4 2 17 15 9 1 48 WNW 0 3 4 4 14 0 25 NW 0 2 2 19 13 8 44 NNW 0 3 3 4 4 0 14 Variable 0 0 0 0 0 0 0 Total 18 109 219 272 166 59 843 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 58 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-4 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, April -June, 2015 Oyster Creek Alpha Period of Record: April -June 2015 Stability Class -Slightly Stable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 0 5 3 1 0 9 NNE 0 4 5 3 1 0 13 NE 0 4 6 5 4 0 19 ENE 3 0 4 2 0 0 9 E 0 3 7 2 1 1 14 ESE 0 2 10 0 0 1 13 SE 2 1 3 1 0 1 8 SSE 1 6 7 7 3 1 25 s 2 8 11 33 2 0 56 SSW 0 6 18 44 38 8 114 SW 0 7 5 22 48 6 88 WSW 1 1 4 28 12 1 47 w 1 0 3 13 7 1 25 WNW 1 2 6 11 9 0 29 NW 2 2 5 18 21 1 49 NNW 0 1 0 7 17 0 25 Variable 0 0 0 0 0 0 0 Total 13 47 99 199 164 21 543 Hours of calm in this stability class: 1 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 59 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-4 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, April -June, 2015 Oyster Creek Alpha Period of Record: April -June 2015 Stability Class -Moderately Stable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 1 0 1 2 0 1 5 NNE 0 3 3 2 1 0 9 NE 0 6 4 1 0 0 11 ENE 0 3 1 0 0 0 4 E 0 2 0 1 0 0 3 ESE 0 0 0 0 0 0 0 SE 0 0 1 0 0 0 1 SSE 1 0 1 0 0 0 2 s 2 1 1 1 0 0 5 SSW 0 1 4 11 8 1 25 SW 1 3 2 3 11 1 21 WSW 0 2 9 3 13 3 30 w 0 1 1 8 7 1 18 WNW 0 1 1 2 6 1 11 NW 1 0 0 3 13 1 18 NNW 0 1 2 8 13 0 24 Variable 0 0 0 0 0 0 0 Total 6 24 31 45 72 9 187 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 60 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-4 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, April -June, 2015 Oyster Creek Alpha Period of Record: April -June 2015 Stability Class -Extremely Stable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 0 5 9 1 2 17 NNE 0 3 0 3 0 0 6 NE 1 0 3 2 1 0 7 ENE 0 0 0 0 0 0 0 E 0 1 1 0 0 0 2 ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE 0 0 0 0 0 0 0 s 0 0 1 4 1 0 6 SSW 0 0 1 5 3 0 9 SW 1 1 2 9 9 2 24 WSW 0 0 3 0 7 4 14 w 0 2 2 1 5 0 10 WNW 0 1 5 4 3 0 13 NW 0 1 6 3 4 2 16 NNW 0 2 5 4 1 0 12 Variable 0 0 0 0 0 0 0 Total 2 11 34 44 35 10 136 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 4 61 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-5 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, July-September, 2015 Oyster Creek Alpha Period of Record: July -September 2015 StaOmty Class-Extremely Unstable -

Delta-T {F) Wi"nds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 3 1 0 0 0 4 NNE 0 4 0 0 0 0 4 NE 0 10 20 0 0 0 30 ENE 0 17 35 0 0 0 52 E 0 8 3 0 0 0 11 ESE 0 15 6 0 0 0 21 SE 0 11 46 4 0 0 61 SSE 0 1 38 1 0 0 40 s 0 5 41 3 0 0 49 SSW 0 6 12 0 0 0 18 SW 0 17 9 0 0 0 26 WSW 0 13 7 0 0 0 20 w 0 11 10 0 0 0 21 WNW 0 6 15 0 0 0 21 NW 0 12 6 0 0 0 18 NNW 0 6 2 0 0 0 8 Variable 0 0 0 0 0 0 0 Total 0 145 251 8 0 0 404 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 62 Oyster Creek 2015 Annual Radioactive Effluent*Release Report Table D-5 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, July -September, 2015 Oyster Creek Alpha Period of Record: July -September 2015 Stability Class -Moderately Unstable -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 7 1 0 0 0 8 NNE 0 2 2 0 0 0 4 NE 0 9 7 0 0 0 16 ENE 1 10 5 0 0 0 16 E 0 4 2 0 0 0 6 ESE 0 4 0 0 0 0 4 SE 0 13 6 1 0 0 20 SSE 0 2 13 0 0 0 15 s 0 3 11 1 0 0 15 SSW 1 3 5 0 0 0 9 SW 3 5 3 0 0 0 11 WSW 0 4 1 0 0 0 5 w 0 7 0 0 0 0 7 WNW 0 6 1 0 0 0 7 NW 1 9 1 0 0 0 11 NNW 0 13 1 0 0 0 14 Variable 0 0 0 0 0 0 0 Total 6 101 59 2 0 0 168 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 63 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-5 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, July -September, 2015 Oyster Creek Alpha Period of Record: July -September 2015 Stability Class -Slightly Unstable -150Ft-33Ft Delta-T (F) Winds Measured at -33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 1 3 0 0 0 0 4 NNE 0 3 0 0 0 0 3 NE 0 3 3 0 0 0 6 ENE 0 4 2 0 0 0 6 E 0 0 0 0 0 0 0 ESE 0 1 1 0 0 0 2 SE 0 4 6 0 0 0 10 SSE 1 l 6 0 0 0 8 s 0 1 12 0 0 0 13 SSW 0 3 1 0 0 0 4 SW 0 4 1 0 0 0 5 WSW 1 5 1 0 0 0 7 w 0 1 2 0 0 0 3 WNW 3 1 0 0 0 0 4 NW 0 2 1 0 0 0 3 NNW 0 3 1 0 0 0 4 Variable 0 0 0 0 0 0 0 Total 6 39 37 0 0 0 82 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 64 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-5 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, July -September, 2015 Oyster Creek Alpha Period of Record: July-September 2015 Stability Class -Neutral -150Ft-33FtDelta-T

{F) IMnds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24

> 24 Total ---------N 5 10 1 0 0 0 16 NNE 0 8 0 0 0 0 8 NE 1 26 27 0 0 0 54 ENE 1 11 24 0 0 0 36 E 3 6 1 0 0 0 10 ESE 0 14 5 0 0 0 19 SE 2 25 10 1 0 0 38 SSE 3 24 10 0 0 0 37 s 1 21 19 0 0 0 41 SSW 2 14 15 0 0 0 31 SW 1 14 1 0 0 0 16 WSW 2 14 2 0 0 0 18 w 4 10 0 0 0 0 14 WNW 7 8 2 0 0 0 17 NW 8 11 2 0 0 0 21 NNW 8 22 0 0 0 0 30 Variable 0 0 0 0 0 0 0 Total 48 238 119 1 0 0 406 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 65 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-5 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, July -September, 2015 Oyster Creek Alpha Period of Record: July -September 2015 Stability Class -Slightly Stable -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 6 8 1 0 0 0 15 NNE 6 8 0 0 0 0 14 NE 6 29 9 0 0 0 44 ENE 3 10 25 0 0 0 38 E 2 3 0 0 0 0 5 ESE 1 4 0 0 0 0 5 SE 5 13 4 0 0 0 22 SSE 13 12 0 0 0 0 25 s 12 40 1 0 0 0 53 SSW 17 70 3 0 0 0 90 SW 18 50 0 0 0 0 68 WSW 13 40 0 0 0 0 53 w 9 21 0 0 0 0 30 WNW 13 12 0 0 0 0 25 NW 10 6 0 0 0 0 16 NNW 6 9 2 0 0 0 17 Variable 0 0 0 0 0 0 0 Total 140 335 45 0 0 0 520 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 66 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-5 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, July-September, 2015 Oyster Creek Alpha Period of Record: July -September 2015 Stability Class -Moderately Stable -150Ft-33Ft Delta-T (F} Winds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 4 3 0 0 0 0 7 NNE 3 2 0 0 0 0 5 NE 0 0 0 0 0 0 0 ENE 1 2 0 0 0 0 3 E 3 1 0 0 0 0 4 ESE 1 0 0 0 0 0 1 SE 2 1 0 0 0 0 3 SSE 8 1 0 0 0 0 9 s 17 3 0 0 0 0 20 SSW 17 4 0 0 0 0 21 SW 16 8 0 0 0 0 24 WSW 24 9 0 0 0 0 33 w 23 6 0 0 0 0 29 WNW 15 3 0 0 0 0 18 NW 16 7 0 0 0 0 23 NNW 6 4 0 0 0 0 10 Variable 0 0 0 0 0 0 0 Total 156 54 0 0 0 0 210 Hours of calm in this stability class: 5 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 67 Oyster Creek 2015 Annual Radioactive Effluent Release Report TableD-5 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, July-September, 2015 Oyster Creek Alpha Period of Record: July -September 2015 Stability Class -Extremely Stable -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24

> 24 Total ---------N 8 0 0 0 0 0 8 NNE 0 0 0 0 0 0 0 NE 0 0 0 0 0 0 0 ENE 0 0 0 0 0 *o 0 E 0 0 0 0 0 0 0 ESE 0 1 0 0 0 0 1 SE 0 0 0 0 0 0 0 SSE 2 0 0 0 0 0 2 s 8 0 0 0 0 0 8 SSW 8 0 0 0 0 0 8 SW 17 0 0 0 0 0 17 WSW 68 6 0 0 0 0 74 w 152 1 0 0 0 0 153 WNW 65 2 0 0 0 0 67 NW 38 5 0 0 0 0 43 NNW 15 2 0 0 0 0 17 Variable 0 0 0 0 0 0 0 Total 381 17 0 0 0 0 398 Hours of calm in this stability class: 15 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 68 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-6 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, July-September, 2015 Oyster Creek Alpha Period of Record: July -September 2015 Stability Class -Extremely Unstable -380Ft-33Ft Delta-T (F) Winds Measur-ed at .380 F-eet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24

> 24 Total ---------N 0 0 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE 0 0 0 1 0 0 1 ENE 0 0 0 2 0 0 2 E 0 0 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE 0 0 0 0 0 0 0 s 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 w 0 0 0 1 0 0 1 WNW 0 0 0 3 0 0 3 NW 0 0 0 0 0 0 0 NNW 0 0 0 0 0 0 0 Variable 0 0 0 0 0 0 0 Total 0 0 0 7 0 0 7 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 69 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-6 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, July -September, 2015 Oyster Creek Alpha Period of Record: July -September 2015 Stability Class -Moderately Unstable -380Ft-33Ft Delta-T (F) Winds Measured at -380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 0 0 1 0 0 1 NNE 0 0 0 0 0 0 0 NE 0 0 4 9 1 0 14 ENE 0 0 5 8 1 0 14 E 0 0 3 0 0 0 3 ESE 0 0 3 0 0 0 3 SE 0 0 6 2 4 0 12 SSE 0 0 3 I 0 0 10 s 0 0 1 18 1 0 20 SSW 0 0 0 4 0 0 4 SW 0 0 1 4 0 0 5 WSW 0 0 2 5 1 0 8 w 0 0 2 6 0 0 8 WNW 0 0 0 4 5 0 9 NW 0 0 0 1 0 0 1 NNW 0 0 0 0 0 0 0 Variable 0 0 0 0 0 0 0 Total 0 0 30 69 13 0 112 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 70 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-6 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, July -September, 2015 Oyster Creek Alpha Period of Record: July -September 2015 Stability Class -Slightly Unstable -380Ft-33Ft Delta-T (F) Winds Measured at . .380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 0 4 1 0 0 5 NNE 0 1 2 0 0 0 3 NE 0 0 12 11 0 0 23 ENE 0 2 13 7 4 0 26 E 0 0 12 0 0 0 12 ESE 0 5 3 0 0 0 8 SE 0 1 25 0 2 0 28 SSE 0 0 19 19 0 0 38 s 0 0 4 13 2 0 19 SSW 0 2 4 12 0 0 18 SW 0 0 7 1 0 0 8 WSW 0 4 10 3 0 0 17 w 0 3 3 5 0 0 11 WNW 0 1 4 4 1 0 10 NW 0 2 7 4 0 0 13 NNW 0 0 9 1 0 0 10 Variable 0 0 0 0 0 0 0 Total 0 21 138 81 9 0 249 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 71 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-6 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, July -September, 2015 Oyster Creek Alpha Period of Record: July -September 2015 Stability Class -Neutral -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 1 9 15 11 0 '0 36 NNE 0 3 7 4 0 0 14 NE 1 4 22 53 18 1 99 ENE 2 8 16 6 39 16 87 E 1 6 7 5 0 0 19 ESE 0 9 18 5 0 0 32 SE 1 7 34 18 2 0 62 SSE 1 12 31 24 1 0 69 s 0 7 27 41 5 1 81 SSW 2 4 18 40 8 1 73 SW 0 8 11 20 0 0 39 WSW 0 6 14 8 0 0 28 w 1 11 9 12 1 0 34 WNW 2 5 15 6 1 0 29 NW 1 13 15 4 0 0 33 NNW 2 5 20 8 0 0 35 Variable 0 0 0 0 0 0 0 Total 15 117 279 265 75 19 770 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes; 0 72 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-6 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, July -September, 2015 Oyster Creek Alpha Period of Record: July-September 2015 Stability Class -Slightly Stable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 5 2 11 0 0 18 NNE 0 1 2 6 1 0 10 NE 1 5 13 5 2 0 26 ENE 1 6 9 6 10 3 35 E 0 3 5 1 0 0 9 ESE 1 3 2 1 3 0 10 SE 0 3 6 5 1 2 17 SSE 1 3 13 5 0 1 23 .S 1 4 12 26 0 0 43 SSW 0 2 18 74 3 0 97 SW 0 2 10 57 28 0 97 WSW 0 0 5 23 10 0 38 w 0 0 2 17 8 0 27 WNW 0 2 7 12 4 0 25 NW 0 2 2 7 3 0 14 NNW 0 3 3 8 2 0 16 Variable 0 0 0 0 0 0 0 Total 5 44 111 264 75 6 505 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 73 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-6 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, July -September, 2015 Oyster Creek Alpha Period of Record: July -September 2015 Stability Class -Moderately Stable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 2 3 14 2 0 21 NNE 1 3 4 3 1 0 12 NE 2 0 3 3 0 0 8 ENE 0 0 3 3 0 0 6 E 1 0 1 0 0 0 2 ESE 1 0 0 0 0 0 1 SE 0 4 2 0 0 0 6 SSE 0 2 7 0 0 0 9 s 0 2 11 1 0 0 14 SSW 0 5 7 10 0 0 22 SW 1 2 2 12 20 0 37 WSW 1 2 5 9 12 3 32 w 0 0 5 7 10 1 23 WNW 0 3 5 12 5 2 27 NW 0 5 4 10 10 0 29 NNW 0 3 1 13 8 0 25 Variable 0 0 0 0 0 0 0 Total 7 33 63 97 68 6 274 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 74 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-6 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, July -September, 2015 Oyster Creek Alpha Period of Record: July -September 2015 Stability Class -Extremely Stable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 0 5 17 0 0 22 NNE 0 4 14 5 0 0 23 NE 0 2 7 3 0 0 12 ENE 0 2 4 2 0 0 8 E 0 1 3 0 0 0 4 ESE 0 1 3 0 0 0 4 SE 0 3 0 0 0 0 3 SSE 0 0 0 0 0 0 0 s 0 1 10 0 0 0 11 SSW 0 6 12 8 0 0 26 SW 0 3 13 4 1 0 21 WSW 0 3 9 6 6 1 25 w 1 0 7 11 2 0 21 WNW 2 6 8 21 3 0 40 NW 1 5 22 11 5 0 44 NNW 0 3 5 11 8 0 27 Variable 0 0 0 0 0 0 0 Total 4 40 122 99 25 1 291 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 0 75 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-7 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, October -December, 2015 Oyster Creek Alpha Period of Record: October -December2015 Stability Class -Extremely Unstable -150Ft-33Ft Delta-T {F) Wi"nds Measured af 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 1 1 0 0 0 2 NNE 0 1 3 0 0 0 4 NE 0 2 1 0 0 0 3 ENE 0 8 9 0 0 0 17 E 0 3 0 0 0 0 3 ESE 0 4 0 0 0 0 4 SE 0 1 1 0 0 0 2 SSE 0 2 1 0 0 0 3 s 0 4 1 1 0 0 6 SSW 0 1 5 1 0 0 7 SW 0 3 3 0 0 0 6 WSW 0 1 7 0 0 0 8 w 0 3 5 0 0 0 8 WNW 0 8 14 1 0 0 23 NW 0 1 17 1 0 0 19 NNW 0 4 5 0 0 0 9 Variable 0 0 0 0 0 0 0 Total 0 47 73 4 0 0 124 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 5 76 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-7 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, October -December, 2015 Oyster Creek Alpha Period of Record: October -December2015 Stability Class -Moderately Unstable -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 2 0 0 0 0 2 NNE 0 0 4 0 0 0 4 NE 0 1 4 0 0 0 5 ENE 0 5 1 0 0 0 6 E 0 3 0 0 0 0 3 ESE 0 10 3 0 0 0 13 SE 0 5 0 0 0 0 5 SSE 0 0 1 0 0 0 1 s 0 1 3 0 0 0 4 SSW 0 0 2 0 0 0 2 SW 0 5 5 0 0 0 10 WSW 0 7 3 0 0 0 10 w 0 5 3 1 0 0 9 WNW 0 10 6 2 0 0 18 NW 0 6 7 0 0 0 13 NNW 0 4 3 0 0 0 7 Variable 0 0 0 0 0 0 0 Total 0 64 45 3 0 0 112 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 5 77 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-7 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, October -December, 2015 Oyster Creek Alpha Period of Record: October -December2015 Stability Class -Slightly Unstable -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 4 0 0 0 0 4 NNE 0 1 0 0 0 0 1 NE 0 0 1 0 0 0 1 ENE 0 3 1 0 0 0 4 E 0 1 0 0 0 0 1 ESE 0 5 1 0 0 0 6 SE 0 3 0 0 0 0 3 SSE 0 1 3 0 0 0 4 s 0 0 1 1 0 0 2 SSW 0 1 1 0 0 0 2 SW 0 3 2 0 0 0 5 WSW 0 5 2 0 0 0 7 w 0 8 2 1 0 0 11 WNW 0 3 4 3 0 0 10 NW 1 6 2 0 0 0 9 NNW 0 0 0 0 0 0 0 Variable 0 0 0 0 0 0 0 Total 1 44 20 5 0 0 70 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 5 78 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-7 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, October -December, 2015 Oyster Creek Alpha Period of Record: October-December2015 Stability Class -Neutral -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 4 16 1 0 0 0 21 NNE 8 17 24 1 0 0 50 NE 1 12 54 28 0 0 95 ENE 5 19 27 0 0 0 51 E 3 19 10 12 0 0 44 ESE 0 12 8 1 0 0 21 SE 5 20 5 1 0 0 31 SSE 0 3 17 '1 0 0 21 s 2 7 6 7 0 0 22 SSW 0 12 21 8 0 0 41 SW 2 12 16 1 0 0 31 WSW 4 15 6 0 0 0 25 w 2 18 6 1 0 0 27 WNW 1 28 16 2 0 0 47 NW 5 21 11 0 0 0 37 NNW 6 18 8 0 0 0 32 Variable 0 0 0 0 0 0 0 Total 48 249 236 63 0 0 596 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 5 79 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-7 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, October -December, 2015 Oyster Creek Alpha Period of Record: October-December2015 Stability Class -Slightly Stable -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24

> 24 Total ---------N 4 6 0 0 0 0 10 NNE 6 7 1 0 0 0 14 NE 8 10 8 2 0 0 28 ENE 13 4 10 0 0 0 27 E 10 13 4 0 0 0 27 ESE 1 13 6 0 0 0 20 SE 6 20 10 0 0 0 36 SSE 7 15 6 0 0 0 28 s 14 17 8 0 0 0 39 SSW 8 35 15 0 0 0 58 SW 10 33 10 0 0 0 53 WSW 10 68 2 0 0 0 80 w 15 52 7 0 0 0 74 WNW 9 39 5 0 0 0 53 NW 8 23 5 0 0 0 36 NNW 8 29 4 0 0 0 41 Variable 0 0 0 0 0 0 0 Total 137 384 101 2 0 0 624 Hours of calm in this stability class: 1 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 5 80 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-7 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, October -December, 2015 Oyster Creek Alpha Period of Record: October -December2015 Stability Class -Moderately Stable -150Ft-33Ft Delta-T (F) Wmds Measured at 33 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24

> 24 Total ---------N 2 2 0 0 0 0 4 NNE 3 1 0 0 0 0 4 NE 2 0 0 0 0 0 2 ENE 2 0 0 0 0 0 2 E 2 0 0 0 0 0 2 ESE 4 0 0 0 0 0 4 SE 7 1 0 0 0 0 8 SSE 3 0 0 0 0 0 3 s 4 3 0 0 0 0 7 SSW 8 7 0 0 0 0 15 SW 18 17 0 0 0 0 35 WSW 15 26 0 0 0 0 41 w 21 14 0 0 0 0 35 WNW 19 10 0 0 0 0 29 NW 9 8 0 0 0 0 17 NNW 2 1 0 0 0 0 3 Variable 0 0 0 0 0 0 0 Total 121 90 0 0 0 0 211 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 5 81.*

Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-7 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, October -December, 2015 Oyster Creek Alpha Period of Record: October -December2015 Stability Glass -.Extremely Stable -1.50Ft-.33F.t .Oelta-T {F,) Wind's Measured' at 33' Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 6 0 0 0 0 0 6 NNE 1 0 0 0 0 0 1 NE 3 0 0 0 0 0 3 ENE 3 0 0 0 0 0 3 E 0 0 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE 3 0 0 0 0 0 3 s 6 0 0 0 0 0 6 SSW 14 2 0 0 0 0 16 SW 21 7 0 0 0 0 28 WSW 96 6 0 0 0 0 102 w 143 13 0 0 0 0 156 WNW 37 8 0 0 0 0 45 NW 54 11 0 0 0 0 65 NNW 12 6 0 0 0 0 18 Variable 0 0 0 0 0 0 0 Total 399 53 0 0 0 0 452 Hours of calm in this stability class: 13 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 5 82 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table 0-8 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, October -December, 2015 Oyster Creek Alpha Period of Record: October -December2015 Stability Class -Extremely Unstable -380Ft-33Ft Delta-T (F) Winds.Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 0 0 0 0 0 0 NNE 0 0 0 0 0 0 0 NE 0 0 0 0 0 0 0 ENE 0 0 0 0 0 0 0 E 0 0 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE 0 0 0 0 0 0 0 s 0 0 0 0 0 0 0 SSW 0 0 0 0 0 0 0 SW 0 0 0 0 0 0 0 WSW 0 0 0 0 0 0 0 w 0 0 0 0 0 0 0 WNW 0 0 0 0 0 0 0 NW 0 0 0 1 1 0 2 NNW 0 0 0 0 0 0 0 Variable 0 0 0 0 0 0 0 Total 0 0 0 1 1 0 2 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 5 83 Oyster Creek 2015 Annual Radioactive Effluent Release Report TableD-8 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, October -December, 2015 Oyster Creek Alpha Period of Record: October -December2015 Stability Class -Moderately Unstable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 0 0 2 0 0 2 NNE 0 0 0 1 0 0 1 NE 0 0 1 1 0 0 2 ENE 0 0 0 0 0 0 0 E 0 0 0 0 0 0 0 ESE 0 0 0 0 0 0 0 SE 0 0 0 0 0 0 0 SSE 0 0 0 0 0 0 0 s 0 0 0 0 0 0 0 SSW 0 0 0 1 0 0 1 SW 0 0 0 1 0 0 1 WSW 0 0 0 2 0 0 2 w 0 0 0 1 0 0 1 WNW 0 0 1 3 1 0 5 NW 0 0 0 4 2 0 6 NNW 0 0 0 1 0 0 1 Variable 0 0 0 0 0 0 0 Total 0 0 2 17 3 0 22 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 5 84 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-8 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, October -December, 2015 Oyster Creek Alpha Period of Record: October -December2015 Stability Class -Slightly Unstable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 0 0 0 0 0 0 NNE 0 0 1 4 0 0 5 NE 0 0 2 2 0 0 4 ENE 0 1 7 8 0 0 16 E 0 0 2 1 0 0 3 ESE 0 0 2 1 0 0 3 SE 0 0 0 0 0 0 0 SSE 0 0 2 1 0 0 3 s 0 0 0 1 0 0 1 SSW 0 0 2 3 2 0 7 SW 0 0 0 3 0 0 3 WSW 0 0 1 6 1 0 8 w 0 0 1 4 3 0 8 WNW 0 0 4 7 4 2 17 NW 0 1 2 7 4 1 15 NNW 0 0 3 2 1 0 6 Variable 0 0 0 0 0 0 0 Total 0 2 29 50 15 3 99 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 5 85 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-8 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, October -December, 2015 Oyster Creek Alpha Period of Record: October -December2015 Stability Class -Neutral -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 1 10 18 7 0 0 36 NNE 0 2 10 22 6 1 41 NE 3 3 2 23 29 58 118 ENE 1 3 14 13 20 11 62 E 1 7 14 12 11 19 64 ESE 1 7 12 18 7 7 52 SE 1 6 10 2 9 1 29 SSE 1 8 5 4 4 2 24 s 1 3 8 5 4 2 23 SSW 0 3 11 13 14 8 49 SW 0 3 14 15 18 1 51 WSW 0 6 21 22 7 0 56 w 0 4 18 10 9 2 43 WNW 0 12 17 24 18 10 81 NW 2 6 17 28 11 1 65 NNW 2 7 9 12 9 0 39 Variable 0 0 0 0 0 0 0 Total / 14 90 200 230 176 123 833 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 5 86 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-8 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, October -December, 2015 Oyster Creek Alpha Period of Record: October -December2015 Stability Class -Slightly Stable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 2 9 12 3 0 26 NNE 1 5 2 5 1 0 14 NE 0 4 6 6 3 1 20 ENE 1 3 6 6 2 0 18 E 0 2 3 6 3 1 15 ESE 2 4 8 8 2 0 24 SE 1 4 6 15 8 3 37 SSE 0 4 7 6 7 5 29 s 0 4 6 11 8 4 33 SSW 0 6 16 22 17 6 67 SW 1 0 13 30 23 8 75 WSW 0 2 10 10 30 4 56 w 0 3 9 30 40 1 83 WNW 1 1 3 26 22 0 53 NW 0 0 3 17 23 0 43 NNW 1 1 2 9 17 0 30 Variable 0 0 0 0 0 0 0 Total 8 45 109 219 209 33 623 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 5 87 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-8 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, October-December, 2015 Oyster Creek Alpha Period of Record: October -December2015 Stability Class -Moderately Stable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24 > 24 Total ---------N 0 0 1 6 7 1 15 NNE 0 0 2 3 4 0 9 NE 0 0 2 2 0 0 4 ENE 0 0 4 1 0 0 5 E 0 0 2 0 0 0 2 ESE 1 3 2 1 0 0 7 SE 2 0 3 0 0 0 5 SSE 0 1 7 1 0 0 9 s 0 1 4 3 0 0 8 SSW 0 0 5 11 7 1 24 SW 0 3 3 16 9 4 35 WSW 0 0 1 6 15 1 23 w 0 1 2 9 19 4 35 WNW 0 0 1 8 25 2 36 NW 0 1 3 8 11 3 26 NNW 0 0 2 7 15 0 24 Variable 0 0 0 0 0 0 0 Total 3 10 44 82 112 16 267 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 5 88 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-8 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, October -December, 2015 Oyster Creek Alpha Period of Record: October -December2015 Stability Class -Extremely Stable -380Ft-33Ft Delta-T (F) Winds Measured at S80 Feet Wind Speed (in mph) Wind Direction 1-3 4-7 8-12 13-18 19-24

> 24 Total ---------N 0 1 6 16 11 1 35 NNE 1 2 9 7 1 0 20 NE 1 0 1 3 1 0 6 ENE 0 1 8 3 0 0 12 E 0 0 9 4 0 0 13 ESE 0 1 5 0 0 0 6 SE 0 4 5 1 0 0 10 SSE 0 2 4 4 3 0 13 s 1 2 0 18 3 0 24 SSW 1 5 3 3 4 0 16 SW 1 3 5 4 13 1 27 WSW 2 9 6 8 3 3 31 w 2 7 3 17 8 5 42 WNW 1 12 1 5 14 5 38 NW 1 5 5 7 5 0 23 NNW 0 2 4 21 12 2 41 Variable 0 0 0 0 0 0 0 Total 11 56 74 121 78 17 357 Hours of calm in this stability class: 0 Hours of missing wind measurements in this stability class: 0 Hours of missing stability measurements in all stability classes: 5 89 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-9 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, January -December, 2015 Oyster Creek Alpha Period of Record: January -December 2015 Stability Class -All Stabilities

-150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Wind Speed (in m/s) Direction 0.5-1.1-1. 6-2.1-3.1-4.1-5.1-6.1-8.1-Sector <0.50 1 1. 5 2 3 4 5 6 8 10 >10.00 Total N 1 32 38 44 67 33 11 0 0 0 0 226 NNE 0 17 20 29 68 91 28 5 0 0 0 258 NE 0 27 26 34 137 172 91 34 16 0 0 537 ENE 1 21 34 29 102 141 72 26 1 0 0 427 E 1 16 21 19 67 37 26 10 15 0 0 212 ESE 0 13 12 22 86 65 10 3 3 0 0 214 SE 0 11 31 51 123 126 48 9 4 0 0 403 SSE 2 26 43 29 88 85 68 27 3 0 0 371 s 3 47 60 46 121 93 88 75 43 1 0 577 SSW 4 53 80 78 189 138 76 58 33 2 0 711 SW 3 78 112 114 195 96 38 13 1 0 0 650 WSW 4 142 222 184 194 63 30 10 2 0 0 851 w 11 277 245 135 158 78 42 17 4 0 0 967 WNW 4 132 158 105 168 115 123 58 35 1 0 899 NW 5 81 185 137 163 129 107 71 37 2 0 917 NNW 2 40 69 79 130 80 44 13 5 0 0 462 Tot 41 1013 1356 1135 2056 1542 902 429 202 6 0 8682 Hours of Calm . 64 Hours of Variable Direction 0 Hours of Valid Data . 8746 Hours of Missing Data 14 Hours in Period . 8760 90 Oyster Creek 2015 Annual Radioactive Effluent Release Report TableD-9 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, January -December, 2015 Oyster Creek Alpha Period of Record: January -December 2015 Stability Class -Extremely Unstable -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Wind Speed (in m/s) Direction 0.5-1.1-1. 6-2.1-3.1-4.1-5.1-6.1-8.1-Sector <0.50 1 1. 5 2 3 4 5 6 8 10 >10.00 Total N 0 0 0 0 6 10 5 0 0 0 0 21 NNE 0 0 0 1 7 8 7 0 0 0 0 23 NE 0 0 0 0 12 33 17 0 0 0 0 62 ENE 0 0 0 1 25 58 28 7 0 0 0 119 E 0 0 0 0 17 15 4 3 0 0 0 39 ESE 0 0 0 1 24 32 1 0 0 0 0 58 SE 0 0 0 2 14 76 29 4 3 0 0 128 SSE 0 0 0 0 8 21 42 17 1 0 0 89 s 0 0 0 1 6 17 31 52 33 1 0 141 SSW 0 0 0 0 6 22 13 9 7 0 0 57 SW 0 0 1 1 24 23 10 1 1 0 0 61 WSW 0 0 0 2 14 22 12 8 2 0 0 60 w 0 0 0 1 10 26 17 5 1 0 0 60 WNW 0 0 0 0 16 36 39 28 12 0 0 131 NW 0 0 0 1 24 41 55 28 18 2 0 169 NNW 0 0 0 0 9 18 9 3 3 0 0 42 Tot 0 0 1 11 222 458 319 165 81 3 0 1260 Hours of Calm 0 Hours of Variable Direction 0 Hours of Valid Data . 1260 Hours of Missing Data 14 Hours in Period . 8760 91 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-9 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, January -December, 2015 Oyster Creek Alpha Period of Record: January -December 2015 Stability Class -Moderately Unstable -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Wind Speed (in m/s) Direction 0.5-1.1-1. 6-2.1-3.1-4.1-5.1-6.1-8.1-Sector <0.50 1 1. 5 2 3 4 5 6 8 10 >10.00 Total N 0 0 0 2 13 1. 1 0 0 0 0 17 NNE 0 0 0 1 6 5 2 0 0 0 0 14 NE 0 0 0 4 11 16 3 0 0 0 0 34 ENE 0 0 1 1 12 13 6 2 0 0 0 35 E 0' 0 0 1 11 2 2 0 0 0 0 16 ESE 0 0 0 3 16 7 1 0 0 0 0 27 SE 0 0 0 6 12 18 4 1 0 0 0 41 SSE 0 0 3 0 4 18 6 0 0 0 0 31 s 0 0 0 1 4 10 14 4 3 0 0 36 SSW 0 1 1 3 6 7 5 4 1 1 0 29 SW 0 0 1 5 10 9 3 1 0 0 0 29 WSW 0 0 0 5 9 8 5 1 0 0 0 28 w 0 0 0 6 14 15 3 7 2 0 0 47 WNW 0 0 0 5 16 8 13 7 3 0 0 52 NW 0 0 1 4 19 10 13 5 5 0 0 57 NNW 0 0 0 4 21 9 2 2 0 0 0 38 Tot 0 1 7 51 184 156 83 34 14 1 0 531 Hours of Calm 0 Hours of Variable Direction 0 Hours of Valid Data . 531 Hours of Missing Data 14 Hours in Period . 8760 92 Oyster Creek 20'15 Annual Radioactive Effluent Release Report Table D-9 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, January -December, 2015 Oyster Creek Alpha Period of Record: January -December 2015 Stability Class -Slightly Unstable -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Wind Speed (in m/s) Direction 0.5-1.1-1. 6-2.1-3.1-4.1-5.1-6.1-8.1-Sector <0.50 1 1.5 2 3 4 5 6 8 10 >10.00 Total N 0 0 2 3 4 2 1 0 0 0 0 12 NNE 0 0 0 1 3 4 1 0 0 0 0 9 NE 0 0 0 1 5 7 5 1 0 0 0 19 ENE 0 0 0 2 10 2 1 2 0 0 0 17 E 0 0 0 3 4 0 1 0 0 0 0 8 ESE 0 0 0 4 9 2 0 0 0 0 0 15 SE 0 0 0 3 9 5 3 0 0 0 0 20 SSE 0 0 1 2 4 9 5 0 0 0 0 21 s 0 0 0 0 2 6 12 3 2 0 0 25 SSW 0 0 1 3 5 5 2 0 0 0 0 16 SW 0 0 0 1 6 6 1 0 0 0 0 14 WSW 0 0 1 2 11 5 3 0 0 0 0 22 w 0 0 0 3 9 6 7 1 1 0 0 27 WNW 0 0 2 3 10 4 6 5 7 0 0 37 NW 0 0 2 5 5 7 4 3 2 0 0 28 NNW 0 0 1 2 7 2 2 1 1 0 0 16 Tot 0 0 10 38 103 72 54 16 13 0 0 306 Hours of Calm 0 Hours of Variable Direction 0 Hours of Valid Data . 306 Hours of Missing Data 14 Hours in Period . 8760 93 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-9 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, January -December, 2015 Oyster Creek Alpha Period of Record: January-December 2015 Stability Class -Neutral -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Wind Speed (in m/s) Direction 0.5-1.1-1. 6-2.1-3.1-4.1-5.1-6.1-8.1-Sector <0.50 1 1. 5 2 3 4 5 6 8 10 >10.00 Total N 0 8 17 21 23 13 4 0 0 0 0 86 NNE 0 2 11 11 45 68 18 5 0 0 0 160 NE 0 10 8 17 61 93 59 32 15 0 0 295 ENE 0 3 14 12 41 46 23 12 1 0 0 152 E 0 3 6 9 21 16 15 6 14 0 0 90 ESE 0 1 3 7 23 15 6 3 3 0 0 61 SE 0 3 11 19 62 20 6 3 1 0 0 125 SSE 0 3 5 8 43 31 10 8 2 0 0 110 s 0 4 7 0 40 39 20 12 5 0 0 127 SSW 0 1 8 3 29 44 24 30 24 1 0 164 SW 0 2 3 12 39 30 18 10 0 0 0 114 WSW 0 3 9 15 37 17 9 1 0 0 0 91 w 0 5 9 9 39 17 14 4 0 0 0 97 WNW 0 10 16 18 44 32 30 17 13 1 0 181 NW 0 6 14 26 35 34 20 27 12 0 0 174 NNW 0 8 21 27 44 29 24 5 1 0 0 159 Tot 0 72 162 214 626 544 300 175 91 2 0 2186 Hours of Calm 0 Hours of Variable Direction 0 Hours of Valid Data . 2186 Hours of Missing Data 14 Hours in Period . 8760 94 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-9 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, January -December, 2015 Oyster Creek Alpha Period of Record: January -December 2015 Stability Class -Slightly Stable -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Wind Speed (in m/s) Direction 0.5-1.1-1. 6-2.1-3.1-4.1-5.1-6.1-8.1-Sector <0.50 1 1. 5 2 3 4 5 6 8 10 >10.00 Total N 0 10 5 10 19 7 0 0 0 0 0 51 NNE 0 6 6 11 6 6 0 0 0 0 0 35 NE 0 13 14 11 48 23 7 1 1 0 0 118 ENE 0 7 17 11 13 22 14 3 0 0 0 87 ,E 0 7 12 4 14 4 4 1 1 0 0 47 ESE 0 3 6 6 14 9 2 0 0 0 0 40 SE Q 3 14 2.0 2.5 7 6 1 Q Q Q 76 SSE 0 10 25 19 28 6 5 2 0 0 0 s 0 18 29 38 67 21 10 4 0 0 0 187 SSW 1 11 39 49 138 60 32 15 1 0 0 346 SW 0 20 36 49 102 28 6 1 0 0 0 242 WSW 0 11 32 65 103 11 1 0 0 0 0 223 w 0 20 22 57 70 14 1 0 0 0 0 184 WNW 0 7 26 33 71 34 35 1 0 0 0 207 NW 0 13 32 36 77 37 15 8 0 0 0 218 NNW 0 9 14 24 48 22 7 2 0 0 0 126 Tot 1 168 329 443 843 311 145 39 3 0 0 2282 Hours of Calm 9 Hours of Variable Direction 0 Hours of Valid Data . 2291 Hours of Missing Data 14 Hours in Period . 8760 95 Oyster Creek 2015 Annual Radioactive Effluent Release Report TableD-9 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, January -December, 2015 Oyster Creek Alpha Period of Record: January -December 2015 Stability Class -Moderately Stable -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Wind Speed (in m/s) Direction 0.5-1.1-1. 6-2.1-3.1-4.1-5.1-6.1-8.1-Sector <0.50 1 1. 5 2 3 4 5 6 8 10 >10.00 Total N 0 3 6 7 2 0 0 0 0 0 0 18 NNE 0 7 3 4 1 0 0 0 0 o* 0 15 NE 0 2 2 1 0 0 0 0 0 0 0 5 ENE 0 6 1 1 1 0 0 0 0 0 0 9 E 1 4 3 2 0 0 0 0 0 0 0 10 ESE 0 7 3 0 0 0 0 0 0 0 0 10 SE 0 5 6 1 1 0 0 0 0 0 0 13 SSE 1 6 7 0 1 0 0 0 0 0 0 15 s 0 12 20 6 2 0 1 0 0 0 0 41 SSW 0 20 22 16 4 0 0 0 0 0 0 62 SW 0 19 37 30 14 0 0 0 0 0 0 100 WSW 0 16 45 58 20 0 0 0 0 0 0 139 w 1 25 42 24 14 0 0 0 0 0 0 106 WNW 1 20 38 27 11 1 0 0 0 0 0 98 NW 1 14 39 34 3 0 0 0 0 0 0 91 NNW 1 5 13 10 0 0 0 0 0 0 0 29 Tot 6 171 287 221 74 1 1 0 0 0 0 761 Hours of Calm 9 Hours of Variable Direction 0 Hours of Valid Data . 770 Hours of Missing Data 14 Hours in Period . 8760 96 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-9 Wind Speed by Direction Measured at 33 Feet for various Stability Classes for the Oyster Creek Generating Station, January -December, 2015 Oyster Creek Alpha Period of Record: January -December 2015 Stability Class -Extremely Stable -150Ft-33Ft Delta-T (F) Winds Measured at 33 Feet Wind Wind Speed (in m/s) Direction 0.5-1.1-1. 6-2.1-3.1-4.1-5.1-6.1-8.1-*Sector <0.50 1 1. 5 2 3 4 5 6 8 10 >10.00 Total N 1 11 8 1 0 0 0 0 0 0 0 21 NNE 0 2 0 0 0 0 0 0 0 0 0 2 NE 0 2 2 0 0 0 0 0 0 0 0 4 ENE 1 5 1 1 0 0 0 0 0 0 0 8 E 0 2 0 0 0 0 0 0 0 0 0 2 ESE 0 2 0 1 0 0 0 0 0 0 0 3 SE 0 0 0 0 0 0 0 0 0 0 0 0 SSE 1 7 2 0 0 0 0 0 0 0 0 10 s 3 13 4 0 0 0 0 0 0 0 0 20 SSW 3 20 9 4 1 0 0 0 0 0 0 37 SW 3 37 34 16 0 0 0 0 0 0 0 90 WSW 4 112 135 37 0 0 0 0 0 0 0 288 w 10 227 172 35 2 0 0 0 0 0 0 446 WNW 3 95 76 19 0 0 0 0 0 0 0 193 NW 4 48 97 31 0 0 0 0 0 0 0 180 NNW 1 18 20 12 1 0 0 0 0 0 0 52 Tot 34 601 560 157 4 0 0 0 0 0 0 1356 Hours of Calm 46 Hours of Variable Direction 0 Hours of Valid Data . 1402 Hours of Missing Data 14 Hours in Period . 8760 97 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D -10 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, January -December, 2015 Oyster Creek Alpha Period of Record: January -December 2015 Stability Class -All Stabilities

-380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Wind Speed (in m/s) Direction 0.5-1.1-1. 6-2.1-3.1-4.1-5.1-6.1-8.1-Sector <0.50 1 1. 5 2 3 4 5 6 8 10 >10.00 Total N 0 2 3 7 28 39 S2 74 128 36 10 379 NNE 0 1 3 7 2S 39 49 S2 110 32 6 324 NE 0 6 6 6 33 S4 61 86 166 111 103 632 ENE 0 2 7 11 26 40 60 64 91 79 6S 44S E 0 2 s 7 24 46 33 32 3S 32 36 2S2 ESE 0 3 4 13 29 SS 39 2S 36 12 lS 231 SE 0 0 8 8 31 53 82 55 47 21 lS 320 SSE 0 2 3 10 33 S2 66 104 76 20 lS 381 s 1 3 s 11 28 so 66 109 188 73 2S SS9 SSW 0 2 4 6 27 so 71 131 268 1S6 134 849 SW 0 1 8 7 28 47 Sl 86 240 197 90 7SS WSW 0 1 2 9 26 S7 S9 79 161 14S 94 633 w 0 4 6 10 40 4S 48 114 166 178 91 702 WNW 0 3 3 17 33 S9 6S 76 216 19S 183 8SO NW 0 2 s 12 31 S4 S4 90 194 218 1S7 817 NNW 0 1 4 8 18 4S 47 4S lSS 160 S9 S42 Tot 1 3S 76 149 460 78S 903 1222 2277 166S 1098 8671 Hours of Calm . 2 Hours of Variable Direction 0 Hours of Valid Data . 8673 Hours of Missing Data 87 Hours in Period . 8760 98 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-10 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, January -December, 2015 Oyster Creek Alpha Period of Record: January -December 2015 Stability Class -Extremely Unstable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Wind Speed (in m/s) Direction 0.5-1.1-1. 6-2.1-3.1-4.1-5.1-6.1-8.1-Sector <0.50 1 1.5 2 3 4 5 6 8 10 >10.00 Total N 0 0 0 0 0 0 1 0 0 0 0 1 NNE 0 0 0 0 0 0 1 0 0 1 0 2 NE 0 0 0 0 0 0 0 2 3 2 0 7 ENE 0 0 0 0 0 1 1 5 7 1 0 15 E 0 0 0 0 0 0 0 3 0 2 0 5 ESE 0 0 0 0 0 0 2 0 0 0 0 2 SE 0 0 0 0 0 0 1 0 0 0 0 1 SSE 0 0 0 0 1 1 0 1 1 1 0 5 s 0 0 0 0 0 0 1 1 7 9 3 21 SSW 0 0 0 0 0 0 0 0 1 7 5 13 SW 0 0 0 0 0 0 0 0 3 1 0 4 WSW 0 0 0 0 0 0 0 1 0 0 6 7 w 0 0 0 0 0 0 0 2 3 5 2 12 WNW 0 0 0 0 0 0 0 2 5 0 4 11 NW 0 0 0 0 0 0 0 1 12 14 12 39 NNW 0 0 0 0 0 0 0 0 1 0 2 3 Tot 0 0 0 0 1 2 7 18 43 43 34 148 Hours of Calm 0 Hours of Variable Direction 0 Hours of Valid Data 148 Hours of Missing Data 87 Hours in Period . 8760 99 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-10 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, January -December, 2015 Oyster Creek Alpha Period of Record: January -December 2015 Stability Class -Moderately Unstable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Wind Speed (in m/s) Direction 0.5-1.1-1. 6-2.1-3.1-4.1-5.1-6.1-8.1-Sector <0.50 1 1. 5 2 3 4 5 6 8 10 >10.00 Total N 0 0 0 0 0 0 1 1 7 1 0 10 NNE 0 0 0 0 0 0 1 1 2 1 0 5 NE 0 0 0 0 0 1 1 10 12 2 0 26 ENE 0 0 0 0 0 0 2 11 12 5 1 31 E 0 0 0 0 0 1 5 2 2 2 0 12 ESE 0 0 0 1 0 3 6 3 0 0 0 13 SE 0 0 0 0 0 2 7 9 1 4 0 23 SSE 0 0 0 0 0 1 2 9 9 0 0 21 s 0 0 0 0 0 1 3 9 23 13 3 52 SSW 0 0 0 0 0 1 1 1 9 2 7 21 SW 0 0 1 0 0 1 1 6 6 1 0 16 WSW 0 0 0 0 0 0 2 3 11 2 1 19 w 0 0 0 0 0 2 0 3 10 2 2 19 WNW 0 0 0 0 0 0 0 4 15 13 13 45 NW 0 0 0 0 0 0 5 5 15 13 12 50 NNW 0 0 0 0 0 0 2 5 6 0 1 14 Tot 0 0 1 1 0 13 39 82 140 61 40 377 Hours of Calm 0 Hours of Variable Direction 0 Hours of Valid Data . 377 Hours of Missing Data 87 Hours in Period . 8760 100 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-10 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, January -December, 2015 Oyster Creek Alpha Period of Record: January -December 2015 Stability Class -Slightly Unstable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Wind Speed (in m/s) Direction 0.5-1.1-1. 6-2.1-3.1-4.1-5.1-6.1-Sector <0.50 1 1. 5 2 3 4 5 6 8 . 10 >10.00 Total N 0 0 0 0 2 0 4 3 4 0 0 13 NNE 0 0 0 0 1 4 3 2 3 4 0 17 NE 0 0 0 0 1 6 7 10 14 7 0 45 ENE 0 0 0 0 3 9 10 12 12 4 4 54 E 0 0 0 0 1 10 8 0 3 0 0 22 ESE 0 0 0 0 4 9 5 1 1 0 0 20 SE 0 0 0 0 3 6 2.7 8 0 2. 0 46 SSE 0 0 0 0 0 2 15 25 18 2 0 62 s 0 0 0 0 1 0 5 8 13 9 1 37 SSW 0 0 0 0 0 4 5 8 15 10 6 48 SW 0 0 0 0 0 6 4 2 9 0 0 21 WSW 0 0 0 0 2 10 3 9 12 4 3 43 w 0 0 0 0 3 2 3 9 7 6 8 38 WNW 0 0 0 0 2 7 6 11 20 17 25 88 NW 0 0 0 0 2 7 10 12 8 18 12 69 NNW 0 0 0 0 0 4 6 4 7 1 3 25 Tot 0 0 0 0 25 86 121 124 146 84 62 648 Hours of Calm 0 Hours of Variable Direction 0 Hours of Valid Data . 648 Hours of Missing Data 87 Hours in Period . 8760 101 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D -10 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, January -December, 2015 Oyster Creek Alpha Period of Record: January -December 2015 Stability Class -Neutral -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Wind Speed (in m/s) Direction o*.5-1.1-1. 6-2.1-3.1-4.1-5.1-6.1-8.1-Sector <0.50 I 1. 5 2 3 4 5 6 8 10 >10.00 Total N 0 2 1 6 18 21 21 20 24 7 0 120 NNE 0 1 0 4 11 11 22 24 73 16 6 168 NE 0 3 3 2 20 28 28 42 113 85 99 423 ENE 0 2 3 6 15 18 26 19 38* 57 55 239 E 0 1 4 4 14 19 11 14 19 20 34 140 ESE 0 1 2 8 13 30 10 13 25 6 14 122 SE 0 0 3 3 17 34 32 27 21 7 5 149* SSE 0 1 1 5 21 27 32 40 28 4 4 163 s 0 0 3 8 11 24 31 42 52 18 7 196 SSW 0 2 3 2 11 8 30 38 79 55 70 298 SW 0 1 1 5 9 17 16 26 61 43 12 191 WSW 0 0 0 1 15 19 26 24 41 26 7 159 w 0 2 3 7 19 20 25 43 42 27 18 206 WNW 0 0 0 6 14 30 35 29 53 47 87 301 NW 0 1 2 6 16 23 18 26 63 55 76 286 NNW 0 1 3 5 9 31 21 16 46 34 30 196 Tot 0 18 32 78 233 360 384 443 778 507 524 3357 Hours of Calm 0 Hours of Variable Direction 0 Hours of Valid Data . 3357 Hours of Missing Data 87 Hours in Period . 8760 102 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-10 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, January -December, 2015 Oyster Creek Alpha Period of Record: January -December 2015 Stability Class -Slightly Stable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Wind Speed (in rn/s) Direction 0.5-1.1-1. 6-2.1-3.1-4.1-5.1-6.1-8.1-Sector <0.50 1 1. 5 2 3 4 5 6 8 10 >10.00 Total N 0 0 0 1 4 12 16 17 27 4 0 81 NNE 0 0 1 1 7 9 4 9 11 3 0 45 NE 0 0 1 4 6 10 14 10 17 12 3 77 ENE 0 0 4 5 5 4 12 7 15 11 5 68 E 0 0 0 2 6 7 3 8 8 8 2 44 ESE 0 2 1 3 6 9 9 5 10 6 1 52 SE 0 0 2 2 5 6 6 8 23 8 10 70 SSE 0 1 1 4 7 10 10 16 15 10 11 85 s 1 1 1 2 11 17 10 36 62 17 10 168 SSW 0 0 0 2 6 21 21 60 122 61 37 330 SW 0 0 2 1 7 10 18 28 100 101 44 311 WSW 0 0 1 0 4 7 11 22 60 61 27 193 w 0 1 0 1 6 8 7 30 58 80 17 208 WNW 0 3 0 0 4 7 13 12 65 58 20 182 NW 0 1 0 1 3 3 8 25 58 66 23 188 NNW 0 0 1 2 2 4 3 6 35 54 2 109 Tot 1 9 15 31 89 144 165 299 686 560 212 2211 Hours of Calm 1 Hours of Variable Direction 0 Hours of Valid Data . 2212 Hours of Missing Data 87 Hours in Period . 8760 103 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D -10 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, January -December, 2015 Oyster Creek Alpha Period of Record: January -December 2015 Stability Class -Moderately Stable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Wind Speed (in m/s) Direction 0.5-1.1-1. 6-2.1-3.1-4.1-5.1-6.1-8.1-Sector <0.50 1 1. 5 2 3 4 5 6 8 10 >10.00 Total N 0 0 1 0 2 3 2 6 32 12 4 62 NNE 0 0 1 2 1 5 6 7 9 6 0 37 NE 0 1 1 0 3 6 5 3 4 0 0 23 ENE 0 0 0 0 2 5 2 4 2 0 0 15 E 0 1 0 1 1 4 0 0 2 0 0 9 ESE 0 0 1 1 4 3 1 2 0 0 0 12 SE 0 0 3 3 2 2 6 1 1 0 0 18 SSE 0 0 1 0 2 8 4 7 0 0 0 22 s 0 1 1 1 4 4 11 5 7 1 0 35 SSW 0 0 0 1 2 7 7 14 26 18 4 79 SW 0 0 2 1 6 6 4 10 38 35 21 123 WSW 0 0 1 1 0 8 7 14 21 40 32 124 w 0 0 0 0 2 4 5 13 20 37 30 111 WNW 0 0 0 1 1 6 6 9 22 40 20 105 NW 0 0 1 3 3 4 3 3 21 36 17 91 NNW 0 0 0 0 3 4 4 4 32 50 13 110 Tot 0 3 13 15 38 79 73 102 237 275 141 976 Hours of Calm 0 Hours of Variable Direction 0 Hours of Valid Data . 976 Hours of Missing Data 87 Hours in Period . 8760 104 Oyster Creek 2015 Annual Radioactive Effluent Release Report Table D-10 Wind Speed by Direction Measured at 380 Feet for various Stability Classes for the Oyster Creek Generating Station, January -December, 2015 Oyster Creek Alpha Period of Record: January -December 2015 Stability Class -Extremely Stable -380Ft-33Ft Delta-T (F) Winds Measured at 380 Feet Wind Wind Speed (in m/s) Direction 0.5-1.1-1. 6-2.1-3.1-4.1-5.1-6.1-8.1-Sector <0.50 1 1. 5 2 3 4 5 6 8 10 >10.00 Total N 0 0 1 0 2 3 7 27 34 12 6 92 NNE 0 0 1 0 5 10 12 9 12 1 0 50 NE 0 2 1 0 3 3 6 9 3 3 1 31 ENE 0 0 0 0 1 3 7 6 5 1 0 23 E 0 0 1 0 2 5 6 5 1 0 0 20 ESE 0 0 0 0 2 1 6 1 0 0 0 10 SE 0 0 0 0 4 3 3 2 1 0 0 13 SSE 0 0 0 1 2 3 3 6 5 3 0 23 s 0 1 0 0 1 4 5 8 24 6 1 50 SSW 0 0 1 1 8 9 7 10 16 3 5 60 SW 0 0 2 0 6 7 8 14 23 16 13 . 89 WSW 0 1 0 7 5 13 10 6 16 12 18 88 w 0 1 3 2 10 9 8 14 26 21 14 108 WNW 0 0 3 10 12 9 5 9 36 20 14 118 NW 0 0 2 2 7 17 10 18 17 16 5 94 NNW 0 0 0 1 4 2 11 10 28 21 8 85 Tot 0 5 15 24 74 101 114 154 247 135 85 954 Hours of Calm . 1 Hours of Variable Direction 0 Hours of Valid Data . 955 Hours of Missing Data 87 Hours in Period . 8760 105 Oyster Creek 2015 Annual Radioactive Effluent Release Report Appendix E ODCM Revisions See attached copy of CY-OC-170-301 Revision 7 106 Oyster Creek 2015 Annual Radioactive Effluent Release Report Appendix F ERRATA None 107 Exelon Generation OFFSITE DOSE CALCULATION MANUAL FOR CY-OC-170-301 Revision 7 Page 1of140 OYSTER CREEK GENERATING STATION Revision of this document requires PORC approval and changes are controlled by CY-AA-170-3100 102015 CY-OC-170-301 Revision 7 Page 2 of 140 TABLE OF CONTENTS INTRODUCTION PART 1 -RADIOLOGICAL EFFLUENT CONTROLS 1.0 DEFINITIONS 3/4 CONTROLS AND SURVEILLANCE REQUIREMENTS 3/4.0 APPLICABILITY 3/4.3 INSTRUMENTATION 3/4.3.3.10 3/4.3.3.11 RADIOACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTATION RADIOACTIVE GASEOUS EFFLUENT MONTIORING INSTRUMENTATION 3/4.11 RADIOACTIVE EFFLUENTS 3/4.11.1 3/4.11.1.1 3/4.11.1.2 3/4.11.1.3 3/4.11.2 3/4, 11.2.1 3/4.11.2.2 3/4.11.2.3 3/4.11.2.4 3/4.11.3 3/4.11.4 3/4.12 3/4.12.1 3/4.12.2 3/4.12.3 3/4.12.4 LIQUID EFFLUENTS CONCENTRATION DOSE UQUIDWASTE TREATMENT SYSTEM GASEOUS EFFLUENTS DOSE RATE DOSE -NOBLE GASES DOSE -IODINE-131, IODINE-133, TRITIUM, AND RADIONUCLIDES IN PARTICULATE FORM GASEOUS RADWASTE TREATMENT SYSTEM MARK I CONTAINMENT TOTAL DOSE RADIOLOGICAL ENVIRONMENTAL MONITORING MONITORING PROGRAM LAND USE CENSUS INTERLABORA TORY COMPARISON PROGRAM METEOROLOGICAL MONITORING PROGRAM 102015 CY-OC-170-301 Revision 7 Page 3 of 140 BASES FOR SECTIONS 3.0 AND 4.0 3/4.3 INSTRUMENTATION 3/4.3.3.10 3/4.3.3.11 RADIOACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTATION RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION 3/4.11 RADIOACTIVE EFFLUENTS 3/4.11.1 3/4.11.1.1 3/4.11.1.2 3/4.11.1.3 3/4.11.2 3/4.11.2.1 3/4.11.2.2 3/4.11.2.3 3/4.11.2.4 3/4.11.3 3/4.11.4 LIQUID EFFLUENTS CONCENTRATION DOSE LIQUID RADWASTETREATMENT GASEOUS EFFLUENTS DOSE RATES DOSE -NOBLE GAS DOSE -IODINE-131, IODINE-133, TRITIUM, AND RADIONUCLIDES IN PARTICULATE FORM GASEOUS RADWASTE TREATMENT SYSTEM MARK I CONTAINMENT TOTAL DOSE 3/4.12 RADIOLOGICAL ENVIRONMENTAL MONITORING 3/4.12.1 3/4.12.2 3/4.12.3 MONITORING PROGRAM LAND USE CENSUS INTERLABORA TORY COMPARISON PROGRAM 5.0 DESIGN FEATURES I SITE MAP 6.0 ADMINISTRATIVE CONTROLS 6.1 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT (AREOR) 6.2 6.3 ANNUAL RADIOACTIVE EFFLUENT RELEASE REPORT (ARERR) RESPONSIBILITES 102015 CY-OC-170-301 Revision 7 Page 4 of 140 PART II -CALCULATIONAL METHODOLOGIES

1.0 LIQUID

EFFLEUNTS

1.1 RADIATION

MONITORING INSTRUMENTATION AND CONTROLS 1.2 LIQUID EFFLUENT MONITOR SETPOINT DETERMINATION

1.2.1 LIQUID

EFFLUENT MONITORS 1.2.2 SAMPLE RESULT SET POINTS 1.2.3 ASSUMED DISTRIBUTION SET POINTS 1.3 BATCH RELEASES 1.4 CONTINUOUS RELEASES 1.5 LIQUID EFFLUENT DOSE CALCULATION-10 CFR 50 1.5.1 MEMBER OF THE PUBLIC DOSE -LIQUID EFFLUENTS

1.5.2 SHORELINE

DEPOSIT DOSE 1.5.3 SHORELINE DOSE EXAMPLE 1 1.5.3.1 SHORELINE DOSE EXAMPLE 2 1.5.4 INGESTION DOSE -LIQUID 1.5.5 INGESTION DOSE CALCULATION EXAMPLE 1 1.5.5.1 INGESTION DOSE CALCULATION EXAMPLE 2 1.5.6 PROJECTED DOSE -LIQUID

1.6 REPRESENTATIVE SAMPLES 2 GASEOUS EFFLUENTS

2.1 RADIATION

MONITORING INSTRUMENTATION AND CONTROLS 2.2. GASEOUS EFFLUENT MONITOR SET POINT DETERMINATION

2.2.1 PLANT

VENT 2.2.2 OTHER RELEASE POINTS 2.2.3 RADIONUCLIDE MIX FOR SET POINTS 2.3 GASEOUS EFFLUENT INSTANTANEOUS DOSE RATE CALCULATIONS 10 CFR 20 2.3.1 2.3.1.1 2.3.1.2 2.3.1.3 SITE BOUNDARY DOSE RATE-NOBLE GASES TOTAL BODY DOSE RA TE EXAMPLE TOTAL BODY DOSE RATE SKIN.DOSE RATE 102015 2.3.1.4 2.3.2 2.3.2.1 2.3.2.2 EXAMPLE SKIN DOSE RATE CY-OC-170-301 Revision 7 Page 5 of 140 SITE BOUNDARY DOSE RATE -RADIOIODINE AND PARTICULATES METHOD -SITE BOUNDARY DOSE RA RADIOIODINE AND PARTICULATES EXAMPLE IODINE AND PARTICULATES DOSE RATE CALCULATION

2.4 NOBLE

GAS EFFLUENT DOSE CALCULATION

-10 CFR 50 2.4.1 2.4.1.1 2.4.1.2 2.4.1.3 UNRESTRICTED AREA DOSE -NOBLE GASES AIR DOSE METHOD EXAMPLE NOBLE GAS AIR DOSE CALCULATION INDIVIDUAL PLUME DOSE METHOD 2.5 RADIOIODINE PARTICULATE AND OTHER RADIONUCLIDES DOSE CALCULATIONS

-10 CFR 50 2.5.1 2.5.2 2.5.3 2.5.3.1 2.5.3.2 2.5.3.3 2.5.3.4 2.5.3.5 2.5.3.6 2.5.3.7 2.5.3.8 2.5.4 INHALATION OF RADIOIODINES, TRITIUM, PARTICULATES.AND OTHER RADIONUCLIDES EXAMPLE CALCULATION

-INHALATION OJ= RADIOIODINES, TRITIUM, PARTICULATES, AND OTHER RADIONUCLIDES INGESTION OF RADIOIODINES, PARTICULATES AND OTHER RADIONUCLIDES CONCENTRATION OF THE RADIONUCLIDE IN ANIMAL FORAGE AND VEGETATION

-OTHER THAN TRITIUM EXAMPLE CALCULATION OF CONCENTRATION OF THE RADIONUCLIDE IN ANIMAL FORAGE AND VEGETATION

-OTHER THAN TRITIUM CONCENTRATION OF TRITIUM IN ANIMAL FORAGE AND VEGETATION EXAMPLE CALCULATION OF CONCENTRATION OF TRITIUM IN ANIMAL FORAGE AND VEGETATION CONCENTRATION OF THE RADIONUCLIDE IN MILK AND MEAT EXAMPLE CALCULATION OF CONCENTRATION OF THE RADIONUCLIDE IN MILK AND MEAT DOSE FROM CONSUMPTION OF MILK, MEAT, AND VEGETABLES EXAMPLE CALCULATION

-DOSE FROM CONSUMPTION OF MILK, MEAT, AND VEGETABLES GROUND PLANE DEPOSITION IRRADIATION 102015 CY-OC-170-301 Revision 7 Page 6 of 140 GROUND PLANE CONCENTRATION 2.5.4.1 2.5.4.2 2.5.4.3 2.5.4.4 EXAMPLE GROUND PLANE CONCENTRATION CALCULATION GROUND PLANE DOSE EXAMPLE GROUND PLANE DOSE 2.6 PROJECTED DOSES -GASEOUS 3 TOTAL DOSE TO MEMBERS OF THE PUBLIC-40 CFR 190 3.1 EFFLUENT DOSE CALCULATIONS

3.2 DIRECT

EXPOSURE DOSE DETERMINATION

4.0 RADIOLOGICAL

ENVIRONMENTAL MONITORING PROGRAM APPRENDIX A -DERIVED DOSE FACTORS AND RECEPTOR LOCATIONS Table A-1: Table A-2: TableA-3:

Table A-4: TableA-5:

Dose Conversion Factors for Deriving Radioactive Noble Gas Radionuclide-To-Dose Equivalent Rate Factors Noble Gas Radionuclide-To-Dose Equivalent Rate Factors Air Dose Conversion Factors for Effluent Noble Gas Locations Associated with Maximum Exposure of a Member of lhe Public Critical Receptor Noble Gas Dose Conversion Factors APPENDIX B -MODELING PARAMETERS Table 8-1: Table B-2: OCGS Usage Factors for Individual Dose Assessment Monthly Average Absolute Humidity g/m 3 APPENDIX C -REFERENCES Table C-1: REFERENCES APPENDIX D -SYSTEM DRAWINGS Figure D-1-1a: Figure D-1-1 b: Figure D-1-1 c: Figure D-1-2: Figure D-2-1 : Figure D-2-2: Figure D-2-3: Liquid Radwaste Treatment Chem Waste and Floor Drain System Liquid Radwaste Treatment

-High Purity and Equipment Drain System Groundwater Remediation System Solid Radwaste Processing System Gaseous Radwaste Treatment

-Augmented Offgas System Ventilation System AOG Ventilation System 102015 CY-OC-170-301 Revision 7 Page 7 of 140 APPENDIX E -RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM -SAMPLE TYPE AND LOCATION Table E-1: Figure E-1: Figure E-2: Figure E-3: Figure E-4: REMP Sample Locations Oyster Creek Generating Station REMP Sample Locations within a 1 Mile Radius Oyster Creek Generating Station REMP Sample Locations within a 1 to 5 Mile Radius Oyster Creek Generating Station REMP Sample Locations over a 5 Mile Radius Area Plot Plan of Site 102015 INTRODUCTION OYSTER CREEK GENERATING STATION OFF SITE DOSE CALCULATION MANUAL CY-OC-170-301 Revision 7 Page 8 of 140 The Oyster Creek Off Site Dose Calculation Manual (ODCM) is an implementing document to the Oyster Creek Technical Specifications.

The previous Limiting Conditions for Operations that were contained in the Radiological Effluent Technical Specifications (RETS) are now included in the ODCM as Radiological Effluent Controls (REC). The ODCM contains two parts: Part I -Radiological Effluent Controls, and Part II -Calculational Methodologies.

Part I includes the following:

The Radiological Effluent Controls and the Radiological Environmental Monitoring Programs required by Technical Specifications 6.8.4

Descriptions of the information that should be included in the Annual Radioactive Effluent Release Report and the Annual Radiological Environmental Operating Report required by Technical Specifications 6.9.1.d and 6.9.1.e, Part II describes methodologies and parameters used for:

The calculation of radioactive liquid and gaseous effluent monitoring instrumentation alarm/trip set points; and

The calculation of radioactive liquid and gaseous concentrations, dose rates, cumulative yearly doses, and projected doses. Part II also contains a list and graphical description of the specific sample locations for the radiological environmental monitoring program (REMP), and the liquid and gaseous waste treatment systems and discharge points. 102015 PART I -RADIOLOGICAL EFFLUENT CONTROLS 1.0 DEFINITIONS CY-OC-170-301 Revision 7 Page 9 of 140 The following terms are defined so that uniform interpretation of these CONTROLS may be achieved.

The defined terms appear in capitalized type and are applicable throughout these CONTROLS.

1.1 OPERABLE

-OPERABILITY A system, subsystem, train, component or device shall be OPERABLE or have OPERABILITY when it is capable of performing its specified function(s).

Implicit in the definition shall be the assumption that all necessary attendant instrumentation, controls, normal and emergency electrical power sources,

cooling or seal water, lubrication or other auxiliary equipment that are required for the system, subsystem, train, component or device to perform its function(s) are also capable of performing their related support function(s).

A verification of OPERABILITY is an administrative check, by examination of appropriate plant records (logs, surveillance test records) to determine that a system, subsystem, train, component or device is not inoperable.

Such verification does not preclude the demonstration (testing) of a given system, subsystem, train, component or device to determine OPERABILITY.

1.2 ACTION

ACTION shall be that part of a CONTROL that prescribes remedial measures required under designated conditions.

1.3 CHANNEL

CALIBRATION A CHANNEL CALIBRATION shall be the adjustment, as necessary, of the channel output such that it responds, with acceptable range and accuracy, to known values of the parameter that the channel monitors.

The CHANNEL CALIBRATION shall encompass the entire channel, including equipment actuation, alarm, or trip. 1.4 CHANNEL CHECK A CHANNEL CHECK shall be a qualitative determination of acceptable operability by observation of channel behavior during operation.

This determination shall include, where possible, comparison of the channel with other independent channels measuring the same variable.

102015

1.5 CHANNEL

FUNCTIONAL TEST CY-OC-170-301 Revision 7 Page 10 of 140 CHANNEL FUNCTIONAL TEST shall be the injection of a simulated signal into the channel to verify its proper response including, where applicable, alarm and/or trip initiating actions. 1.6 CONTROL The Limiting Conditions for Operation (LCOs) that were contained in the Radiological Effluent Technical Specifications were transferred to the OFF SITE DOSE CALCULATION MANUAL (ODCM) and were renamed CONTROLS.

This is to distinguish between those LCOs that were retained in the Technical Specifications and those LCOs or CONTROLS that were transferred to the ODCM. 1.7 FREQUENCY NOTATION The FREQUENCY NOTATION specified for the performance of Surveillance Requirements shall correspond to the intervals defined in Table 1.1. 1.8 REPORTABLE EVENT A REPORABLE EVENT shall be any of those conditions specified Section 50. 73 to 1 OCFR Part 50. 1.9 SOURCE CHECK SOURCE CHECK shall be the qualitative assessment of channel response when the channel sensor is exposed to a source of increased radioactivity.

1.10 AUGMENTED OFF GAS SYSTEM (AOG) The AUGMENTED OFF GAS SYSTEM is designed and installed to holdup and/or process radioactive gases from the main condenser off gas system for the purpose of reducing the radioactive material content of the gases before release to the environs.

1.11 MEMBER (S) OF THE PUBLIC MEMBER (S) OF THE PUBLIC shall include all persons who are not occupationally associated with Exelon Generation and who do not normally frequent the Oyster Creek Generating Station site. This category does not include employees of the utility, its contractors, contractor employees, vendors, or persons who enter the site to make deliveries, to service equipment, work on site or for other purposes associated with plant functions.

This category does include persons who use portions of the site for recreational, occupational, or other 102015 CY-OC-170-301 Revision 7 Page 11 of 140 purposes not associated with the plant. An individual is not a member of the public during any period in which the individual receives an occupational dose. 1.12 OFF SITE DOSE CALCULATION MANUAL (ODCM) The OFF SITE DOSE CALCULATION MANUAL (ODCM) shall contain the methodology and parameters used in the calculation of Off Site doses due to radioactive gaseous and liquid effluents, in the calculation of gaseous and liquid effluent monitoring Alarm/Trip Set points, and in the conduct of the Radiological Environmental Monitoring Program. The ODCM shall also contain (1) the Radioactive Effluent Controls and Radiological Environmental Monitoring Programs required by Technical Specification Section 6.8.4 and (2) descriptions of the information that should be included in the Annual Radioactive Effluent Release Report AND Annual Radiological Environmental Operating Report required by Technical Specification Sections 6.9.1.d and 6.9.1.e, respectively.

1.13 PURGE -PURGING PURGE or PURGING shall be the controlled process of discharging air or gas from a confinement and replacing it with air or gas. 1.14 SITE BOUNDARY The SITE BOUNDARY shall be the perimeter line around OCGS beyond which the land is neither owned, leased, nor otherwise subject to control by Exelon Generation.

The area outside the SITE BOUNDARY is termed OFF SITE or UNRESTRICTED AREA. 1.15 OFF SITE The area that is beyond the site boundary where the land is neither owned, leased nor otherwise subject to control by Exelon Generation.

Can be interchanged with UNRESTRICTED AREA. 1.16 UNRESTRICTED AREA An UNRESTRICTED AREA shall be any area at or beyond the SITE BOUNDARY, access to which is not controlled by the licensee for purposes of protection of individuals from exposure to radiation and radioactive materials, or any area within the SITE BOUNDARY used for residential quarters or for industrial, commercial, institutional, and/or recreational purposes.

Can be interchanged with OFF SITE. 102015 1.17 DOSE EQUIVALENT 1-131 CY-OC-170-301 Revision 7 Page 12 of 140 DOSE EQUIVALENT 1-131 shall be that concentration of 1-131 (micro curies per gram), which alone would produce the same thyroid dose as the quantity and isotopic mixture of 1-131, 1-132, 1-133, 1-134, and 1-135 actually present. The thyroid dose conversion factors used for this calculation shall be those listed in Table E-7 of Regulatory Guide 1.109, "Calculation of Annual Doses to Man from Routine Releases of Reactor Effluences for the Purpose of Evaluating Compliance with 10CFR Part 40 Appendix I." 1.18 DEPOSITION

{D/Q) The direct removal of gaseous and particulate species on land or water surfaces.

DEPOSITION is expressed as a quantity of material per unit area (e.g. m-2). 1.19 DOSE CONVERSION FACTOR (DCF) A parameter calculated by the methods of internal dosimetry, which indicates the committed dose equivalent (to the whole body or organ) per unit activity inhaled or ingested.

This parameter is specific to the isotope and the dose pathway. DOSE CONVERSION FACTORS are commonly tabulated in units of mrem/hr per picocurie/m 3 in air or water. They can be found in Reg Guide 1.109 appendices.

1.20 EFFLUENT CONCENTRATION (EC) The liquid and air concentration levels which, if inhaled or ingested continuously over the course of a year, would produce a total effective dose equivalent of 0.05 rem. LEC refers to liquid EFFLUENT CONCENTRATION.

1.21 ELEVATED (STACK) RELEASE An airborne effluent plume whose release point is higher than twice the height of the nearest adjacent solid structure and well above any building wake effects*so as to be essentially unentrained.

Regulatory Guide 1.111 is the basis of the definition of an ELEVATED RELEASE. Elevated releases generally will not produce any significant ground level concentrations within the first few hundred yards of the source. ELEVATED RELEASES generally have less dose consequence to the public due to the greater downwind distance to the ground concentration maximum compared to ground releases.

All main stack releases at the OCGS are ELEVATED RELEASES.

1.22 FINITE PLUME MODEL Atmospheric dispersion and dose assessment model which is based on the assumption that the horizontal and vertical dimensions of an effluent plume are not necessarily large compared tg the distance that gamma rays can travel in air. It is more realistic than the semi-infinite plume model because it considers the 102015 CY-OC-170-301 Revision 7 Page 13 of 140 finite dimensions of the plume, the radiation build-up factor, and the air attenuation of the gamma rays coming from the cloud. This model can estimate the dose to a receptor who is not submerged in the radioactive cloud. It is particularly useful in evaluating doses from an elevated plume or when the receptor is near the effluent source. 1.23 GROUND LEVEL NENT) RELEASE An airborne effluent plume which contacts the ground essentially at the point of release either from a source actually located at ground elevation or from a source well above the ground elevation which has significant building wake effects to cause the plume to be entrained in the wake and driven to the ground elevation.

GROUND LEVEL RELEASES are treated differently than ELEVATED RELEASES in that the X/Q calculation results in significantly higher concentrations at the ground elevation near the release point. 1.24 OCCUPATIONAL DOSE . The dose received by an individual in a RESTRICTED AREA or in the course of employment in which the individual's assigned duties involve exposure to radiation and to radioactive material from licensed and unlicensed sources of radiation, whether in the possession of the licensee or other person. Occupational dose does not inClude dose received from background radiation, as a patient from medical practices, from voluntary participation in medical research programs, or as a member of the general public

1.25 "OPEN DOSE" A routine effluent dosimetry computer program that uses Reg. Guides 1 .109 and 1.111 methodologies.

1.26 RAGEMS (RADIOACTIVE EMISSIONS MONITORING SYSTEM) A plant system that monitors gaseous effluent releases from monitored release points. There is a RAG EMS system for the main stack (RAG EMS I) and one for the turbine building (RAGEMS II). They monitor particulates, iodine's, and noble gases. 1.27 SEMI-INFINITE PLUME MODEL Dose assessment model with the following assumptions.

The ground is considered to be an infinitely large flat plate and the receptor is located at the origin of a hemispherical cloud of infinite radius. The radioactive cloud is limited to the space above the ground plane. The semi-infinite plume model is limited to immersion dose calculations.

1.28 SOURCE TERM 102015 CY-OC-170-301 Revision 7 Page 14 of 140 The activity release rate, or concentration of an actual release or potential release. The common units for the source term are* curies, curies per second, and curies per cubic centimeter, or multiples thereof (e.g., micro curies). 1.29 X/Q -("CHI over Q") The dispersion factor of a gaseous release in the environment calculated by a point source Gaussian dispersion model. Normal units of XIQ are sec/m 3. The X/Q is used to determine environmental atmospheric concentrations by multiplying the source term, represented by Q (in units of µCi/sec or Ci/sec). Thus, the plume dispersion, X/Q (seconds/cubic meter) multiplied by the source term, Q (uCi/seconds) yields an environmental concentration, X (µCi/m 3). X/Q is a function of many parameters including wind speed, stability class, release point height, building size, and release velocity.

1.30 SEEDS (Simplified Effluent Environmental Dosimetry System) A routine effluent dosimetry computer program that uses Reg. Guides 1.109 and 1.111 methodologies.

TABLE 1.1: SURVEILLANCE FREQUENCY NOTATION*

NOTATION s D w M Q SA A R FREQUENCY At least once per 12 hours1.388889e-4 days 0.00333 hours 1.984127e-5 weeks 4.566e-6 months . At least once per 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months . At least once per 7 days. At least once per 31 days. At least once per 92 days. At least once per 184 days. At least once per 366 days. At least once per 18 months (550 days). 1/24 S/U At least once per 24 months (refueling cycle) Prior to each reactor startup. p Prior to each radioactive release. N.A. Not applicable.

Each surveillance requirement shall be performed within the specified time interval with a maximum allowable extension not to exceed 25% of the surveillance interval.

102015 3/4 CONTROLS AND SURVEILLANCE REQUIREMENTS 3/4.0 APPLICABILITY CONTROLS CY-OC-170-301 Revision 7 Page 15 of 140 3.0.1 Compliance with the CONTROLS contained in the succeeding CONTROLS is required during the OPERATIONAL CONDITIONS or other conditions specified therein; except that upon failure to meet the CONTROL, the associated ACTION requirements shall be met. 3.0.2 Noncompliance with a CONTROL shall exist when the requirements of the CONTROL and associated ACTION requirements are not met within the specified time intervals.

If the CONTROL is restored prior to expiration of the specified time intervals, completion of the ACTION requirements is not required.

3.0.3 Except

as provided in the associated ACTION requirements, when a CONTROL is not met or the associated ACTION requirements cannot be satisfied, action shall be initiated to place the unit into COLD SHUTDOWN within the following 30 hours3.472222e-4 days 0.00833 hours 4.960317e-5 weeks 1.1415e-5 months . Where corrective measures are completed that permit operation under the ACTION

requirements, the ACTION may be takeh in accordance with the specified time limits as measured from the time of failure to meet the CONTROL. Exceptions to these requirements are stated in the individual CONTROLS.

This CONTROL is not applicable in COLD SHUTDOWN or REFUELING.

3.0.4 Entry

into an OPERATIONAL CONDITION or other specified condition shall not be made when the conditions of the CONTROLS are not met and the associated ACTION requires a shutdown if they are not met within a specified time interval.

Entry into an OPERATIONAL CONDITION or other specified condition may be made in accordance with ACTION requirements when conformance to them permits continued operation of the facility for an unlimited period of time. This provision shall not prevent passage through or to OPERATIONAL CONDITIONS as required to comply with ACTION requirements.

Exceptions to these requirements are stated in the individual CONTROLS.

3.0.5 Equipment

removed from service or declared inoperable to comply with ACTIONS may be returned to service under administrative control solely to perform testing to demonstrate its OPERABILITY or the OPERABILITY of other equipment.

This is an exception to CONTROL 3.0.2 for the system returned to service under administrative control to perform the testing required to demonstrate OPERABILITY.

102015 3 /4.0 APPLICABILITY SURVEILLANCE REQUIREMENTS CY-OC-170-301 Revision 7 Page 16 of 140 4.0.1 Surveillance Requirements shall be met during the OPERATIONAL CONDITIONS or other conditions specified for individual CONTROLS unless otherwise stated in an individual Surveillance Requirement.

4.0.2 Each Surveillance Requirement shall be performed within the specified surveillance interval with a maximum allowable extension not to exceed 25 percent of the specified surveillance interval.

4.0.3 Failure

to perform a Surveillance Requirement within the allowed surveillance interval, defined by CONTROL 4.0.2, shall constitute a failure to meet the OPERABILITY requirements for a CONTROL. The time limits of the ACTION requirements are applicable at the time it is identified that a Surveillance Requirement has not been performed.

The ACTION requirements may be delayed for up to 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months to permit the completion of the surveillance when the allowed outage time limits of the ACTION requirements are less than 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months . Surveillance Requirements do not have to be performed on inoperable equipment.

4.0.4 Entry

into an OPERATIONAL CONDITION or other specified applicable condition shall not be made unless the Surveillance Requirement(s) associated with the CONTROLS have been performed within the applicable surveillance interval or as otherwise specified.

This provision shall not prevent passage through or to OPERATIONAL CONDITIONS as required to comply with ACTION requirements.

102015 3/4.3 INSTRUMENTATION CY-OC-170-301 Revision 7 Page 17 of 140 3/4.3.3.10 RADIOACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTATION CONTROLS 3.3.3.1 O In accordance with Oyster Creek Technical Specifications 6.8.4.a.1, the radioactive liquid effluent monitoring instrumentation channels shown in Table 3.3.3.10-1 shall be OPERABLE with their Alarm/Trip set points set to ensure that the limits of CONTROL 3.11.1.1 are not exceeded.

The Alarm/Trip set points of these channels shall be determined and adjusted in accordance with the methodology and parameters in the ODCM Part II section 1.2.1. APPLICABILITY:

During all liquid releases via these pathways.

ACTION: a. With a radioactive liquid effluent monitoring instrumentation channel Alarm/Trip set point less conservative than required by the above CONTROL, immediately suspend the release of radioactive liquid effluents monitored by the affected channel, or declare the channel inoperable, or change the set point so iris acceptably conservative, or provide for manual initiation of the Alarm/Trip function(s).

b. With less than the minimum number of radioactive liquid effluent monitoring instrumentation channels OPERABLE, take the ACTION shown in Table 3.3.3.10-1.

Make every reasonable effort to return the instrument to OPERABLE status within 30 days and, if unsuccessful, explain in the next Radioactive Effluent Release Report pursuant to Technical Specification 6.9.1.d why the inoperability was not corrected in a timely manner. c. The provisions of CONTROL 3.0.3 and 3.0.4 are not applicable.

Report all deviations in the Radioactive Effluent Release Report. SURVEILLANCE REQUIREMENTS 4.3.3.1 O Each radioactive liquid effluent monitoring instrumentation channel shall be demonstrated OPERABLE by performance of the CHANNEL CHECK, SOURCE CHECK, CHANNEL CALIBRATION, and CHANNEL FUNCTIONAL TEST at the Frequencies shown in Table 4.3.3.10-1.

102015 CY-OC-170-301 Revision 7 Page 18of140 TABLE 3.3.3.10-1:

RADIOACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTATION INSTRUMENT

1. RADIOACTIVITY MONITORS PROVIDING ALARM AND AUTOMATIC TERMINATION OF RELEASE a. Liquid Radwaste Effluent Line (DELETED)

b. Turbine Building Sump No. 1-5 (DELETED)

2. RADIOACTIVITY MONITORS PROVIDING ALARM BUT NOT PROVIDING AUTOMATIC TERMINATION OF RELEASE a. Reactor Building Service Water System Effluent Line 3. FLOW RATE MEASUREMENT DEVICES a. Liquid Radwaste Effluent Line (DELETED)

b. Groundwater Remediation Release Path MINIMUM CHANNELS OPERABLE N/A N/A 1 N/A 1 ACTION N/A N/A 112 N/A 115 102015 CY-OC-170-301 Revision 7 Page 19of140 TABLE 3.3.3.10-1 (Continued)

TABLE NOTATIONS ACTION 110 With no channels OPERABLE, effluent releases via this pathway may continue provided that: a. At least two independent samples are taken, one prior to discharge and one near the completion of discharge and analyzed in accordance w.ith SURVEILLANCE REQUIREMENT 4.11.1.1.1.

b. Before initiating a release, at least two technically qualified members of the Facility Staff independently verify the release rate calculations and discharge line valving; Otherwise, suspend release of radioactive effluents via this pathway. ACTION 112 With no channels OPERABLE, effluent releases via this pathway may continue provided that, at least once per 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months , grab samples are collected and analyzed for radioactivity at a limit of detection specified by Table 4.11.1.1.1-1.

ACTION 113 With no channel OPERABLE, effluent releases via the affected pathway may continue provided the flow is estimated with the pump curve .or change in tank level, at least once per batch during a release.*

ACTION 114 With no channel OPERABLE effluent may be released provided that before initiating a release: a. A sample is taken and analyzed in accordance with SURVEILLANCE REQUIREMENT 4.11.1.1.1.

b. Qualified personnel determine and independently verify the acceptable release rate. ACTION 115 With. no channel OPERABLE, effluent releases via this pathway may continue provided the flow rate is estimated at least once per 4 hours4.62963e-5 days 0.00111 hours 6.613757e-6 weeks 1.522e-6 months during actual releases.

Pump performance curves may be used _to estimate flow. 102015 CY -OC-170-301 Revision 7 Page 20 of 140 TABLE 4.3.3.10-1:

RADIOACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTATION SURVEILLANCE REQUIREMENTS 8 CHANNEL CHANNEL SOURCE CHANNEL FUNCTIONAL INSTRUMENT CHECK CHECK CALIBRATION TEST 1. RADIOACTIVITY MONITORS PROVIDING ALARM AND AUTOMATIC TERMINATION OF RELEASE a. Liquid Radwaste Effluent Line (DELETED) NIA NIA NIA NIA b. Turbine Building Sump No. 1-5 (DELETED) NIA NIA NIA NIA

2. RADIOACTIVITY MONITORS PROVIDING ALARM BUT NOT PROVIDING AUTOMATIC TERMINATION OF RELEASE a. Reactor Building Service Water System Effluent Line D M 3. FLOW RATE.MEASUREMENT DEVICES a. Liquid Radwaste Effluent Line (DELETED)

NIA NIA NIA NIA b. Groundwater Remediation Release path NIA NIA 102015 TABLE 4.3.3.10-1 (Continued)

TABLE NOTATIONS CY-OC-170-301 Revision 7 _,Page 21 of 140 a. Instrumentation shall be OPERABLE and in service except that a channel may be taken out of service for the purpose of a check, calibration, test or maintenance without declaring it to be inoperable.

d. The CHANNEL FUNCTIONAL TEST shall also demonstrate that Control Room alarm annunciation occurs if any of the following conditions exists: 1. Instrument indicates measured levels above the alarm set point. 2. Instrument indicates a downscale failure. 3. Instrument controls not set in operate mode. 4. Instrument electrical power loss. e. The CHANNEL CALIBRATION shall be performed according to established calibration procedures.

f. While actively discharging through this pathway. 102015 3/4.3 INSTRUMENTATION CY-OC-170-301 Revision 7 Page 22 of 140 3/4.3.3.11 RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION CONTROLS 3.3.3.11 In accordance with Oyster Creek Technical Specifications 6.8.4.a.1, the radioactive gaseous effluent monitoring instrumentation channels shown in Table 3.3.3.1_ 1-1 shall be OPERABLE with their alarm/trip set points set to ensure that the limits of CONTROL 3.11.2.1 are not exceeded.

The alarm/trip set points of these channels meeting CONTROLS 3.11.2.1 shall be determined and adjusted in accordance with the methodology and parameters in the ODCM Part II Section 2.2. APPLICABILITY:

As shown in Table 3.3.3.11-1 ACTION: a. With a radioactive gaseous effluent monitoring instrumentation channel alarm/trip set point less conservative than required by the above CONTROL, immediately suspend the release of radioactive gaseous effluents monitored by the affected channel, or declare the channel inoperable, or change the set point so it is acceptably conservative.

-b. With less than the minimum number of radioactive gaseous effluent monitoring instrumentation channels OPERABLE, take the ACTION shown in Table 3.3.3.11-1. Exert best efforts to return the instrument to OPERABLE status within 30 days and, if unsuccessful, explain in the next Radioactive Effluent Release Report pursuant to Technical Specification 6.9.1.d why this inoperability was not corrected in a timely manner. c. The provisions of CONTROLS 3.0.3 and 3.0.4 are not applicable.

Report all deviations in the Radioactive Effluent Release Report. SURVEILLANCE REQUIREMENTS 4.3.3.11 Each radioactive gaseous effluent monitoring instrumentation channel shall be demonstrated OPERABLE by performance of the CHANNEL CHECK, SOURCE CHECK, CHANNEL CALIBRATION, and CHANNEL FUNCTIONAL TEST operations at the frequencies shown in Table 4.3.3.11-1.

--102015 CY-OC-170-301 Revision 7 Page 23 of 140 TABLE 3.3.3.11-1:

RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION MINIMUM CHANNELS INSTRUMENT OPERABLE 8 APPLICABILITY ACTION 1. DELETED 2. STACK MONITORING SYSTEM a. Radioactive Noble Gas Monitor (Low Range) 1 b,e 124 b. Iodine Sampler 1 b,e 127 c. Particulate Sampler 1 b,e 127 d. Effluent Flow Measuring Device 1 b 122 e. Sample Flow Measuring Device 1 b 128 3. TURBINE BUILDING VENTILATION MONITORING SYSTEM a. Radioactive Noble Gas Monitor (Low Range) 1 b 123 b. Iodine Sampler 1 b 127 c. Particulate Sampler 1 b 127 d. Effluent Flow Measuring Device* 1 b 122 e. Sample Flow Measuring Device 1 b 128 102015 TABLE 3.3.3.11-1 (Continued)

RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION INSTRUMENT MINIMUM CHANNELS OPERABLE 8 APPLICABILITY

4. AUGMENTED OFF GAS BUILDING EXHAUST VENTILATION MONITORING SYSTEM a. Radioactive Noble Gas Monitor 1 b b. Iodine Sampler 1 b c. Particulate Sampler 1 b d. Sample Flow Measuring Device 1 b CY-OC-170-301

Revision 7 Page 24 of 140 ACTION 123 127 127 128 102015 TABLE 3.3.3.11-1 (Continued)

TABLE NOTATIONS CY-OC-170-301 Revision 7 Page 25 of 140 a. Channels shall be OPERABLE and in service as indicated except that a channel may be taken out of service for the purpose of a check, calibration, test maintenance or sample media change without declaring the channel to be inoperable.

b. During releases via this pathway e. Monitor I sampler or an alternate shall be OPERABLE to monitor I sample Stack effluent whenever the drywell is being purged. ACTION 122 With no channel OPERABLE, effluent releases via this pathway may continue provided the flow rate is estimated whenever the exhaust fan combination in this system is changed. ACTION 123 With no channel OPERABLE, effluent releases via this pathway may continue provided a grab sample is taken at least once per 48 hours5.555556e-4 days 0.0133 hours 7.936508e-5 weeks 1.8264e-5 months and is analyzed for gross radioactivity within 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months thereafter or provided an alternate monitoring system with local display is utilized.

ACTION 124 With no channel OPERABLE, effluent releases via this pathway may continue provided a grab sample is taken at least once per 8 hours9.259259e-5 days 0.00222 hours 1.322751e-5 weeks 3.044e-6 months and analyzed for gross radioactivity within 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months or provided an alternate monitoring system with local display is utilized.

Drywell purge is permitted only when the radioactive noble gas monitor is operating.

ACTION 127 With no channel OPERABLE, effluent releases via this pathway may continue provided the required sampling is initiated with auxiliary sampling equipment as soon as reasonable after discovery of inoperable primary sampler(s).

ACTION 128 With no channel OPE:RABLE, effluent releases via the sampled pathway may continue provided the sampler air flow is estimated and recorded at least once per day. 102015 CY-OC-170-301 Revision 7 Page 26 of 140 TABLE 4.3.3.11-1:

RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION SURVEILLANCE REQUIREMENTS CHANNEL MODES IN WHICH CHANNEL SOURCE CHANNEL FUNCTIONAL SURVIELLANCE INSTRUMENT CHECK CHECK CALIBRATION TEST REQUIRED 8 1. DELETED 2. MAIN STACK MONITORING SYSTEM a. Radioactive Noble Gas Monitor (Low Range) D M 1/24f Qh b b. Iodine Sampler w N.A. N.A. N.A. b c. Particulate Sampler w N.A. N.A. N.A. b d. Effluent Flow Measuring Device D N.A. 1/24 Q b e. Sample Flow Measuring Device D N.A. R Q b 3. TURBINE BUILDING VENTILATION MONITORING SYSTEM a. Radioactive Noble Gas Monitor (Low Range) D M 1/24f Qi b b. Iodine Sampler w N.A. N.A.

N.A. b c. Particulate Sampler w N.A. N.A. N.A. b d. Effluent Flow Measuring Device D N.A. 1/24 Q b e. Sample Flow Measuring Device D N.A. R Q b 102015 TABLE 4.3.3.11-1{Continued)

CY-OC-170-301 Revision 7 Page 27 of 140 RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION SURVEILLANCE REQUIREMENTS CHANNEL MODES IN WHICH CHANNEL SOURCE CHANNEL FUNCTIONAL SURVIELLANCE IS INSTRUMENT CHECK CHECK CALIBRATION TEST REQUIRED a 4. AUGMENTED OFF GAS BUILDING EXHAUST VENTILATION MONITORING SYSTEM a. Radioactive Noble Gas Monitor D M Rf ae *b b. Iodine Sampler w N.A. N.A. N.A. b c. Particulate Sampler w N.A. N.A.

N.A. b d. Sample Flow Measuring Device D N.A. .R N.A. b 102015 CY-OC-170-301 Revision 7 Page 28of140 TABLE 4.3.3.11-1 (Continued)

TABLE NOTATIONS

a. Instrumentation shall be OPERABLE and in service except that a channel may be taken out of service for the purpose of a check calibration, test or maintenance without declaring it to be inoperable.

b. During releases via this pathway. e. The CHANNEL FUNCTIONAL TEST shall also demonstrate that control room alarm annunciation occurs if any of the following conditions exist: 1. Instrument indicates measured levels above the alarm set point. 2. Instrument indicates a downscale failure. 3. Instrument controls not set in operate mode. 4. Instrument electrical power loss. f. The CHANNEL CALIBRATION shall be performed according to established calibration procedures.

h. The CHANNEL FUNCTIONAL TEST shall also demonstrate that control room alarm annunciation occurs if any of the following conditions exists: 1. Instrument indicates measured levels above the alarm set point. 2. Instrument indicates a low count rate/monitor failure. 3. Switch cover alarm shall be verified to alarm when the cover is opened; and clear when the cover is closed after the faceplate switches are verified in their correct positions.

i. The CHANNEL FUNCTIONAL TEST shall also demonstrate that control room alarm annunciation occurs if any of the following conditions exists: 1. Instrument indicates measured levels above the alarm set point. 2. Instrument indicates a low count rate/monitor failure. 102015 3/4.11 RADIOACTIVE EFFLUENTS 3/4.11.1 LIQUID EFFLUENTS 3/4.11.1.1 CONCENTRATION CONTROLS CY-OC-170-301 Revision 7 Page 29 of 140 3.11.1.1 In accordance with the Oyster Creek Technical Specifications 6.8.4.a.2 and 3, the concentration of radioactive material, other than noble gases, in liquid effluent in the discharge canal at the Route 9 bridge (See Figure E-4) shall not exceed the concentri;ltions specified in 10 CFR Part 20, Appendix B, Table 2, Column 2. The concentration of noble gases dissolved or entrained in liquid effluent in the discharge canal at the Route 9 bridge shall not exceed 2E-4 microcuries/milliliter.

APPLICABILITY:

At all times. ACTION: a. In the event the concentration of radioactive material in liquid effluent released into the Off Site area beyond the Route 9 bridge exceeds either of the concentration . limits above, reduce the release rate without delay to bring the concentration below the limit. b. The provisions of CONTROLS 3.0.3, 3.0.4 and Technical Specification 6.9.2 are not applicable.

SURVEILLANCE REQUIREMENTS 4.11.1.1.1 Radioactive liquid wastes shall be sampled and analyzed according to the sampling and analysis program in Table 4.11.1.1.1-1.

Alternately, pre-release analysis of batches(es) of radioactive liquid waste may be by gross beta or gamma counting provided a maximum concentration limit of 1 E-8 µCi/ml in the discharge canal at the Route 9 bridge is applied. 4.11.1.1.2 The results of the radioactivity analyses shall be used in accordance with the methodology and parameters in the ODCM Part 11 Section 1.2 to assure that the concentrations at the point of release are maintained within the limits of CONTROL 3.11.1.1 and 3.11.1.2.

4.11.1.1.3 The alarm or trip set point of each radioactivity monitoring channel in Table 3.3.3.10-1 shall be determined on the basis of sampling and analyses results obtained according to Table 4.11.1.1.1-1 and the set point method in ODCM Part II 1.2.1 and set to alarm or trip before exceeding the limits of CONTROL 3.11.1.1.

102015 CY-OC-170-301 Revision 7 Page 30 of 140 TABLE 4.11.1.1.1-1:

RADIOACTIVE LIQUID WASTE SAMPLING AND ANALYSIS PROGRAM Sampling Minimum Lower Limit Liquid Release Type Analysis Type of Activity Analysis Detectiona (LLD) Frequency Frequency

(µCi/ml) p pc Principal Gamma Emitters 5E-07 1. Batch Waste Release Tanks Each Batchb Each Batch 1-131 5E-07 p M Dissolved and Entrained One Gases (Gamma Emitters) 1E-05 Batch/Mb p M H-3 1E-05 Each Batchb Composited Gross Alpha 1E-07 p Q Sr-89, Sr-90 5E-08 Each Batchb Composited Fe-55 1E-06 w Principal Gamma Emitters 5E-07 2. Continuous w Release Grab 1-131 5E-07 a. Reactor Building Samplee Service Water H-3 1E-05 Effluent Gross Alpha 1E-07 M (note f) Composite 9 Fe-55 1E-06 3. Groundwater D Principal Gamma Emitters 5E-07 Remediation Pathway Continuoush

a. Continuous Composite H-3 1E-05 Gross Alpha 1E-07 M Sr-89, Sr-90 5E-08 M Composite 9 Fe-55 1E-06 Ni-63 1E-06 b. Batch Release p p Principal Gamma Emitters 5E-07 Tank Each Batchb Each Batch H-3 1E-05 Gross Alpha 1E-07 p M Sr-89, Sr-90 5E-08 Each Batchb Composited Fe-55 1E-06 Ni-63 1E-06 102015 TABLE 4.11.1.1-1 (CONTINUED)

TABLE NOTATIONS CY-OC-170-301 Revision 7 Page 31 of 140 a. The Lower Limit of Detection (LLD) is defined, for purposes of these specifications, as the smallest concentration of radioactive material in a sample that will yield a net count, above system background, that will be detected with 95 percent probability with only 5 percent probability of falsely concluding that a blank obse.rvation represents a "real" signal. The LLD is applicable to the capability of a measurement system under typical conditions and not as a limit for the measurement of a particular sample in the radioactive liquid waste sampling and analyses program. For a particular measurement system, which may include radiochemical separation:

LLD=

__ _ E

V

2.22E6

Y

exp(-'A1'1.t)

Where: !-LO is the lower limit of detection as defined above (microcurie per unit mass or volume), .. Sb is the standard deviation of the background counting rate or -of the counting rate of a blank

sample as appropriate (counts per minute), Eis the counting efficiency, V is the sample size (units of mass or volume), 2.22E+6 is the number of disintegrations per minute per microcurie, Y is the fractional radiochemical yield, when applicable,*

'A is the radioactive decay constant for the particular radionuclide, and. At is the elapsed time between the end of the sample collection and the time of counting.

Analyses shall be performed in such a manner that the stated LLDs wilf be achieved under routine conditions with typical values of E, V, Y, and t for the radionuclides Mn-54, Fe-59, Co-58, Co-60, Zn-65, Mo-99, Ce-141, Cs-134, Cs-137; and an LLD of 5E-6 µCi/ml should typically be achieved for Ce-144. 102015 TABLE 4.11.1.1.1-1 (CONTINUED)

TABLE NOTATIONS CY-OC-170-301

Revision 7 Page 32 of 140 Occasionally, background fluctuations, interfering radionuclides, or other uncontrollable circumstances may render these LLD's unachievable.

When calculating the LLD for a radionuclide determined by gamma ray spectrometry, the background may include the typical contributions of other radionuclides normally present in the sample. The background count rate of a semiconductor detector (e.g. HPGe) is determined from background counts that are determined to be within the full width of the specific energy band used for the quantitative analysis for the radionuclide.

The principal gamma emitters for which the LLD specification will apply are exclusively the following radionuclides:

Mn-54, Fe-59, Co-58, Co-60, Zn-65, Mo-99, Cs-134, Cs-137, Ce-141, and Ce-144. This list does not mean that only these nuclides are to be detected anq reported.

Other peaks that are measurable and identifiable, together with the-above nuclides, shall be identified and reported.

The LLD for Ce-144 is 5E-6 µCi/ml whereas the LLD for Mo-99 and the other gamma emitters is 5E-7 µCi/ml. Nuclides that are below the LLD for the analysis should not be reported.

b. A batch release is the discharge ofliquid wastes of a discrete volume. Before sampling for analysis, each batch should be thoroughly mixed. c. In the event a gross radioactivity analysis is performed in lieu of an isotopic analysis before a batch is discharged, a sample will be analyzed for principal gamma emitters afterwards.

d. A composite sample is one in which the quantity of liquid sampled is proportional to the quantity of liquid waste discharged and in which the method of sampling employed results in a specimen which is representative of the liquids released.

e. Analysis may be performed after release. f. In the event a grab sample contains more than 5E-7 µCi/ml of 1-131 and principal gamma emitters or in the event the Reactor Building Service Water radioactivity monitor indicates more than 5E-7 µCi/ml radioactivity in the effluent, as applicable, sample the elevated activity effluent daily until analysis confirms the activity concentration in the effluent does not exceed 5E-7 µCi/ml. In addition a composite sample must be made up* for further analysis for all samples taken when the activity was> 5E-7 µCi/ml. g. A composite sample is produced combining grab samples, each having a defined volume,* collected routinely from the sump or stream being sampled h. Aliquot sampling shall be at least hourly to be representative of the quantities and concentrations of radioactive materials in liquid effluent.

Prior to analyses, all samples taken for the composite shall be thoroughly mixed in order for the composite samples to be representative of the effluent release. 102015 3/ 4.11 RADIOACTIVE EFFLUENTS CY-OC-170-301 Revision 7 Page 33 of 140 3/ 4.11.1.2 DOSE CONTROLS 3.11.1.2 In accordance with Oyster Creek Technical Specifications 6.8.4.a.4 and 5, the dose or dose commitment to a MEMBER OF THE PUBLIC from radioactive materials in liquid effluents released to UNRESTRICTED AREAS (see Figure E-4) shall be limited: a. During any calendar quarter to less than or equal to 1.5 mrem to the Total Body and to less than or equal to 5 mrem to any body organ, and b. During any calendar year to less than or equal to 3 mrem to the Total Body and to less than or equal to 10 mrem to any body ormm. APPLICABILITY:

At all times. ACTION: a. With the calculated dose from the release of radioactive materials in liquid effluents exceeding any of the above limits, prepare and submit to the Commission within 30 days from the end of the quarter, pursuant to Technical Specification 6.9.2, a Special Report that identifies the cause(s) for exceeding the limit(s) and defines the corrective actions that have been taken and/or will be taken to reduce the releases and the proposed corrective actions to be taken to assure that subsequent releases will be in compliance with the above limits. b. The provisions of CONTROL 3.0.3 and 3.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS

4.11.1.2 Cumulative dose contributions from liquid effluents for the current calendar quarter and the current calendar year shall be determined in accordance with the methodology and parameters in the ODCM Part II Section 1.5 at least once per 31 days in accordance with Technical Specification 6.8.4.a.5.

102015 3/4.11 RADIOACTIVE EFFLUENTS CY-OC-170-301 Revision 7 Page 34 of 140 3/4.11.1.3 LIQUID WASTE TREATMENT SYSTEM CONTROLS 3.11.1.3 In accordance with the Oyster Creek Technical Specifications 6.8.4.a.6, the liquid radwaste treatment system shall be OPERABLE and appropriate portions of the system shall be used to reduce releases of radioactivity when projected doses due to the liquid effluent to UNRESTRICTED AREAS (see Figure E-4) would exceed 0.06 mrem to the Total Body or 0.2 mrem to any organ in a 31 day period. APPLICABILITY:

At all times. ACTION: a. With radioactive liquid waste being discharged without treatment and in excess of the above, prepare and submit to the Commission within 30 days, pursuant to Technical Specification 6.9.2, a Special Report that includes the following information:

1. Explanation of why liquid radwaste was being discharged without treatment, identification of any inoperable equipment or subsystems, and the reason for the inoperability, 2. Action(s) taken to restore the inoperable equipment to OPERABLE status, and 3. Summary description of action(s) taken to prevent a recurrence.

b. The provisions of CONTROL 3.0.3 and 3.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS 4.11.1.3.1 Doses due to liquid releases to UNRESTRICTED AREAS shall be projected at least once per 31 days in accordance with the methodology and parameters in the ODCM Part II Section 1.5 in accordance with Technical Specifications 6.8.4.a.5.

4.11.1.3.2 The installed liquid radwaste treatment system shall be demonstrated OPERABLE by meeting CONTROLS 3.11.1.1, 3.11.1.2, and 3.11.1.3.

102015 3/4.11 RADIOACTIVE EFFLUENTS 3/4.11.2 GASEOUS EFFLUENTS 3/4.11.2.1 DOSE RA TE CONTROLS CY-OC-170-301 Revision 7 Page 35 of 140 3.11.2.1 In accordance with the Oyster Creek Technical Specifications 6.8.4.a.5 and 7, the dose rate due to radioactive materials released in gaseous effluents in the UNRESTRICTED AREA (see Figure E-4) shall be limited to the following:

a. For noble gases: Less than or equal to 500 mrem/yr to the total body and less than or equal to 3000 mrem/yr to the skin, and b. For iodine-131, iodine-133, tritium, and for all radionuclides in particulate form with half-lives greater than 8 days: Less than or equal to 1500 mrem/yr to any body organ. APPLICABILITY:

At all times. ACTION: a. With the dose rate(s) exceeding the above limits, immediately restore the release rate to within the above limit(s).

b. If the gaseous effluent release rate cannot be reduced to meet the above limits, the reactor shall be in at least SHUTDOWN CONDITION within 48 hours5.555556e-4 days 0.0133 hours 7.936508e-5 weeks 1.8264e-5 months unless corrective actions have been completed and the release rate restored to below the above limit. SURVEILLANCE REQUIREMENTS 4.11.2.1.1 The dose rate due to noble gases in gaseous effluents shall be determined to be within the above limits in accordance with the methodology and parameters in the ODCM Part 11 Section 2.3.1. 4.11.2.1.2 The dose rate due to iodine-131, iodine-133, tritium, and all radionuclides in particulate form with half-lives greater than 8 days in gaseous effluents shall be determined to be within the above limits in accordance with the methodology and parameters in the ODCM Part II Section 2.3.2 by obtaining representative samples and performing analyses in accordance with the sampling and analysis program specified in Table 4.11.2.1.2-1.

4.11.2.1.3 Dose rates due to tritium, Sr-89, Sr-90, and alpha-emitting radionuclides are averaged over no more than 3 months and the dose rate due to other radionuclides is averaged no more than 31 days. 102015 CY-OC-170-301 Revision 7 Page 36 of 140 TABLE 4.11.2.1.2-1:

RADIOACTIVE GASEOUS WASTE SAMPLING AND ANALYSIS PROGRAM Gaseous Release Sampling Minimum Type of Activity Lower Limit Analysis Detectiona (LLD) Type Frequency Frequency Analysis (µCi/ml) Q Grab Samplef Q H-3 1E-06 M M Principal Gamma Grab Sample Emittersb (Noble 1E-04 c,d,f Gases) w 1-131 1E-12 Continuousf Charcoal Sample 1-133 1E-10 w Principal Stack; Continuousf Particulate Gamma 1 E-11 Turbine Building Sample Emittersb Exhaust Vents; (particulates)

Augmented Off gas Me Building Vent Continuousf Composite Gross Alpha 1 E-11 Particulate Sample ae Composite 1 E-11 Continuous Sr-89, Sr-90 Particulate Sample Noble Gas Noble Gases 1E-06 Continuous Monitor Gamma Radioactivity 102015 TABLE 4.11.2.1.2-1 (Continued)

TABLE NOTATIONS CY-OC-170-301 Revision 7 Page 37 of 140 a. The Lower Limit of Detection (LLD) is defined, for purposes of these specifications, as the smallest concentration of radioactive material in a sample that will yield a net count, above system background, that will be detected with 95 percent probability with only 5 percent probability of falsely concluding that a blank observation represents a "real" signal. The LLD is applicable to the capability of a measurement system under typical conditions and not as a limit for the measurement of a particular sample in the radioactive*

liquid waste sampling and analyses program. For a particular measurement system which may include radiochemical separation:

LLD = __ 4_.6_6_*_Sb

___ _ E

V

2.22E6

Y

Where: LLD is the lower limit of detection as defined above (microcurie per unit mass or volume), Sb is the standard deviation of the background counting rate or of the counting rate of a blank sample as appropriate (counts per minute), Eis the counting efficiency, Vis the sample size (units of mass or volume), 2.22E+6 is the number of disintegrations per minute per microcurie, Y is the fractional radiochemical yield, when applicable, 'A is the radioactive decay constant for the particular radionuclide, and .M is the elapsed time between the end of the sample collection and the time of counting.

Analyses shall be performed in such a manner that the stated LLD's will be achieved under routine conditions with typical values of E, V, Y, and t for the radionuclides.

Mn-54, Fe-59, Co-58, Co-60, Zn-65, Cs-134, Cs-137, and Ce-141. Occasionally background fluctuations or other uncontrollable circumstances may render these LLD's unachievable.

When calculating the LLD for a radionuclide determined by gamma ray spectrometry, the background may include the typical contributions of other radionuclides normally present in the samples. The background count rate of a HpGe detector is determined from background 102015 TABLE 4.11.2.1.2-1 (Continued)

TABLE NOTATIONS CY-OC-170-301 Revision 7 Page 38 of 140 counts that are determined to be within the full width of the specific energy band used for the quantitative analysis for that radionuclide

b. The principal gamma emitters for which the LLD specification applies exclusively are the following radionuclides:

Kr-87, Kr-88, Xe-133, Xe-133m, Xe-135 and Xe-138 for gaseous emissions and Mn-54, Fe-59, Co-58, Co-60, Zn-65, Mo-99, Cs-134, Cs-137, Ce-141, and Ce-144 for particulate emissions.

This list does not mean that only these nuclides are to be considered.

Other gamma peaks that are identifiable, together with those of the above nuclides, shall also be analyzed and reported in the Annual Radioactive Effluent Release Report consistent with CONTROL 3.11.2.1.

The LLD for Mo-99 and Ce-144 is 1 E-1 O µCi/ml whereas the LLD for other principal gamma emitting particulates is 1 E-11 µCi/ml. Radionuclides which are below the LLD for the analysis should not be reported.

c. The noble gas radionuclides in gaseous effluent may be identified by taking a grab sample of effluent and analyzing it. d. In the event the reactor power level increases more than 15 percent in one hour and the Stack noble gas radioactivity monitor shows an activity increase of more than a factor of three after factoring out the effect due to the change in reactor power, a grab sample of Stack effluent shall be collected and analyzed.

e. A composite particulate sample shall include an equal fraction of at least one particulate sample collected during each week of the compositing period. f. In the event a sample is collected for 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months or less, the LLD may be increased by a factor of 10. 102015 3/4.11 RADIOACTIVE EFFLUENTS 3/4.11.2.2 DOSE -NOBLE GASES CONTROLS CY-OC-170-301 Revision 7 Page 39 of 140 3.11.2.2 In accordance with the Oyster Creek Technical Specification 6.8.4.a.5 and 8, the air dose due to noble gases released in gaseous effluents in the UNRESTRICTED AREA (see Figure E-4) shall be limited to the following:

a. During any calendar quarter: Less than or equal to 5 mrad for gamma radiation and less than or equal to 10 mrad for beta radiation and, b. During any calendar year: Less than or equal to 10 mrad for gamma radiation and less than or equal to 20 mrad for beta radiation.

APPLICABILITY:

At all times. ACTION: a. With the calculated air dose from radioactive noble gases in gaseous effluents exceeding any of the above limits, prepare and submit to the Commission within 30 days from the end of the quarter during which the release occurred, pursuant to Technical Specification 6.9.2, a Special Report that identifies the cause(s) for exceeding the limit(s) and defines the corrective actions that have been taken to reduce the release and the proposed corrective actions to be taken to assure that subsequent releases will be in compliance with the above limits. b. The provisions of CONTROLS 3.0.3 and 3.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS 4.11.2.2 Cumulative dose contributions for the current calendar quarter and current calendar year for noble gases shall be determined in accordance with the methodology and parameters in the ODCM Part II Section 2.4.1 at least once per 31 days in accordance with Technical Specification 6.8.4.a.5.

102015 3/4.11 RADIOACTIVE EFFLUENTS CY-OC-170-301 Revision 7 Page 40 of 140 3/4.11.2.3 DOSE-IODINE-131, IODINE-133, TRITIUM, AND RADIONUCLIDES IN PARTICULATE FORM CONTROLS 3.11.2.3 In accordance with Oyster Creek Technical Specification 6.8.4.a.5 and 9, the dose to a MEMBER OF THE PUBLIC from iodine-131, iodine-133, tritium, and all radionuclides in particulate form with half-lives greater than 8 days in gaseous effluents released in the UNRESTRICTED AREA (see Figure E-4) shall be limited to the following:

a. During any calendar quarter: Less than or equal to 7.5 mrem to any body organ and, b. During any calendar year: Less than or equal to 15 mrem to any body organ. APPLICABILITY:

At all times. ACTION: a. With the calculated dose from the release of iodine-131, iodine-133 and radionuclides in particulate form with half-lives greater than 8 days, in gaseous effluents exceeding any of the above limits, prepare and submit to the Commission within 30 days, pursuant to Technical Specification 6.9.2, a Special Report that identifies the cause(s) for exceeding the limit and defines the corrective actions that have been taken to reduce the releases and the proposed corrective actions to be taken to assure that subsequent releases will be in compliance with the above limits. b. The provisions of CONTROLS 3.0.3 and 3.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS 4.11.2.3 Cumulative dose contributions for the current calendar quarter and current calendar year for iodine-131, iodine-133, tritium, and radionuclides in particulate form with lives greater than 8 days shall be determined in accordance with the methodology and parameters in the ODCM Part II Section 2.5 at least once per 31 days in accordance with Technical Specification 6.8.4.a.5.

102015 3/4.11 RADIOACTIVE EFFLUENTS 3/4.11.2.4 GASEOUS RADWASTE TREATMENT SYSTEM CONTROLS CY-OC-170-301 Revision 7 Page 41 of 140 3.11.2.4 The AUGMENTED OFF GAS SYSTEM shall be in operation to reduce releases of radioactivity when the projected doses in 31 days due to gaseous effluent releases to areas at and beyond the SITE BOUNDARY (see Figure E-4) would exceed: a. 0.2 mrad to air from gamma radiation, or b. 0.4 mrad to air from beta radiation, or c. 0.3 mrem to any body organ APPLICABILITY:

Whenever the main condenser steam jet air ejector is in operation except during startup or shutdown with reactor power less than 40 percent of rated. In addition, the AUGMENTED OFF GAS SYSTEM need not be in operation during end of cycle coast-down periods when the system can no longer function due to low off gas flow. ACTION: a. Every reasonable effort shall be made to maintain and operate charcoal absorbers in the AUGMENTED OFF GAS SYSTEM to treat radioactive gas from the main condenser air ejectors.

b. With gaseous radwaste from the main condenser air ejector system being discharged without treatment for more than 30 consecutive days and either CONTROL 3.11.2.1 or 3.11.2.4 exceeded, prepare and submit to the Commission within 30 days from the end of the quarter during which release occurred, pursuant to Technical Specification 6.9.2, a Special Report that includes the following information:

1. Identification of any inoperable equipment or subsystems, and the reason for the inoperability, 2. Action(s) taken to restore the inoperable equipment to OPERABLE status, and 3. Summary description of action(s) taken to prevent a recurrence.

c. The provisions of CONTROL 3.0.3 and 3.0.4 are not applicable.

102015 SURVEILLANCE REQUIREMENTS CY-OC-170-301 Revision 7 Page 42 of 140 4.11.2.4.1 Operation of the Augmented Off gas System charcoal absorbers shall be verified by verifying the AOG System bypass valve, V-7-31, alignment or alignment indication closed at least once every 12 hours1.388889e-4 days 0.00333 hours 1.984127e-5 weeks 4.566e-6 months whenever the main condenser air ejector is operating.

4.11.2.4.2 Doses due to gaseous releases to UNRESTRICTED AREAS shall be projected at least once per 31 days in accordance with the methodology and parameters in the ODCM Part II Section 1.5 in accordance with Technical Specifications 6.8.4.a.5.

102015 3/4.11 RADIOACTIVE EFFLUENTS 3/4.1,1.3 MARK I CONTAINMENT CONTROLS CY-OC-170-301 Revision 7 Page 43 of 140 3.11.3.1 Venting or purging of the containment Drywall may be through normal Reactor Building Ventilation if the following requirements are met: APPLICABILITY:

If the Station year-to-date radiological effluent releases (either iodine or noble gas) are less than 10% of the ODCM limit, then Standby Gas Treatment is NOT required for purging the contents of the Drywall. ACTION: a. If the Station year-to-date radiological effluent releases (either iodine or noble gas) are greater than 10% of the ODCM limit, then the Standby Gas Treatment System must be used for purging the contents of the Drywall. SURVEILLANCE REQUIREMENTS 4.11.3.1 The Standby Gas Treatment System is OPERABLE and available whenever the . purge system is in use. 102015 3/4.11 RADIOACTIVE EFFLUENTS 3/4.11.4 TOTAL DOSE C,ONTROLS CY-OC-170-301 Revision 7 Page 44 of 140 3.11.4.1 In accordance with Oyster Creek Technical Specifications 6.8.4.a.10, the annual (calendar year) dose commitment to any MEMBER OFTHE PUBLIC due to radioactive.material in the effluent and direct radiation from the OCGS in the UNRESTRICTED AREA shall be limited to less than or equal to 75 mrem to the thyroid or less than or equalJo 25 mrem to the total body or any other organ. APPLICABILITY:

At all times ACTION: a. With the calculated doses from the release of radioactive materials in liquid or gaseous effluents exceeding twice the limits of CONTROLS 3.11.1.2a, 3.11.1.2b, 3.11.2.2a, 3.11.2.2b, 3.11.2.3a, or 3.11.2.3b, perform an assessment to determine whether the limits of CONTROL 3.11.4.1 have been exceeded.

If such is the case, prepare and submit to the Commission within 30 days, pursuant to Technical Specification 6.9.2, a Special Report that defines the corrective action to be taken to reduce subsequent releases to preverit recurrence of exceeding the above limits and includes the schedule for achieving conformance with the above limits. This Special Report shall include information specified in 1 OCFR20.2203.

If the estimated dose(s) exceeds the above limits, and if the release condition resulting in violation of 40 CFR Part 190 has not already been corrected, the Special Report shall include a request for a variance in accordance with the provisions of 40 CFR Part 190. Submittal of the report is considered a timely request, and a variance is granted until staff action on the request is complete.

b. The provisions of CONTROLS 3.0.3 and 3.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS 4.11.4.1 Cumulative dose contributions from liquid and gaseous effluents shall be determined

in accordance with SURVEILLANCE REQUIREMENT 4.11.1.2, 4.11.2.2, 4.11.2.3, and in accordance with the methodology and parameters in the ODCM Pa_rt II Section 3.0 at least once per year. 4.11.4.2 Cumulative dose contributions from direct radiation from the facility shall be determined in accordance with the methodology and parameters in the ODCM Part II Section 3.2. This requirement is applicable only under conditions set forth in CONTROL 3.11.4, ACTION a. . 102015 CY-OC-170-301 Revision 7 Page 45 of 140 3/4.12 RADIOLOGICAL ENVIRONMENTAL MONITORING 3/4.12.1 MONITORING PROGRAM CONTROLS 3.12.1. In accordance with Oyster Creek Technical Specifications 6.8.4.b, the radiological environmental monitoring program shall be conducted as specified in Table 3.12.1-1.

For specific sample locations see Table E-1. Revisions to the non-ODCM required portions of the program may be implemented at any time. Non-ODCM samples are those taken in addition to the minimum required samples listed in Table 3.12.1-1.

APPLICABILITY:

At all times: ACTION: a. With the radiological environmental monitoring program not being conducted as specified in Table 3.12.1-1, prepare and submit to the Commission, in the Annual Radiological Environmental Operating Report required by Technical Specification 6.9.1.e, a description of the reasons for not conducting the program as required and the plans for preventing a recurrence.

b. With the level of radioactivity as the result of plant effluents in an environmental sampling medium at a specified location exceeding the reporting levels of Table 3.12.1-2 when averaged over any calendar quarter, prepare and submit to the Commission within 60 days of the end of the quarter, pursuant to Technical Specification 6.9.2, a Special Report that identifies the cause(s) for exceeding the limit(s) and defines the corrective actions to be taken to reduce radioactive effluents so that the potential annual dose* to a MEMBER OF THE PUBLIC is less than the calendar year limits of CONTROLS 3.11.1.2, 3.11.2.2, and 3.11.2.3.

When more than one of the radionuclides in Table 3.12.1-2 are detected in the sampling medium, this report shall be submitted if: concentration (1) + concentration (2) + ... l.O reporting level (1) reporting level (2) When radionuclides other than those in Table 3.12.1-2 are detected and are the result of plant effluents, this report shall be submitted if the potential annual dose* to a MEMBER OF THE PUBLIC from all radionuclides is equal to or greater than the calendar year limits of CONTROLS 3.11.1.2, 3.11.2.2, and 3.11.2.3.

This report is not required if the measured level of radioactivity was not the result of plant effluents; however, in such an event, the condition shall be reported and described in the Annual Radiological Environmental Operating Report pursuant to Section 6.1.2.1. *The methodology used to estimate the potential annual dose to a MEMBER OF THE PUBLIC shall be indicated in this report. 102015 CY-OC-170-301 Revision 7 Page 46 of 140 3/4.12 RADIOLOGICAL ENVIRONMENTAL MONITORING 3/4.12.1 MONITORING PROGRAM CONTROLS (Continued)

ACTION: (Continued)

c. If garden vegetation samples are unobtainable due to any legitimate reason, it is NOT ACCEPTABLE to substitute vegetation from other sources. The missed sample will be documented in the annual report, with no further actions necessary.

If a permanent sampling location becomes unavailable, follow Table 3.12.1-1 Table Notation (1) to replace the location.

d. The provisions of CONTROLS 3.0.3, 3.0.4 and Technical Specification 6.9.2 are not applicable.

SURVEILLANCE REQUIREMENTS 4.12.1 The radiological environmental monitoring samples shall be collected pursuant to Table 3.12.1-1 from the specific locations given in Table E-1, and shall be analyzed pursuant to the requirements of Table 3.12.1-1, and the detection capabilities required by Table 4.12.1-1.

102015 CY-OC-170-301 Revision 7 Page 47of140 TABLE 3.12.1-1:

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM EXPOSURE PATHWAY AND/OR SAMPLE NUMBER OF REPRESENTAIVE SAMPLES AND SAMPLE LOCATIONS(1 l SAMPLING AND TYPE AND FREQUENCY COLLECTION FREQUENCY OF ANALYSIS 1. DIRECT RADIATION(2 l Routine monitoring Quarterly Gamma dose quarterly stations with two or more dosimeters placed as follows: An inner ring of stations one in each meteorological sector in the general area of the SITE BOUNDARY (At least 16 locations);

An outer ring of stations, one in each land-base.d meteorological sector in the approximately 6-to 8-km range from the site (At least 14 locations);

and At least 8 stations to be placed in special interest areas such as population centers, nearby residences, schools, and in one or two areas to serve as control stations.

102015 EXPOSURE PATHWAY AND/OR SAMPLE 2. AIRBORNE Radioiodine and Particulates TABLE 3.12.1-1(Cont'd)

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM NUMBER OF REPRESENTATIVE CY-OC-170-301 Revision 7 Page 48 of 140 SAMPLES AND SAMPLING AND TYPE AND FREQUENCY SAMPLE LOCATIONs<

1 l COLLECTION FREQUENCY OF ANALYSIS Samples from 5 locations:

Three samples from close to the SITE BOUNDARY in different sectors of the highest calculated annual average ground-level D/Q One sample from the vicinity of a community having the highest calculated annual average level D/Q; and One sample from a control location, as for example 15-30 km distant and in the least prevalent wind direction (S) Continuous sampler operation with sample collection weekly or more frequently if required by dust loading Radioiodine Canister:

1-131 analysis weekly Particulate Sampler Gross beta vity analysis ing filter change<3 l; Gamma isotopic analysis(4) of composites (by location) quarterly 102015 EXPOSURE PATHWAY AND/OR SAMPLE 3. WATERBORNE

a. Surface b. Ground(5 l c. Drinking TABLE 3. 12.1-1{Cont'd)

RADIOLQGICAL ENVIRONMENTAL MONITORING PROGRAM NUMBER OF REPRESENTATIVE CY-OC-170-301 Revision 7 Page 49 of 140 SAMPLES AND SAMPLING AND TYPE AND FREQUENCY SAMPLE LOCATIONS(1 l COLLECTION FREQUENCY OF ANALYSIS One sample upstream One sample downstream Samples from one or two sources if likely to be affected 1 sam pie of each of 1 to 3 of the nearest water supplies that could be affected by its discharge One sample from a background location Grab sample weekly, Combine into monthly composite.

Grab sample quarterly Grab sample weekly, combine into a 2-week composite if 1-131 analysis Is required; composite monthly otherwise Gamma isotopic and tritium analysis(4 l Gamma isotopic and tritium analysis(4 l Gross beta, gamma isotopic and tritium analysis monthly (4 l(7 l 102015 EXPOSURE PATHWAY AND/OR SAMPLE d. Sediment TABLE 3.12.1-1(Cont'd}

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM NUMBER OF REPRESENTATIVE SAMPLES AND SAMPLE LOCATIONS(1) One sample from downstream area with existing or potential recreational value SAMPLING AND COLLECTION FREQUENCY Semiannually CY-OC-170-301 Revision 7 Page 50 of 140 TYPE AND FREQUENCY OF ANALYSIS Gamma isotopic analysis(4) semiannually 102015 CY-OC-170-301 Revision 7 Page 51 of 140 TABLE 3.12.1-1(Cont'd)

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM NUMBER OF REPRESENTATIVE EXPOSURE PATHWAY SAMPLES AND AND/OR SAMPLE SAMPLE LOCATIONS(1) 4. INGESTION

a. Milk (G) No milking animals SAMPLING AND TYPE AND FREQUENCY COLLECTION FREQUENCY OF ANALYSIS Semimonthly when on pasture; Gamma isotopic (4) and Iodine -131 If milk animals are identified:

monthly at other times semimonthly when animals are on pasture; monthly at other times b. Fish Samples from milking animals in three locations within 5km having the highest dose potential.

If there are none, then one sample from milking animals in each of three areas between 5 an 8 km distant where doses are calculated to be greater than 1 mrem per year. One sample from milking animal at a control location 15 to 30 km distant and in the least prevalent wind direction . One sample of available species consumed by man in plant discharge canal One sample of available species consumed by man not influenced by plant discharge

-Semiannually, when available Gamma isotopic analysis (4) on edible portions 102015 TABLE 3.12.1-1{Cont'd)

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM NUMBER OF REPRESENTATIVE CY-OC-170-301 Revision 7 Page 52 of 140 EXPOSURE PATHWAY SAMPLES AND SAMPLING AND TYPE AND FREQUENCY AND/OR SAMPLE SAMPLE LOCATIONS(1 l c.. Clams One sample of available species consumed by man within the influence of the facility discharge.

d. Vegetation (B) One sample of available species consumed by man not influenced by plant discharge.

3 samples of broad leaf vegetation grown nearest each of two different Off Site locations of highest predicted annual average combined elevated and ground level release D/Q One sample of each of the similar broad COLLECTION FREQUENCY OF ANALYSIS Semiannually, Gamma isotopic when available analysis (4) Monthly during growing season on edible portions.

Gamma isotopic analysis (4) and 1-131 on edible portion. leaf vegetation grown at least 15 to 30 km (9.3-18.6 miles) distant in the least prevalent wind direction.

102015 TABLE 3.12.1-1 (Continued)

TABLE NOTATIONS CY-OC-170-301 Revision 7 Page 53 of 140 1 Specific parameters of distance and direction sector from the centerline of the reactor, and additional description where pertinent, are provided for each and every sample location in Table 3.12.1-1 and Table E-1. Deviations are permitted from the required sampling schedule if specimens are unobtainable due to circumstances such as hazardous conditions, seasonal unavailability, malfunction of automatic sampling equipment, and other legitimate reasons. If specimens are unobtainable due to sampling equipment malfunction, effort shall be made to complete corrective action prior to the end of the next sampling period. All deviations from the sampling schedule shall be documented in the Annual Radiological Environmental Operating Report pursuant to CONTROL 6.1.2.4. It is recognized that, at times, it may not be possible or practicable to continue to obtain samples of the media of choice at the most desired location or time. In these instances suitable specific alternative media and locations may be chosen for the particular pathway in question and appropriate substitutions made within 30 days in the Radiological Environmental Monitoring Program given in the ODCM. Pursuant to Technical specification 6.19, submit in the next Radioactive Effluent Release Report documentation for a change in the ODCM including revised figure(s) and table for the ODCM reflecting the new location(s) with supporting information identifying the cause of the unavailability of samples for the pathway and justifying the selection of the new location(s) for obtaining samples. This applies to changes/deletions/additions of permanent sampling locations.

This does not apply to one-time deviations from the sampling schedule.

In those cases, it is NOT ACCEPT ABLE to substitute sample media from other sources. The missed sample will be documented in the annual report, with no further actions necessary.

2 One or more instruments, such as pressurized ion chamber, for measuring and recording dose rate continuously may be used in place of, or in addition to, integrating dosimeters.

The number of direct radiation monitoring stations has been reduced from the NUREG 1302 recommendation due to geographical limitations; e.g., some sectors are over water and some sectors cannot be reached due to lack of highway access, therefore the number of dosimeters has been reduced accordingly.

3 Airborne particulate sample filters shall be analyzed for gross beta radioactivity 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months or more after sampling to allow for radon and thoron daughter decay. If gross beta activity in air particulate is greater than ten times the yearly mean of control samples, gamma isotopic analysis shall be performed on the individual samples. 4 Gamma isotopic analysis means the identification and quantification of gamma-emitting radionuclides that may be attributable to the effluents from the facility.

5 Groundwater samples shall be taken when this source is tapped for drinking or irrigation purposes in areas where the hydraulic gradient or recharge properties are suitable for contamination.

Extensive studies of geology and groundwater in the vicinity of the OCGS (Reference 21 and 31) have demonstrated that there is no plausible pathway for effluents from the facility to contaminate offsite groundwater, including the local 102015 CY-OC-170-301 Revision 7 Page 54 of 140 drinking water supplies.

Samples of groundwater, including local drinking water wells, are collected in order to provide assurance to the public that these water resources are not impacted.

6 The purpose of this sample is to obtain background information.

If it-is not practical to establish control locations in accordance with the distance and wind direction criteria, other sites which provide valid background data may be substituted 7 1-131 analysis on each composite when the dose calculated for the consumption of the water is greater than 1 mrem per year. If garden vegetation samples are unobtainable due to any legitimate reason (see (1) above), it is NOT ACCEPTABLE to substitute vegetation from other sources. The missed sample will be documented in the annual report, with no further actions necessary.

102015 CY-OC-170-301 Revision 7 Page 55 of 140 TABLE 3.12.1-2:

REPORTING LEVELS FOR RADIOACTIVITY CONCENTRATIONS IN ENVIRONMENTAL SAMPLES-REPORTING LEVELS Surface and Airborne Fish Milk Vegetation Analysis Ground Particulate (pCi/Kg, (pCi/I) (pCi/Kg, Water(pCi/I) and Iodine (pCi/m 3) , wet) wet) H-3 20000* Mn-54 1000 30000 Fe-59 400 10000 Co-58 1000 30000 Co-60 300 10000 Zn-65 300 20000 ' Zr-Nb-95 400 1-131 2** 0.9 3 100 Cs-134 30 10 1000 60 1000 Cs-137 50 20 2000 70 2000 Ba-La-140 200 300 *For drinking water samples (this is the 40 CFR Part 141 value). If no drinking water pathway exists, a value of 30,000 pCi/L may be used. **If no drinking water pathway exists., a value of 20 pCi/L may be used. 102015 CY-OC-170-301 Revision 7 Page 56 of 140 TABLE 4.12.1-1:

DETECTION CAPABILITIES FOR ENVIRONMENTAL SAMPLE ANAL YSIS(i).(2)-LOWER LIMITS OF DETECTION (LLD) (3) Surface and Air Vegetation Sediment Fish, Clams Analysis Ground Particulate (pCi/Kg, (pCi/Kg, dry) and Crabs Water and Air wet) (pCi/Kg, wet) (pCi/I) Iodine (pCi/m 3) Gross Beta 4 0.01 H-3 2000(4) Mn-54 15 130 Fe-59 30 260 Co-58, 60 15 130 Zn-65 30 260 Zr-95 30 Nb-95 15 1-131 1 (4) ' 0.07(5) 60 Cs-134 15 0.05(6) 60 150 130 Cs-137 18 0.06(6) 80 180 150 : La-140 15 Ba-140 60(?) 102015 TABLE 4.12.1-1 (Continued)

TABLE NOTATIONS CY-OC-170-301 Revision 7 Page 57 of 140 1. This list does not mean that only these nuclides are to be considered.

Other peaks that are identifiable, together with those of the above nuclides, shall also be analyzed and reported in the Annual Radiological Environmental Operating Report pursuant to CONTROL 6.1.2.3. 2. Required detection capabilities for dosimeters used for environmental measurements shall be in accordance with the recommendations of Regulatory Guide 4.13. 3. The LLD is defined, for purposes of these CONTROLS as the smallest concentration of radioactive material in a sample that will yield a net count, above system background, that will be detected with 95% probability with only 5% probability of falsely concluding that a blank observation represents a "real" signal. For a particular measurement system, which may include radiochemical separation:

LLD= ___ 4_.6_6_*_Sb

__ _ E

V

2.22

Y

Where: LLD is the "a priori" lower limit of detection as defined above, as picocuries per unit mass or volume, Sb is the standard deviation of the background counting rate or of the counting rate of a blank sample as appropriate, as counts per minute, E is the counting efficiency, as counts per disintegration, V is the sample size in units of mass or volume, 2.22 is the number of disintegrations per minute per Pico curie, Y is the fractional radiochemical yield, when applicable, 'A is the radioactive decay constant for the particular radionuclide (sec-1), and At for environmental samples is the elapsed time between sample collection, or end of the sample collection period, and time of counting (sec). Typical values of E, V, Y, and At should be used in the calculation.

102015 TABLE 4.12.1-1 (Continued)

TABLE NOTATIONS CY-OC-170-301 Revision 7 Page 58 of 140 It should be recognized that the LLD is defined as an priori (before the fact) limit representing the capability of a measurement system and not as posteriori (after the fact) limit for a particular measurement.

Analyses shall be performed in such a manner that the stated LLPs will be achieved under routine conditions.*

Occasionally, background fluctuations, unavoidable small sample sizes, the presence of interfering nuclides, or other uncontrollable circumstances may render these LLDs unachievable.

In such cases, the contributing factors shall be identified and described in the Annual Radiological Environmental Operating Report pursuant Technical Specification 6.9.1.e and Control 6.1.2.6.4.

4. If no drinking water pathway exists, a value of 3000 pCi/L for tritium and 15 pCi/L for iodine-131 may be used. 5. For the air iodine sample 6. For the air particulate sample 7. Ba-140 and La-140 are in equilibrium 102015 CY-OC-170-301 Revision 7 Page 59 of 140 3/4.12 RADIOLOGICAL ENVIRONMENTAL MONITORING 3/4.12.2 LAND USE CENSUS CONTROLS 3.12.2 In accordance with the Oyster Creek Technical Specifications 6.8.4.b, a land use census shall be conducted and shall identify within a distance of 5 miles the location in each of the 16 meteorological sectors of the nearest milk animal, the nearest residence and the nearest garden* of greater than 500 ft 2 producing broad leaf vegetation.

The census shall also identify within a distance of 3 miles the location in each of the 16 meteorological sectors all milk animal and all gardens greater than 500 square feet producing broad leaf vegetation.

APPLICABILITY:

At all times. ACTION: a. With a land use census identifying a location(s) that yields a calculated dose or dose commitment greater than the values currently being calculated in SURVEILLANCE REQUIREMENT 4.11.2.3, identify the new location(s) in the next Radioactive Effluent Release Report, pursuant to Control 6.2.2.4. b. With a land use census identifying a location(s) that yields a calculated dose or dose commitment (via the same exposure pathway) 20 percent greater than at a location from which samples are currently being obtained in accordance with CONTROL 3.12.1, add the new location(s) to the radiological environmental monitoring program within 30 days. The sampling location(s), excluding the control station location, having the lowest calculated dose or dose commitment(s), via the same exposure pathway, may then be deleted from this monitoring.

Pursuant to CONTROL 6.2.2.4, identify the new location(s) in the next Radioactive Effluent Release Report and also include in the report a revised figure(s) and table for the ODCM reflecting the new location(s).

c. The provisions of CONTROLS 3.0.3 and 3.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS 4.12.2 The land use census shall be conducted during the growing season at least once per 12 months using that information that will provide the best results, such as by door survey, visual survey, aerial survey, or by consulting local agriculture authorities.

The results of the land use census shall be included in the Annual Radiological Environmental Operating Report pursuant to CONTROL 6.1.2.2. *Broad leaf vegetation sampling of at least three different kinds of vegetation may be performed at the SITE BOUNDARY in each of two different direction sectors with the highest predicted elevated release D/Q's in lieu of the garden census. Controls for broadleaf vegetation sampling in Table 3.12.1-1, Part 4.c shall be followed, including analysis of control samples. 102015 CY-OC-170-301 Revision 7 Page 60 of 140 3/4.12 RADIOLOGICAL ENVIRONMENTAL MONITORING 3/4.12.3 INTERLABORATORY COMPARISON PROGRAM CONTROLS 3.12.3 In accordance with Oyster Creek Technical Specifications 6.8.4.b.3, analyses shall be performed on radioactive materials supplied as part of an interlaboratory comparison program which has been approved by the Commission.

APPLICABILITY:

At all times. ACTION: a. With analyses not being performed as required above, report the reason and corrective actions taken to prevent a recurrence to the Commission in the Annual Radiological Environmental Operating Report pursuant to CONTROL 6.1.2.6.3.

b.

The provisions of CONTROLS 3.0.3 and 3.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS . 4.12.3 A summary of the results obtained as part of the above-required lnterlaboratory Comparison Program shall be included in the Annual Radiological Environmental Operating Report pursuant to CONTROL 6.1.2.6.3.

102015 CY-OC-170-301 Revision 7 Page 61 of 140 314 .12 RADIOLOGICAL ENVIRONMENTAL MONITORING 3/4.12.4 METEOROLOGICAL MONITORING PROGRAM CONTROLS 3.12.4 The meteorological monitoring instrumentation channels shown in Table 3.12.4.-1 shall be operable.

APPLICABILITY:

At all times. ACTION: a. With less than the minimum required instrumentation channels OPERABLE for more than 7 days, initiate an Issue Report outlining the cause of the malfunction and the plans for restoring the instrumentation to OPERABLE status. b. The provisions of CONTROLS 3.0.3 and 3.0.4 are not applicable.

TABLE 3.12.4-1 METEOROLOGICAL MONITORING INSTRUMENTATION INSTRUMENT ELEVATION

1. Wind Speed a 380 feet b. 150 feet c. 33 feet 2. Wind Direction

a. 380 feet b. 150 feet c. 33 feet 3. AT a. 380-33 b. 150-33 MINIMUM INSTRUMENT OPERABLE 1 1 1 1 1 1 1 1 102015 BASES FOR SECTIONS 3.0 AND 4.0 CY-OC-170-301 Revision 7 Page 62 of 140 CONTROLS AND SURVEILLANCE REQUIREMENTS.

NOTE: The BASES contained in the succeeding pages summarize the reasons for the CONTROLS of Sections 3.0 and 4.0, but are not considered a part of these CONTROLS.

3/4.3 INSTRUMENTATION BASES 3/4.3.3.10 RADIOACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTATION The radioactive liquid effluent instrumentation is provided to monitor and control, as applicable, the releases of radioactive materials in liquid effluents during actual or potential releases of liquid effluents.

The reactor service water system discharge line radioactivity monitor initiates an alarm in the Control Room when the alarm set point is exceeded.

The alarm/trip set points for these instruments shall be calculated and adjusted in accordance with the methodology and parameters in the ODCM to ensure that the alarm/trip will occur prior to exceeding the limits of 10 CFR Part 20. The OPERABILITY and use of this instrumentation is consistent with the requirements of General Design Criteria 60, 63, and 64 of Appendix A to 10 CFR Part 50. 3/4.3.3.11 RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION The radioactive gaseous effluent instrumentation is provided to monitor and control, as applicable, the releases of radioactive materials in gaseous effluents during actual or potential releases of gaseous effluents.

The alarm/trip set points for each of the noble gas monitors shall be calculated and adjusted in accordance with the methodology and parameters in the ODCM. This will ensure the alarm/trip will occur prior to exceeding the limits of 10 CFR Part 20. The radioactive gas monitors for the stack effluent and the Augmented Off gas Building exhaust ventilation have alarms which report in the Reactor Control Room. The OPERABILITY and use of this instrumentation is consistent with the requirements of General Design Criteria 60, 63, and 64 of Appendix A to 10 CFR Part 50. 102015 3/4.11 BASES 3/4.11.1 RADIOACTIVE EFFLUENTS LIQUID EFFLUENTS CY-OC-170-301 Revision 7 Page 63 of 140 3/4. 11.1.1 CONCENTRATION This CONTROL is provided to ensure that the concentration of radioactive materials released in liquid waste effluents to UNRESTRICTED AREAS will be less than the concentration levels specified in 10 CFR Part 20, Appendix B, Table 2, Column 2. This limitation provides additional assurance that the levels of radioactive materials in bodies of water in UNRESTRICTED AREAS will result in exposures within (1) the Section II.A design objectives of Appendix I, 10 CFR Part 50, to a MEMBER OF THE PUBLIC and (2) the limits of 10 CFR Part 20.106(a) to the population.

The concentration limit for dissolved or entrained noble gases is based upon the assumption that Xe-135 is the controlling radioisotope and its concentration limit in air (submersion) was converted to an equivalent concentration in water using the methods described in International Commission on Radiological Protection (ICRP) Publication

2. The value 1 E-8 is the limit for unidentified gross gamma or beta releases as per 10 CFR 20 Appendix B, Table 2, Column 2 "any single radionuclide

... other than alpha or spontaneous fission ... half life greater than 2 hours2.314815e-5 days 5.555556e-4 hours 3.306878e-6 weeks 7.61e-7 months ". This provides operational flexibility while providing reasonable assurance that dose will remain less than 0.1 . The required detection capabilities for radioactive materials in liquid waste*samples are tabulated in terms of the lower limits of detection (LLDs). Detailed discussion of the LLD, and other detection limits can be found in references 25, 26, and 27. Weekly grab samples for Service Water Effluent are composited for monthly tritium and gross alpha analysis and quarterly Sr-89/90 and Fe-55 analysis if activity is detected.

While discharging groundwater via the continuous release remediation pathway, the composite sample will be analyzed daily for principal gamma emitters and tritium. A monthly composite sample is analyzed for gross alpha, Sr-89/90, Fe-55, and Ni-63. While discharging groundwater via the batch release mode remediation pathway, a grab sample is collected from each tank and analyzed for principal gamma emitters and tritium, a composite sample is analyzed monthly for gross alpha, Sr-89/90, Fe-55, and Ni-63. Circulating Water Effluent is not included in Table 4.11.1.1.1-1, Radioactive Liquid Waste Sampling and Analysis Program since the Circulating Water is sampled as part of the Radiological Environmental Monitoring Program, Table 3.12.1-1, 3a, Waterborne, Surface downstream sample. 102015 3/4.11.1.2 DOSE CY-OC-170-301 Revision 7 Page 64 of 140 This CONTROL is provided to implement the requirements of Sections II.A, Ill.A, and IV.A of Appendix I, 10 CFR Part 50. The CONTROL implements the guides set forth in Section II.A of Appendix I. The ACTION statements provide the required operating flexibility and at the same time implement the guides set forth in Section IV.A of Appendix I to assure that the releases of radioactive material in liquid effluents to UNRESTRICTED AREAS will be kept "as low as is reasonably achievable." The dose calculation methodology and parameters in the ODCM implement the requirements in Section Ill.A of Appendix I that conformance with the guides of Appendix I be shown by calculational procedures based on models and data, such that the actual exposure of a MEMBER OF THE PUBLIC through appropriate pathways is unlikely to be substantially underestimated.

The equations specified in the ODCM for calculating the doses due to the actual release rates of radioactive materials in liquid effluents are consistent with the methodology provided in Regulatory Guide 1.109 and Regulatory Guide 1.113. 3/4.11.1.3 LIQUID RADWASTE TREATMENT The OPERABILITY of the liquid radwaste treatment system ensures that this system will be available for use whenever liquid effluents require treatment prior to their release to the environment.

The requirement that the appropriate portions of this system be used, when specified, provides assurance that the release$ of radioactive materials in liquid effluents will be kept "as low as is reasonably achi.evable".

This CONTROL implements the requirements of General Design Criterion 60 of Appendix A to 10 CFR Part 50 and the design objective given in Section 11.D of Appendix I to 10 CFR Part 50. The specified limits governing the use ofappropriate portions of the liquid radwaste treatment system were specified as a suitable fraction of the dose design objectives set forth in Section II.A of Appendix I, 10 CFR Part 50, for liquid effluents.

Figure D-1-1a, Liquid Radwaste Treatment Chem Waste and Floor Drain System and Figure D-1-1 b, *Liquid Radwaste Treatment

-High Purity and Equipment Drain System provides details of the Liquid Radwaste Treatment system. 3/4.11.2 GASEOUS EFFLUENTS 3/4.11.2.1 DOSE RA TE This CONTROL is provided to ensure that the dose at any time at and beyond the SITE BOUNDARY from gaseous effluents will be within the annual dose limits of 10 CFR Part 20 to UNRESTRICTED AREAS. The annual dose limits are the doses associated with the concentrations of 10 CFR Part 20, Appendix B, Table 2, Column 1. These limits provide reasonable assurance that radioactive material discharged in gaseous effluents will not result in the exposure of a MEMBER OF THE PUBLIC in an UNRESTRICTED AREA either within or outside the SITE BOUNDARY, to annual average concentrations exceeding the limits specified in Appendix B, Table 2 of 10 CFR Part 20. For MEMBERS OF THE PUBLIC who may at times be within the SITE BOUNDARY, the occupancy of the individual will usually be sufficiently low to 102015 CY-OC-170-301 Revision 7 Page 65 of 140 compensate for any increase in the atmospheric diffusion factor above that for the SITE BOUNDARY.

Examples of calculations for such MEMBERS OF THE PUBLIC with the appropriate occupancy factors shall be given in the ODCM. The specified release rate limits restrict, at all times, the corresponding gamma and beta dose rates above background to a MEMBER OF THE PUBLIC at or beyond the SITE BOUNDARY to less than or equal to 500 mrem/year to the total body or to less than or equal to 3000 mrem/yr to the skin. These release rate limits also restrict, at all times, the corresponding thyroid dose rate above background to a child via the inhalation pathway to less than or equal to 1500 mrem/year.

The required detection capabilities for radioactive materials in liquid waste samples are tabulated in terms of the lower limits of detection (LLDs). Detailed discussion of the LLD, and other detection limits can be found in references 2p, 26 and 27. Tritium is sampled quarterly for gaseous effluents.

Based on the consistency of the data from the quarterly sampling, the sampling frequency is adequate.

3/4.11.2.2 DOSE -NOBLE GASES This CONTROL is provided to implement the requirements of Section 11.B, Ill.A and IV.A of Appendix I, 10 CFR Part 50. The CONTROL implements the guides set forth in Section 11.B of Appendix I. The ACTION statements provide the required operating flexibility and at the same time implement the guides set forth in Section IV.A of

Appendix I to assure that the releases of radioactive material in gaseous effluents will be kept "as low as is reasonably achievable." The SURVEILLANCE REQUIREMENTS implement the requirements in Section Ill.A of Appendix I that conformance with the guides of Appendix I be shown by calculational procedures based on models and data such that the actual exposure of a MEMBER OF THE PUBLIC through appropriate pathways is unlikely to be substantially underestimated.

The dose calculation methodology and parameters established in the ODCM for calculating the doses due to the actual release rates of radioactive noble gases in gaseous effluents are consistent with the methodology provided in Regulatory Guide 1.109 and Regulatory Guide 1.111. The ODCM equations provided for determining the air doses at and beyond the SITE BOUNDARY are based upon the historical average atmospheric conditions.

3/4.11.2.3 DOSE-IODINE-131, IODINE-133, TRITIUM, AND RADIONUCLIDES IN PARTICULATE FORM This CONTROL is provided to implement the requirements of Section 11.C, Ill.A and IV.A of Appendix I, 10 CFR Part 50. The CONTROLS are the guides set forth in Section 11.C of Appendix I. The ACTION statements provide the required operating flexibility and at the same time implement the guides set forth in Section IV.A of Appendix I to assure that the releases of radioactive material in gaseous effluents to UNRERSTRICTED AREAS will be kept "as low as is reasonably achievable." The ODCM calculational methods specified in SURVEILLANCE REQUIREMENTS implement the requirements in Section Ill.A of Appendix I that conformance with the

gui<;les of Appendix I be shown by calculational procedures based on models and data 102015 CY-OC-170-301 Revision 7 Page 66 of 140 such that the actual exposure of a MEMBER OF THE PUBLIC through appropriate pathways is unlikely to be substantially underestimated.

The ODCM calculational methodology and parameters for calculating the doses due to the actual release rates of the subject materials are* consistent with the methodology provided in Regulatory Guide 1.109, and Regulatory Guide 1.111. These equations also provide for determining the actual doses based upon the historical average atmospheric conditions.

Th.e release rate controls for iodine-131, iodine-133, tritium, and radionuclides in particulate form with half-life greater than 8 days are dependent on the existing radionuclide pathways to man, in the areas at and beyond the SITE BOUNDARY.

The pathways that were examined in the development of these calculations were: 1) individual inhalation of airborne radionuclides, 2) deposition of radionuclides onto green leafy vegetation with subsequent consumption by man, 3) deposition onto grassy areas where milk animals and meat producing animals graze with consumption of the milk and meat by man, and 4) deposition on the ground with subsequent exposure of man. 3/4.11.2.4 GASEOUS RADWASTE TREATMENT SYSTEM The OPERABILITY of the AUGMENTED OFF GAS TREATMENT SYSTEM (AOG) ensures that the system will be available for use whenever gaseous effluents require treatment prior to release to the environment The requirement that the appropriate portions of these systems be used, when specified, provides reasonable assurance that the releases of radioactive materials in gaseous effluents will be kept "as low as is reasonably achievable." This CONTROL implements the requirements of General Design Criterion 60 of Appendix A to 10 CFR Part 50, and the design objectives given in Section 11.D of Appendix I to 10 CFR Part 50. The specified limits governing the use of appropriate portions of the systems were specified as a suitable fraction of the dose design objectives set forth in Section 11.B and 11.C of Appendix I, 10 CFR Part 50, for gaseous effluents.

Figure D-2-1, Gaseous Radwaste Treatment

-Augmented Off gas System, Figure D-2-2, Ventilation System provide details of the Augmented Off Gas Treatment System and Figure D-2-3, AOG Ventilation System. 3/4.11.4 TOTAL DOSE This CONTROL is provided to meet the dose limitations of 40 CFR Part 190 that have now been incorporated into 10 CFR Part 20 by 46 FR 18525. The CONTROL requires the preparation and submittal of a Special Report whenever the calculated doses from plant radioactive effluents exceed 25 mrem to the total body or any organ, except the thyroid, which shall be limited to less than or equal to 75 mrem. It is highly unlikely that the resultant dose to a MEMBER OF THE PUBLIC will exceed the dose limits of 40 CFR Part t90 if the doses remain within twice the dose design objectives of .. Appendix I, and if direct radiation doses from the unit, including outside storage tanks, etc. are kept small. The Special Report will describe a course of action that should result in the limitation of the annual dose to a MEMBER OF THE PUBLIC to within the 40 CFR Part 190 limits. For purposes of the Special Report, it may be assumed that the dose commitment to the MEMBER OF THE PUBLIC from other uranium fuel cycle sources is negligible.

If the dose to any MEMBER OF THE PUBLIC is estimated to exceed the requirements of 40 CFR Part 190, the Special Report with a request for a 102015 CY-OC-170-301 Revision 7 Page 67 of 140 variance (provided the release conditions resulting in violation of 40 CFR Part 190 have not already been corrected), in accordance with the provisions of 40 CFR Part 190 and 10 CFR Part 20, is considered'to be a timely request and fulfills the requirements of 40 CFR Part 190 until NRC staff action is completed.

The variance only relates to the limits of 40 CFR Part 190, and does not apply in any way to the other requirements for dose limitation of 10 CFR Part 20, as addressed in CONTROLS 3.11.1.1 and 3.11.2.1.

An individual is not consitjered a MEMBER OF THE PUBLIC during any period in which he/she is engaged in carrying out any operation that is part of the nuclear fuel cycle. 102015 3/4.12 BASES RADIOLOGICAL ENVIRONMENTAL MONITORING CY-OC-170-301 Revision 7 Page 68 of 140 3/4.12.1 MONITORING PROGRAM The radiological environmental monitoring program required by this CONTROL* provides representative measurements of radiation and of radioactive materials in those exposure pathways and for those radionuclides that lead to the highest potential radiation exposures of MEMBERS OF THE PUBLIC resulting from the station operation.

This monitoring program implementsSection IV.B.2 of Appendix I to 10 CFR Part 50 and thereby supplements the radiological effluent monitoring program by verifying that the measurable concentrations of radioactive materials and levels of radiation are not higher than expected on the basis of the effluent measurements and the modeling of the environmental exposure pathways.

Guidance for this monitoring program is provided by the Radiological Assessment Branch Position on Environmental Monitoring, Revision 1, November 1979. The required detection capabilities for environmental sample analyses are tabulated in terms of the lower limits of detection (LLDs). The LLDs required by Table 4.12.1-1 are considered optimum for routine environmental measurements in industrial laboratories.

It should be recognized that the LLD is defined as an .§. priori (before the fact) limit representing the capability of a measurement system and not as an .§. posteriori (after the fact) limit for a particular measurement.

Detailed discussion of the LLD, and other detection limits in references 25, 26, and 27. Site-specific research, which included the installation of a groundwater monitoring well network, has demonstrated that the groundwater pathway is not a potential pathway to man from the OCGS. The surface water into which the OCGS discharges is a marine estuary containing saline water that is not used as drinking water or irrigation water by man. 3/4.12.2 LAND USE CENSUS This CONTROL is provided to ensure that changes in the use of areas at arid beyond the SITE BOUNDARY are identified and that modifications to the radiological environmental monitoring program are made if required by the results of this census. The best information from the door-to-door survey, from aerial survey, from visual survey or consulting with local agricultural authorities shall be used. This census satisfies the requirements of Section IV.B.3 of-Appendix I to 10. CFR Part 50. Restricting the census to gardens of greater than 50 m 2 (500 ft 2) provides assurance that significant exposure pathways via leafy vegetables will be identified and monitored since a garden of this size is the minimum required to produce the quantity (26 kg/year) of leafy vegetables assumed in Regulatory Guide 1 .109 for consumption by a child. To determine this minimum garden size, the following assumptions were " made: 1) 20% of the garden was used for growing broad leaf vegetation (i.e., similar to . lettuce and cabbage), and 2) a vegetation yield of2 kg/m 2. 102015 3/4.12 BASES RADIOLOGICAL ENVIRONMENTAL MONITORING CY-OC-170-301 Revision 7 Page 69 of 140 3/4.12.3 INTERLABORATORY COMPARISON PROGRAM The requirement for participation in an approved lnterlaboratory Comparison Program is provided to ensure that independent checks on the precision and accuracy of the measurements of radioactive material in environmental sample matrices are performed as part of the quality assurance program for environmental monitoring in order to demonstrate that the results are valid for the purposes of Section IV.B.2 of Appendix I to 10 CFR Part 50.5.0 5.0 DESIGN FEATURES I SITE MAP (Provided FOR INFORMATION ONLY. Technical Specifications are controlling.)

5.1 Site map which will allow identification of structures and release points shall be as shown in Figure E-4. 102015 CY-OC-170-301 Revision 7 Page 70 of 140 6.0 ADMINISTRATIVE CONTROLS 6.1 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT (AREOR) 6.1.1 In accordance with Oyster Creek Technical Specifications 6.9.1.e, a routine radiological environmental operating report covering the operation of the unit during the previous calendar year shall be submitted prior to May 1 of the following year. 6.1.2 The Annual Radiological Environmental Operating Reports shall include: 6.1.2.1 Summaries, interpretations, and an analysis of trends of the results of the radiological environmental surveillance activities (Radiological Environmental Monitoring Program -REMP) for the report period. This will include a comparison with preoperational studies, with operational controls (as appropriate), and with previous environmental surveillance reports, and an assessment of the observed impacts of the plant operation on the environment.

6.1.2.2 The reports shall also include the results of land use censuses required by CONTROL 3.12.2. If harmful effects or evidence .of irreversible damage are detected by the monitoring, the report shall provide an analysis of the problem and a planned course of action to alleviate the problem. 6.1.2.3 The Annual Radiological Environmental Operating Reports shall include summarized and tabulated results similar in format to that in Regulatory Guide 4.8, December 1975 of all the radiological environmental samples taken during the report period. 6.1.2.4 Deviations from the sampling program identified in CONTROL 3.12.1 shall be reported.

6.1.2.5 In the event that some individual results are not available for inclusion with the report, the report shall be submitted noting and explaining the reasons for the missing results. The missing data shall be submitted as soon as possible in a supplementary report. 6.1.2.6 The reports shall also include the following:

a. A summary description of the radiological environmental monitoring Program; b. Map(s), covering sampling locations, keyed to a table giving distances and directions from the reactor; c. The results of licensee participation in the Inter-laboratory Comparison Program, as required by CONTROL 3.12.3; d. Identification of environmental samples analyzed when the analysis instrumentation was not capable of meeting the detection capabilities in Table 4.12.1-1.

102015 CY-OC-170-301 Revision 7 Page 71 of 140 6.2 ANNUAL ROUTINE RADIOACTIVE EFFLUENT RELEASE REPORT (ARERR) 6.2.1 Routine radioactive effluent release reports covering the operation of the unit shall be submitted prior to May 1 of each year and in accordance with the requirements of 10CFR50.36a and section IV.B.1of10CFR 50 Appendix I. 6.2.2 The Radioactive Effluent Release Report shall include: 6.2.2.1 A summary of the quantities of radioactive liquid and gaseous effluents and solid waste released from the unit as outlined in Regulatory Guide 1.21. "Measuring, Evaluating, and Reporting Radioactivity in Solid Wastes and Releases of Radioactive Materials in Liquid and Gaseous Effluents from Light-Water-Cooled Nuclear Power Plants," Revision 1, June 1974, with data summarized on a quarterly basis following the format of Appendix B thereof. 6.2.2.2 An annual summary of hourly meteorological data collected over the previous year. This annual summary may be in the form of joint frequency distributions of wind speed, wind direction, and atmospheric stability.

Alternatively, summary meteorological data may be retained and made available to the NRC upon request. 6.2.2.3 An assessment of the radiation doses due to the radioactive liquid and gaseous effluents released from the unit or station during the previous calendar year. The historical annual average meteorology or the meteorological conditions concurrent with the time of release of radioactive materials in gaseous effluents (as determined by sampling frequency and measurement) shall be used for determining the gaseous* pathway doses. The assessment of radiation doses shall be performed in accordance with this OFF SITE DOSE CALCULATION MANUAL (ODCM). 6.2.2.4 Identify those radiological environmental sample parameters and locations where it is not possible or practicable to continue to obtain samples of the media of choice at the most desired location or time. In addition, the cause of the unavailability of samples for . the pathway and the new location(s) for obtaining replacement samples should be identified.

The report should also include a revised figure(s) and table(s) for the ODCl\ll reflecting the new location(s).

* . 6.2.2.5 An assessment of radiation doses to the likely most exposed MEMBER OF THE PUBLIC from reactor releases and other nearby uranium fuel cycle sources (including doses from primary effluent pathways and direct radiation) for the previous calendar year to show conformance with 40 CFR Part 190, Environmental Radiation Protection Standards for Nuclear Power Operation.

The assessment of radiation doses shall be performed in accordance with this OFF SITE DOSE CALCULATION MANUAL (ODCM) Part II Sections 1.5, 2.4, 2.5 and 3.2. 6.2.2.6 The Radioactive Effluent Release Reports shall include the following information for each class of solid waste (as defined by 10 CFR Part 61) shipped Off Site during the report period (see Figure D-1-2): a. Total volume shipped b. Total curie quantity (specify whether determined by measurement or estimate), c. Principal radionuclides (specify whether determined by measurement or estimate), 102015 CY-OC-170-301 Revision 7 Page 72 of 140 d. Type of waste (e.g., dewatered spent resin, compacted dry waste, evaporator bottoms) 6.2.2.7 Unplanned releases from the site to UNRESTRICTED AREAS of radioactive materials in gaseous and liquid effluents on a quarterly basis. 6.2.2.8 Changes to the PROCESS CONTROL PROGRAM (PCP) 6.2.2.9 Changes to the OFF SITE DOSE CALCULATION MANUAL (ODCM) in the form of a complete, legible copy of the ODCM. 6.3 RESPONSIBILITIES:

6.3.1 Chemistry

I Radwaste -Responsible for: 6.3.1.1 Implementing approval.

6.3.1.2 Compliance with specifications regarding routine dose assessment.

6.3.1.3 Radiological Environmental Monitoring Program 6.3.1.4 Technical consultation and review 6.3.2

Operations

-Responsible for compliance with specifications regarding operation of the OCGS. 6.3.3 Engineering

-Responsible for compliance with specifications regarding set point determination and implementation

6.3.4 Radiological

Engineering

-Responsible for technical consultation and review. 102015 PART II -CALCULATIONAL METHODOLOGIES CY-OC-170-301 Revision 7 Page 73 of 140 1.0 LIQUID EFFLUENTS

1.1 RADIATION

MONITORING INSTRUMENTATION AND CONTROLS The liquid effluent monitoring instrumentation and controls at Oyster Creek for controlling and monitoring normal radioactive material releases in accordance with the Oyster Creek Radiological Effluent Technical Specifications are summarized as follows: Reactor Building Service Water Effluent -The Reactor Building Service Water Effluent Line Monitor provides an alarm function only for releases into the environment.

Liquid radioactive waste flow diagrams are presented in Figures D-1-1 a, D-1-1 b, and D-1-1 c. 1.2 LIQUID EFFLUENT MONITOR SET POINT DETERMINATION Per the requirements of CONTROL 3.3.3.10, alarm set points shall be established for the liquid monitoring instrumentation to ensure that the release concentration limits of CONTROL 3.11.1.1 are met (i.e., the concentration of radioactive material released in liquid effluents to UNRESTRICTED AREAS at the U.S. route 9 bridge over the discharge canal shall not exceed the concentrations specified in 10 CFR 20 Appendix B. Table 2, Column 2, for radionuclides and 2E-04 µCi/ml for dissolved or entrained noble gases). 1.2.1 LIQUID EFFLUENT MONITORS Where: The set points for the liquid effluent monitors at the Oyster Creek Generating Station are determined by the following equation:

s A F2 -F-'LE-C-g -F-1 + BKG S =radiation monitor alarm set point (cpm) A =activity concentration

(µCi/ml) of sample in laboratory: A = LCi g = the primary conversion factor for the instrument

-the ratio of effluent radiation monitor counting rate to laboratory activity concentration in a sample of liquid (cpm per µCi/ml). F1 =flow in the batch release line (e.g. gal/min).

Value not greater than the discharge line flow alarm maximum set point. 102015 CY-OC-170-301 Revision 7 Page 74of140 F2 =flow in the discharge canal (e.g. gal/min).

Value not less than the discharge canal minimum flow. BKG =Monitoring instrument background (cpm) FLEC =fraction or multiple of unrestricted area LEG in aqueous effluent based on sample analysis.

FLEC is the ratio between the LECi and Ci. FLEC is unitless.

For example: LEG for Co-60 is 3E-6 µCi/ml. If the concentration in a expected release is 6E-6 µCi/ml; then FLEC is 6E-6/3E-6

= 2. The term" _A_ represents the count rate of a solution having the same nuclide FLEC distribution as the sample and the LEG of that mixture. Ci =concentration of radionuclide i in.effluent, i.e., in a liquid radwaste sample tank, in reactor building service water (µCi/ml).

LECi =the unrestricted area liquid effluent concentration (LEG) of radionuclide i, i.e., 10 CFR Where: 20, Appendix B, Table 2, Column 2 quantity for radionuclide i (µCi/ml).

In the event gross radioactivity analysis alone is used to determine the radioactivity in an effluent stream or batch, FLEC is C/1 E-8 (see 4.11.1.1.1

), C =the gross radioactivity concentration in effluent (µCi/ml).

1 E-8 =the unrestricted area LEG for unidentified radionuclides

(µCi/ml) from 4.11.1.1.1.

If the gross activity concentration, C, is below the lower limit of detection for gross activity, the value, 1 E-8 µCi/ml, or the equivalent counting rate (cpm/ml) may be substituted for the factor _A_ FLEC _A_ = 1 E-8 µCi/ml FLEC . 1.2.2 SAMPLE RESULT SET POINTS Usually, when the concentration of specific radionuclides is determinable in a sample(s), i.e., greater than the LLD, the alarm/trip set point of each liquid effluent radioactivity monitor is based upon the measurement of radioactive material in a batch of liquid to be released or in a continuous aqueous discharge.

102015

1.2.3 ASSUMED

DISTRIBUTION SET POINTS CY-OC-170-301 Revision 7 Page 75 of 140 Alternatively, a radionuclide distribution that represents the distribution expected to be in the effluent if the concentration were high enough to be detectable, i.e., greater than the LLD, may be assumed. The representative distribution may be based upon past measurements of the effluent stream or upon a computed distribution.

1.3 BATCH

RELEASES A sample of each batch of liquid radwaste is analyzed for 1-131 and other principal gamma emitters or for gross beta or gross gamma activity before release. The result of the analysis is used to calculate the trip set point of the radioactivity monitor on the liquid radwaste effluent line to apply to release of the batch. 1.4 CONTINUOUS RELEASES The Reactor Building.

Service Water Effluent is sampled and analyzed weekly for 1-131, other principal gamma emitters.

Results of analyses for the preceding week or for a period as long as the preceding 3 months are used to calculate the alarm/trip set point of the corresponding effluent radioactivity monitor in order to determine a representative value. In each case, whether batch or continuous, the monitor alarm/trip set point may be set at lower activity than the calculated set point. 1.5 LIQUID EFFLUENT DOSE CALCULATION

-10 CFR 50 Doses resulting from the release of radioiodines and particulates must be calculated to show compliance with Appendix I of 1 OCFR50. Calculations will be performed at least monthly for all liquid effluents as stated in SURVEILLANCE REQUIREMENT 4.11; 1.2 and SURVEILLANCE REQUIREMENT 4.11.1.3.1 to verify that the dose to MEMBERS OF THE PUBLIC is maintained below the limits specified in CONTROL 3.11.1.2 The maximum dose to an individual from radioiodines, tritium, and radioactive particulates with half-lives of greater than eight days in liquid effluents released to unrestricted areas is determined as described in Reg. Guide 1.109. Environmental pathways that radioiodine, tritium, and particulates in liquid effluent follow to the maximally exposed MEMBER OF THE PUBLIC are assumed to be: exposure to shoreline deposits, ingestion of fish, and ingestion of shellfish.

To assess compliance with CONTROL 3.11.1.2, the dose due to radioactive iodine, tritium, and particulates in liquid effluent is calculated tq a person at the Route 9 bridge who consumes fish and shellfish harvested at that location.

102015 CY-OC-170-301 Revision 7 Page 76 of 140 1.5.1 MEMBER OF THE PUBLIC DOSE-LIQUID EFFLUENTS CONTROL 3.11.1.2 limits the dose or dose commitment to MEMBERS OF THE PUBLIC from radioactive materials in liquid effluents from Oyster Creek Generating Station to those* listed in Table 1.5.1-1. TABLE 1.5.1-1 LIQUID PATHWAY DOSE LIMITS During Any Calendar Quarter 1.5 mrem to total body 5.0 mrem to any organ During Any Calendar Year < 3.0 mrem to total body 10.0 mrem to any organ Per the SURVEILLANCE REQUIREMENTS of 4.11.1.2, the following calculation methods shall be used for determining the dose or dose commitment due to the liquid radioactive effluents from Oyster Creek. Applicable liquid pathways to man for Oyster Creek include shoreline exposure, and ingestion of saltwater fish and shellfish.

The receptor location is provided in Table A-4. 1.5.2

SHORELINE DEPOSIT DOSE Where: The shoreline exposure pathway dose is calculated generally in the form (based on Reg. Guide 1.109): Rapj = 110000 UapWM L QiTiDaipj (1-exp( -}dTb )) F ; 110000 = a constant that accounts for time and flow conversions Rapj =the annual dose to organ j (including the total body), through pathway p, to age group a Uap = the age dependent usage factor for the specific pathway. Usage factors for shoreline exposure are residence time on the shoreline (hours). Usage factors are provided in Reg. Guide 1.109 Table E-5. Usage factors specifically selected for Oyster Creek are presented in Table B-1. W = the shore width factor. This adjusts the infinite.

plane gamma or beta dose factors for. . the finite size and shape of the shoreline.

Different factors apply to different bodies of water. A factor of 0.1 is used for OC for 'discharge canal bank'. M = the recirculation factor. The recirculation factor is a multiplier of 3. 76 to account for recirculation of discharge water back into the intake. Although this occurs infrequently, it is assumed to occur for each liquid release. 102015 CY-OC-170-301 Revision 7 Page 77 of 140 F = the flow rate in the discharge canal in cubic feet per second Qi = the activity of the ith isotope in the release in curies Ti = the half life of the ith isotope in days Daipj =the age a, isotope i, pathway p, and organ j, specific dose conversion factor. Pathway, isotope, age, and organ specific dose factors are obtained from Regulatory Guide 1.109 Appendix E, Tables E-6 through E-14 Ai = the decay constant of the ith isotope in years Tb = the long term buildup time, assumed to be 30 years Note: Ai and Tb can use any time units as long as they are both the same. No transit delay (Tp from Reg. Guide 1.109) is assumed. 1.5.3 SHORELINE DOSE EXAMPLE 1 The following provides an example of the liquid dose calculation:

Initial parameters:

Canal flow rate 1 E6 gpm (typical of normal full power operation)

Release: 10,000 gallons of water at 1 E-3 µCi/ml Co-60 Problem: calculate shoreline whole body dose Uap = 67 (teenager) hours w =0.1 M = 3.76 F = 2228 [1E6 gpm *3785 ml I gal I (60 sec/min* 28316 ml/ft 3) = 2228 CFS] Qi = 0.03785 Ci [1E-3uCi/ml

10000gal

3785ml/gal

/ 1E6 uCi/Ci = 0.03785 Ci] Ti = 1920 [5.27 years*365 days/yr = 1.92E3 days) Ai = 1.31 E-1 [0.693 / (5.27 yrs)] Tb = 30 years Daipj = 1. 7E-8 mrem/hr I pCi/m 2 Gamma dose factor Calculate Rapj for a= Teen, j =total body, p =shoreline dose for one isotope Rap}= l l0000 67*0.l *3*76 ,L0.03785*1920*1.7 E-8*(1-exp(-1.3£-1

30)) . 2228 i Rap}= 1.5 lE -3 mrem: teen: wholebody 102015 CY-OC-170-301 Revision 7 Page 78 of 140 1.5.3.1 SHORELINE DOSE EXAMPLE 2 The following provides an example of the liquid dose calculation for groundwater remediation discharge:

Initial parameters:

Canal flow rate 1 E6gpm (typical of normal full power operation)

Release: 50 gpm for 7 days at 1 E-8 µCi/ml Co-60 Problem: Calculate shoreline whole body dose Uap = 67 (teenager) hours w =0.1 M = 3.76 F = 2228 [1 E6 gpm *3785 ml I gal I (60 sec/min

28316 ml/ft 3) = 2228 CFS] Qi = 1.91 E-5 Ci [1 E-08 µCi/ml*50gpm*7days*24hr/day*60 min/hr*3785ml/gal/1 E+6 µCi/Ci] Ti = 1920 [5.27 years*365 days/yr= 1.92E+03 days) A.i = 1.31 E-1 [0.693 / (5.2Tyrs)]

Tb = 30 years Daipj = 1. 7E-8 mrem/hr I pCi/m 2 External Dose factor Calculate Rapj for a= Teen, j =total body, p =shoreline dose for one isotope Rapj = 110000 67*0.l

30)) 2228 i Rap}= 7.60E-7 mrem:teen:wholebody

1.5.4 INGESTION

DOSE -LIQUID Where: Ingestion dose pathway calculations are similar to those for the shoreline dose, with minor changes in constants, removal of the shore width factor, and inclusion of the bioaccumulation factor: Rap} = 1100 UapM L QiBipDaipj F Bip = the stable element bioaccumulation factor for pathway p for the ith isotope No transit delay is assumed Pathway, isotope, age, and organ specific dose factors are obtained from Regulatory Guide 1.109 Appendix E Tables E-7 through E-14. Bioaccumulation factors are 102015 CY-OC-170-301 7 Page 79 of 140 provided in Reg. Guide 1.109 Table A-1. Usage factors are provided in Reg. Guide 1.109 Table E-5. Usage factors specifically selected for Oyster Creek are presented in Table B-1. The radionuclides included in the periodic dose assessment per the requirements of CONTROL 3/4.11.1.2 are those as identified by gamma spectral analysis of the liquid waste samples collected and analyzed per the requirements of CONTROL 3/4.11.1.1, Table 4.11.1.1.1-1.

Radionuclides requiring radiochemical analysis (e.g., Sr-89 and Sr-90) will be added to the dose analysis at a frequency consistent with the required minimum analysis frequency of Table 4.11.1.1.1-1.

1.5.5 INGESTION

DOSE CALCULATION EXAMPLE 1 ' The following provides an example of the liquid dose calculation:

Initial parameters:

Canal flow rate 1 E6 gpm (typical of normal full power operation)

Release: 10000 gallons of water at 1 E-3 µCi/ml Co-60 Problem: calculate teen whole body dose from saltwater fish ingestion Rapj = 1100 UapM L QiBipDaipj F Uap = 16 (teenager)

Kg M = 3.76 F = 2228 [1 E6 gpm *3785 ml I gal I (60 sec/min

28316 ml/ft 3) = 2228 CFS] Qi = 0.03785 Ci [1 E-3uCi/mL

1 OOOOgal

3785ml/gal / 1 E6 uCi/Ci = 0.03785 Ci] Bip = 100 . Daipj = 6.33E-6 mrem I pCi Calculate Rapj for a= Teen, j =total body, p =fish ingestion dose for one isotope Rapj = 1100 16

3 *76 L 0.03785

100

6.33 E -6 2228 i Rapj = 7 .12 E -4 mrem : teen : whole body

102015 CY-OC-170-301 Revision 7 Page 80 of 140 1.5.5.1 INGESTION DOSE CALCULATION EXAMPLE 2 The following provides an example of the liquid dose calculation for ground water remediation discharge:

Initial parameters:

Canal flow rate 1 E6 gpm (typical of normal full power operation)

Release: 50 gpm for 7 days at 700,000 pCi/I H-3 Problem: calculate teen whole body dose from saltwater fish ingestion Rapj = 1100 UapM L f4iBipDaipj F i Uap = 16 (teenager)

Kg M = 3.76 . F = 2228 [1 E6 gpm *3785 ml I gal I (60 sec/min

28316 milft 3) = 2228 CFS] Qi = 1.34 Ci [7E+5 pCi/1*50gpm*7days*24hr/day*60 min/hr*3.

785 I/gal/ 1 E+12 pCi/Ci] Bip =.0.90 (Regulatory Guide 1.109, TableA-1)

Daipj = 1.06E-07 mrem I pCi Calculate Rapj for a= Teen, j =total body, p =fish ingestion dose for one isotope Rapj = 1100 16*3*76 L1.34

0.9

l.06E...:.

7 . 2228 i . Rapj = 3 .80 E -6 mrem : teen : wholebody

1.5.6 PROJECTED

DOSE -LIQUID The projected doses in a 31 day period are equal to the calculated doses from the current 31 day period. 1.6 REPRESENTATIVE SAMPLES . A sample should be representative of the bulk stream or volume of effluent from which it is taken. Prior to sampling, large volumes of liquid waste should be mixed in as short a time interval as practicable to assure that any sediments or particulate solids are distributed uniformly in the waste mixture. Recirculation pumps for liquid waste tanks (collection or sample test tanks) should be capable of recirculating at a rate of not less than two tank volumes in eight hours. Minimum recirculation times and methods of recirculation are controlled by specific plant procedures.

102015

2.0 GASEOUS

EFFLUENTS CY-OC-170-301 Revision 7 Page 81 of 140 2.1 RADIATION MONITORING INSTRUMENTATION AND CONTROLS The gaseous effluent monitoring instrumentation and controls at Oyster Creek for controlling and monitoring normal radioactive material releases in accordance with the Radiological Effluent CONTROLS are summarized as follows: (1) Main Stack The main stack receives normal ventilation flow from the reactor building, new radwaste, old radwaste, process discharge flow from the augmented off gas system (AOG), condenser off gas flow if AOG is not in service, and normal ventilation flow from portions of the turbine building, predominantly the condenser bay area. Reactor building and turbine building flow is not normally processed or filtered.

Reactor Building flow may be manually or automatically directed through the Standby Gas Treatment System (SBGTS) which has particulate and charcoal filtration.

Off gas flow is processed through AOG or through a 30-minute delay pipe prior to release. Flow from the 'new' and 'old' radwaste buildings is HEPA filtered.

Releases through the main stack are monitored for noble gases using the RAGEMS I system and sampled for iodine, particulates and tritium. The plant stack is considered to be a true elevated release point. (2) Turbine Building Vent The Turbine building vent is monitored for noble gases by the RAGEMS II system and sampled for iodine, particulates and tritium. It discharges on the west side of the turbine building approximately at roof height and is considered to be a ground level release. It* ventilates the turbine floor and other areas of the turbine building.

Flow through this release point is not filtered.

(3) Feed Pump Room Vent The feed pump room vent is monitored by RAGEMS II. It discharges on the east side of the turbine building below roof height and is considered to be a ground level release. It ventilates the reactor feed pump room. Flow through this release point is not filtered.

(4) Augmented Off Gas Building Vent Off gas Building HVAC is released through a ground level release from the building.

Off Gas process flow is not released through the building ventilation, but is routed to the stack plant. A ventilation monitoring system monitors for noble gas and samples for particulate and iodine. 102015 CY-OC-170-301 Revision 7 Page 82 of 140 (5) Isolation Condensers The isolation condensers are a ground level release. The predominant isotope through this potential release point is tritium as a *consequence of the forced evaporation of condensate transfer water when the isolation condensers are initiated.

Releases are neither monitored nor is the release process flow sampled. Releases of tritium are evaluated based on liquid samples of the input and the volume used. Gaseous radioactive waste flow diagrams with the applicable, associated radiation monitoring instrumentation controls are presented in Figures D-2-1 and D-2-2. 2.2 GASEOUS EFFLUENT MONITOR SET POINT DETERMINATION

2.2.1 PLANT

VENT Where: s h Ci 1.06 DFSi f Per the requirements of CONTROL 3.3.3.11, alarm set points shall be established for the gaseous effluent monitoring instrumentation to ensure that the release rate of noble gases does not exceed the limits of CONTROL 3.11.2.1, which corresponds to a dose rate at the SITE BOUNDARY of 500 mrem/year to the total body or 3000 mrem/year to the skin. Based on a grab sample analysis of the applicable release (i.e., of the Stack, Off gas process flow, etc.), the radiation monitoring alarm set points may be established by the following calculation methods. A set point of a monitor of an elevated release, e.g., from the stack, may be calculated using the equation:

S = 1.06 !!__ 1 +Bk ( J Le* f L ( CiDFSi) g =the alarm set point (cpm) = primary conversion factor of the instrument

-monitor response to activity concentration of effluent being monitored, cpm/(µCi/cm 3 ). Each monitoring channel has a unique response, h, which is determined by the instrument calibration.

= relative concentration of noble gas radionuclide i in effluent at the point of monitoring

(µCi/cm 3) = 500 mrem/year

/472 (conversion of cfm to cc/sec) = factor converting elevated release rate of radionuclide i to total body dose equivalent rate at the location of potential exposure.

Units are: mrem/(yr(µCi/sec)).

From Table A-1. = flow of gaseous effluent stream being monitored, i.e., stack flow, vent flow, etc. (ft3/min) 102015 CY-OC-170-301 Revision 7 Page 83 of 140 BKG = Monitoring instrument background (cpm or mR/hr) 2.2.2 OTHER RELEASE POINTS Where: The set point of a monitor of a ground-level or vent release, e.g., from the turbine building vent or the AOG building, may be calculated with the equation:

s = 1.06 h f x Q =-_Li __ i -+ Bkg L(CiDFVi)

DFVi =factor converting ground-level or vent release of radionuclide i to the total body dose equivalent rate at the location of potential exposure.

Units are: mrem-m 3/µCi-year From Table A-1. XIQ =atmospheric dispersion from point of ground-level or vent release to the location of potential exposure (sec/m 3) from Table 2.2.2-1.

The atmospheric dispersion, X/Q, and the dose conversion factor, DFSi, depend upon local conditions.

For the purpose of calculating radioactive noble gas effluent monitor alarm set points appropriate for the OCGS, the locations of maximum potential Off Site exposure and the reference atmospheric dispersion factors applicable to the derivation of set points are given in Table 2.2.2-1. Symbols for this equation were defined in Section 2.2.1. TABLE 2.2.2-1 RECEPTOR LOCATIONS AND DISPERSION FOR GASEOUS MONITOR SET POINTS Discharge Point Recegtor Location Atm. Dispersion Sector Distance(m) (sec/m 3) Ground-level or vent ENE 338 4.59 E-5 Stack SW 229 N/A 2.2.3 RADIONUCLIDE MIX FOR SET POINTS For the purpose of deriving a set point, the distribution of radioactive noble gases in an effluent stream may be determined in one of the following ways: 102015 CY-OC-170-301 Revision 7 Page 84 of 140 2.2.3.1 Preferably, the radionuclide distribution is obtained by gamma isotopic analysis of identifiable noble gases in effluent gas samples. Results of the analyses of one or more samples may be averaged to obtain a representative spectrum.

2.2.3.2 In the event a representative distribution is unobtainable from recent measurements by the radioactive gaseous waste sampling and analysis program, it may be based upon past measurements.

2.2.3.3 Alternatively, the total activity concentration of radioactive noble gases may* be assumed to be Xenon-133 as found in Reg Guide 1.97. 2.3 GASEOUS EFFLUENT INSTANTANEOUS DOSE RATE CFR 20 10 2.3.1 SITE BOUNDARY DOSE RA TE -NOBLE GASES CONTROL 3.11.2.la limits the dose rate at the SITE BOUNDARY due to noble gas releases to 500 mrem/yr, total body and 3000 mrem/yr, skin. Radiation monitor alarm set points are established to ensure that these release limits are not exceeded.

In the event any gaseous releases from the station results in an alarm set point (as determined in Section 2.2) being exceeded, an evaluation of the SITE BOUNDARY dose rate resulting from the release shall be performed.

2.3.1.1 TOTAL BODY DOSE RA TE Where: DG Qi Py Vi x Qv The total body dose equivalent rate from radioactive noble gases discharged from an elevated point (stack *above building wake) is Galculated with the equation:

DG= LQiPySi i From a ground-level release (building vent) the total body dose equivalent rate is: DG = LQiPyVi Qv ; = total body dose equivalent rate due to irradiation by radioactive noble gas (mrem/hr)

=average discharge rate of noble gas radionuclide i released during the averaging time (µCi/hr) = factor converting time integrated ground-level concentration of noble gas nuclide i to total body dose mrem -m 3 . See Table A-2. µCi -sec = atmospheric dispersion factor from the OCGS to the Off Site location of interest (sec/m 3) from Table 2.3.1.3-1 102015 CY-OC-170-301 Revision 7 Page 85 of 140 PySi = factor converting unit noble gas nuclide i stack release to total body dose at ground level received outdoors from the overhead plume (mrem/µCi).

See Table A-2 The noble gas plume gamma-to-total body dose factors, PySi at designated locations are derived from meteorological dispersion data with the USNRC RABFIN software computer code or similar computer program implementing Reg Guide 1.109, Appendix B. The noble gas semi-infinite cloud gamma-to-total body dose factors, PyVi, are derived from Reg Guide 1.109, Revision 1, Table B-1, Column 5. 2.3.1.2 EXAMPLE TOTAL BODY DOSE RA TE Calculate the dose from a release of 100 Ci of Xe133 in 1 hour1.157407e-5 days 2.777778e-4 hours 1.653439e-6 weeks 3.805e-7 months from a ground level release DG = QiP yVi Qv j X/Qv =4.59E-5 sec/m3 (Table 2.3.1.3-1)

Qi = 1 E8 µCi/hr [100Ci*1 E6 µCi/Ci] PyVi = 9.33E-6 mrem-m 3 I µCi-sec DG = 4. 59 E -5 L 1E8

9. 33 E -6 i DG = 0.043 mrem/ hr 2.3.1.3 SKIN DOSE RATE where: DB x Q The dose _equivalent rate to skin from radioactive noble gases is calculated by assuming a person at ground level is immersed in and irradiated by a semi-infinite cloud of the noble gases originating in airborne effluent.

It is calculated for each air effluent discharge point with the equation:

DB = _!_ L Qi (SB i + 1.11 A yVi) Q i = dose rate to skin from radioactive noble gases (mrem/hr)

=Atmospheric dispersions Jrom gaseous effluent discharge point to ground-level location of interest (sec/m 3) from Table 2.3.1.3-1.

Qi = discharge rate of noble gas radionuclide i (µCi/hr) 102015 CY-OC-170-301 Revision 7 Page 86 of 140 SBi = factor converting time integrated ground-level concentration of noble gas radionuclide i to skin dose from beta radiation mrem -m 3 from Table A-2. µCi* sec AyVi = factor for converting time integrated, semi-infinite concentration of noble gas radionuclide i to air dose from its gamma mrad -m 3 from Table A-2. µCi* sec The noble gas beta radiation-to-skin-dose factors, SBi and the noble gas gamma-to-air dose factors, AyVi, are derived from Reg Guide 1.109, Revision 1, Table B-1, columns 3 and 4 respectively.

A tabulation of these factors used to compute noble gas-to-dose equivalent rate at 338 meters ENE for ground-level or vent and 544 meters SE for stack from the OCGS is in Table A-2. The dose equivalent rate is calculated with the meteorological dispersion data given in Table 2.3.1.3-1.

TABLE 1 RECEPTOR LOCATIONS AND DISPERSION FOR SITE BOUNDARY DOSE RATES Discharge Point Ground Level or Vent Stack Receptor Location Sector Distance (m) ENE 338 SE 544 Atm. Dispersion (sec/m 3) 4.59E-5 1.05 E-8 Alternatively, an approved computer code (e.g., "SEEDS" or "Open EMS") that implements the requirements of Regulatory Guide 1.109 may be used. Actual meteorological conditions concurrent with the release period or the default, annual average dispersion parameters as presented above may be used for evaluating the gaseous effluent dose rate. 2.3.1.4 EXAMPLE SKIN DOSE RATE Calculate the skin dose from a release of 100 Ci of Xe133 in 1 hour1.157407e-5 days 2.777778e-4 hours 1.653439e-6 weeks 3.805e-7 months from a ground level release: DB = L Qi c SBi + 1 .11 A r Vi ) Q i X/Q = 4.59 E-5 sec/m3 Qi = 1 EB µCi/hr SBi = 9. 71 E-6 mrem/µCi/

m3/sec AyVi = 1.12E-5 mrad/yr per µCi/m 3 102015 DB= 4.59E-5LlE8(9.7lE-6+

1.11 *l.12E-5) i DB= O.l02mrad I hr CY-OC-170-301 Revision 7 Page 87 of 140 2.3.2 SITE BOUNDARY DOSE RA TE -RADIOIODINE AND PARTICULATES 2.3.2.1 METHOD -SITE BOUNDARY DOSE RATE -RADIOIODINE AND PARTICULATES Where: 1E6 DFAija Ra x Qe The dose rate Off Site due to the airborne release of 1-131, 1-133, tritium, and particulates with half-lives greater than 8 days is limited to no more than 1500 mrem/yr to any organ in CONTROL 3.11.2.1 b. Evaluation of compliance with CONTROL 3.11 b is based on the sampling and analyses specified in TABLE 4.11.2.1.2-1.

Since the dose rate cannot be resolved within less than the sample integration or compositing time, the contribution of each radionuclide to the calculated dose rate will be averaged no more than 3 months for H-3, Sr-89, Sr-90, and alpha-emitting radionuclides and no more than 31 days for other radionuclides.

These are their usual sample integration or compositing times. The equation used to assess compliance of radioiodine, tritium, and radioactive particulate releases with the dose rate limit is: DRp = lE6L f RaDFAijaQe ili_ e i Qe = conversion pCi/µCi =the average dose rate to an organ via exposure pathway, p (mrem/yr).

=inhalation dose factors due to intake of radionuclide i, to organ j age group a (mrem/pCi) from Reg. Guide 1.109 Appendix E. =age group dependent inhalation respiratory rate (usage factor) m 3/yr from Table B-1 =annual average relative airborne concentration at an Off Site location due to a release from either the Stack or a vent, i.e. release point, e (sec/m 3) from Table 2.3.2.1-1.

Qei = release rate of radionuclide i from release point, e during the period of interest (µCi/sec).

For real-time meteorology and on an annual average basis, the location of the maximum ground-level concentration originating from a vent release will differ from the maximum ground-level concentration from a stack release. When assessing 102015 CY-OC-170-301 Revision 7 Page 88 of 140 compliance with CONTROL 3.11.2.1 b for tritium, iodine, and particulate, the air dispersion (X/Q) values are provided in Table 2.3.2.1-1.

TABLE 2.3.2.1-1 LOCATION OF MAXIMUM EXPOSURE RE BY INHALATION Discharge Point Recegtor Location Atm. Dispersion Sector Distance (m) (sec/m3) Ground Level or Vent ENE 338 4.59 E-5 Stack SE 937 1.25 E-8 Alternatively, inhalation exposure to effluent from the stack may be evaluated at the closest hypothetical individual located at: Stack SE 805 1.29 E-8 Alternatively, an approved computer code (e.g., "SEEDS" or "Open EMS") that implements the methods of Regulatory Guide 1.109, may be used. 2.3.2.2 EXAMPLE IODINE AND PARTICULATES DOSE RATE CALCULATION Ra DFAija Qei X/Qe Calculate the child thyroid dose rate from a release of 100 µCi/hr of 1131 from a ground level release: DRp =.lE6LIRaDFAijaQeili_

e . i Qe = 3700 m 3/yr = 4.39E-3 mrem/pCi = 0.028 µCi/sec [1 OOµCi/hr /3600 sec/hr = 0.02778] = 4.59 E:-5 sec/m 3 n DRp = lE6L3700*

4.39E -3

0.028* 4.59E -5 i DRp = 20.9mrem/

yr 2.4 NOBLE GAS EFFLUENT DOSE CALCULATIONS

-10 CFR 50 Doses resulting from the release of noble gases must be calculated to show compliance with Appendix I of 1 OCFR50. Calculations will be performed at least monthly for all gaseous effluents as stated in SURVEILLANCE REQUIREMENT 4.11.2.2 to verify that the dose to air is kept below the limits specified in CONTROL 3.11.2.2 and the dose to MEMBERS OF THE PUBLIC is maintained below the limits specified in CONTROL 3.11.2.3.

102015 CY-OC-170-301 Revision 7 Page 89 of 140 2.4.1 UNRESTRICTED AREA DOSE -NOBLE GASES CONTROL 3.11.2.2 requires a periodic assessment of releases of noble gases to evaluate compliance with the quarterly air dose limits shown in Table 2.4.1-1. TABLE 2.4.1-1 ANNUAL AIR DOSE LIMITS During any calendar quarter s 5 mrad gamma-air s 10 mrad beta-air During any calendar year s 10 mrad gamma-air s*20 mrad beta-air The method used to calculate the air dose at the critical location due to noble gas is described by the following equations.

The limits are provided in CONTROL 3.11.2.2 for air dose Off Site due to gamma and beta radiations from effluent noble gas. 2.4.1.1 AIR DOSE METHOD For Gamma Radiation:

Dose y = f A yVi X vQvi + A ySiQsi i=l Q For Beta Radiation Dose/3 = L e i=I Q Where: Dosey =the gamma dose during any specified time period (mrad). Dose J3 =the beta dose during any specified time period (mrad). AyVi = the air dose factor due to ground level gamma emissions for each identified noble gas radionuclide, i; (mrad/yr per µCi/m 3). Table A-2 AySi = the factor for air dose at ground level due to irradiation for an airborne plume resulting from a Stack release (mrad per µCi), Table A-3. AJ3i = the air dose factor due to beta emissions for each identified noble gas radionuclide, i (mrad/yr per µCi/m 3). Table A-3 Xv =the annual average relative concentration for areas at or beyond the site boundary for Q Q releases from either the Stack or ground vent at the critical location (sec/m 3), Table 2.4.1.1-1 102015 Qvi =amount of radionuclide i released from vents (µCi). Qsi =amount of radionuclide i released from the Stack (µCi). Qei = amount of radionuclide i released from release point e(µCi). CY-OC-170-301 Revision 7 Page 90 of 140 Noble gases may be released from the ground level vents and stack. The quantity of noble gas radionuclides released will be determined from the continuous noble gas monitors and periodic isotopic analyses.

The maximum Off Site gamma radiation dose rate to air from noble gases discharged from either the stack or from building vents occurs at 805 meters SE of the OCGS for the stack and 338 meters ENE of the OCGS for building vents. Values of AySi depend upon the meteorological conditions and the location of exposure and are calculated using the NRC RABFIN code or similar one in accordance with Reg. Guide 1.109, Appendix B, Section 1. AyVi and ABi are derived from Reg. Guide.1.109, Table B-1 for a semi-infinite cloud, independent of meteorology or location.

Values of AySi, AyVi and ABi used to calculate the noble gas radiation dose to air at 805 meters SE of the OCGS for the stack and 338 meters ENE of the OCGS for building vents are in Table A-3. Reference atmospheric dispersion from the OCGS to 805 meters SE for the stack and 338 meters ENE for building vents is given in Table 2.4.1.1-1.

TABLE 2.4.1.1-1 RECEPTOR LOCATIONS AND DISPERSION FOR AIR DOSE Discharge Point Ground Level or Vent Stack Receptor Location Sector Distance (m) ENE 338 SE 805 Atm. Dispersion (sec/m3) 4.59 E-5 1.29 E-8 Alternatively, an approved computer code (e.g., "SEEDS" or "Open EMS") that implements the requirements of Reg. Guide 1.109 may be used. 2.4.1.2 EXAMPLE NOBLE GAS AIR DOSE CALCULATION Calculate the gamma air dose from a release of 1 Ci per hour of Xe133 for 10 hours1.157407e-4 days 0.00278 hours 1.653439e-5 weeks 3.805e-6 months from a ground level release and 1 OOCi per hour for 10 hours1.157407e-4 days 0.00278 hours 1.653439e-5 weeks 3.805e-6 months from an elevated release: Dosey = f Ay Vix vQvi + AySiQsi-. i=l Q AyVi = 1.12E-5 mrad -m 3 /µCi -sec X/Q = 4.59 E-5 sec/m 3 Qvi = 1 E7 µCi [1 Ci/hr*1 Ohrs*1 E6 µCi/Ci] AySi = 1.03E-12 mrad I µCi Qsi = 1 E9 µCi [100Ci/hr*1 Ohrs*1 E6 µCi/Ci] 102015 n Dosey=

4.59E-5*1E7+l.03E-12*1E9 i=l n Dose; = L5.14E -3+1.03£ -3 i=l Dosey = 6.17 E -3mrad CY-OC-170-301 Revision 7 Page 91 of 140 Note how the ground level portion has a higher dose contribution per unit activity than the elevated portion. 2.4.1.3 INDIVIDUAL PLUME DOSE METHOD . The method for dose to an individual from noble gases is essentially identical with the qir dose method except that different dose factors apply. Also, since dose to the skin combines the contribution from gamma and beta emissions, the gamma dose must be added to the beta dose to obtain a total skin dose. For Total Body: Dos*(t) = iPrViX vQvi+ Py.SiQsi i=l Q For Skin Dose(s) = L

+ Dose(t) e i=l Q Where: Dose(t) =the total body dose during any specified time period (mrem). Dose(s) = tne skin dose during any specified time period (mrem). PyVi = the plume dose factor due to ground level gamma emissions for each identified noble gas radionuclide, i; (mrad/yr per µCi/m 3). Table A-5 PySi . = the factor for plume dose at ground level due to irradiation for an airborne plume resulting from a Stack release (mrad per µCi), Table A-5. SJ3i = the skin dose factor due to beta *emissions for each identified noble gas radionuclide, i (mrad/yr per µCi/m 3) from Table A-5. 102015 CY-OC-170-301 Revision 7 Page 92 of 140 Xv =the annual average relative concentration for areas at or beyond the site boundary for Q Q releases from either the Stack or ground vent at the critical location (sec/m 3) from Table 2.5.1. Qvi =amount of radionuclide i released from vents (µCi). Qsi =amount of radionuclide i released from the Stack (µCi). Qei =amount of radionuclide i released from release point e (µCi). 102015 CY-OC-170-301 Revision 7 Page 93 of 140 2.5 RADIOIODINE, PARTICULATE AND OTHER RADIONUCLIDES DOSE CALCULATIONS

-10 CFR 50 Doses resulting from the release of radioiodines and particulates must be calculated to show compliance with Appendix I of 1 OCFR50. Calculations will be performed at least monthly for all gaseous effluents as stated in SURVEILLANCE REQUIREMENT 4.11.2.2 and SURVEILLANCE REQUIREMENT 4.11.2.3 to verify that the dose to air is kept below the limits specified in CONTROL 3.11.2.2 and the dose to MEMBERS OF THE PUBLIC is maintained below the limits specified in CONTROL 3.11.2.3.

The maximum dose to an individual from radioiodines, tritium, and radioactive particulates with half-lives of greater than eight days in gase*ous effluents released to unrestricted areas is determined as described in Reg. Guide 1.109. Environmental pathways that radioiodine, tritium, and particulates in airborne effluent follow to the maximally exposed MEMBER OF THE PUBLIC as determined by the annual land use survey and reference meteorology will be evaluated.

The seasonality of exposure pathways may be considered.

For instance, if the most exposed receptor has a garden, fresh and stored vegetables are assumed to be harvested and eaten during April through October. Fresh vegetables need not be considered as an exposure pathway during November through March. To assess compliance with CONTROL 3.11.2.3, the dose due to radioactive iodine, tritium, and particulates in airborne effluent is calculated to a person residing 972 meters ESE of the OCGS for ground-level or vent and 937 meters SE of the OCGS for stack. Reference atmospheric dispersion and deposition factors are given in Table 2.5-1. TABLE 2.5-1 DISPERSION FOR 10CFR50 DOSES Discharge Point Dispersion XIQ (sec/m 3) Deposition D/Q(1/m 2) Ground Level or Vent 5.13 E-6 1.68 E-8 Stack 1.25 E-8 2.39 E-9 The environmental pathways of exposure to be evaluated are: inhalation, irradiation from ground deposition, and ingestion of milk (cow and goat are treated separately), meat, and vegetables.

Eight organs are considered:

Bone, Liver, Total Body, Thyroid, Kidney, Lung, Gl-LLI (Gastro-lntestinal tract I Lower Large Intestine), and Skin. Four different age groups are considered:

Infants, Children, Teens, and Adults. Doses are calculated to a 'receptor' -a person who inhales the airborne activity and resides in a location with ground deposition, and eats and drinks the foodstuffs produced.

The maximally exposed individual is conservatively assumed to reside at the location of the highest sum of the inhalation and ground plane doses, while eating and drinking foodstuffs transported from the locations that are highest for those pathways.

Receptor locations are provided in TableA-4.

Alternatively, an approved computer code (e.g., "SEEDS" or "Open EMS") that implements the requirements of Reg Guide 1.109 may be used. 102015 CY-OC-170-301 Revision 7 Page 94 of 140 2.5.1 INHALATION OF RADIOIODINES, TRITIUM, PARTICULATES, AND OTHER RADIONUCLIDES.

Where: Oja Ra T x Q Dose from the inhalation pathway is generally in the form: Dja = RaTL iQ =the dose to the organ j (of eight) of age group a (of four) =the respiration rate for age group a from Table B-1 = the duration of the release in fraction of a year = The atmospheric dispersion to the point of interest (the 'receptor')

in sec/m 3 from Table 2.5-1 Qi =The release rate of radionuclide i (pCi/sec)

DFAija =The inhalation dose conversion factor (mrem per pCi) for radionuclide i to organ j of age group a from Reg. Guide 1.109 Appendix E.

Ai =decay constant of isotope i: 0.693/ Half life in years Tr = plume transit time from release to receptor in years Ai and Tr may be in any time units as long as they are the same Note that a 'depleted X/Q' (dX/Q) is applicable to particulates only, which accounts for the natural settling and lack of surface reflection of particulates to estimate the downwind concentration accounting for these removal processes.

Depleted X/Q will be slightly smaller than the X/Q. This is not used in the ODCM for simplicity.

Using the X/Q is therefore slightly conservative compared to the dX/Q. 102015 CY-OC-170-301 Revision 7 Page 95 of 140 2.5.2 EXAMPLE CALCULATION

-INHALATION OF RADIOIODINES, TRITIUM, PARTICULATES, AND OTHER RADIONUCLIDES Oja Ra T* x Q Qi Calculate the dose to child lung from inhalation from a ground level release of 100 µCi of Co-60 in 10 hours1.157407e-4 days 0.00278 hours 1.653439e-5 weeks 3.805e-6 months . Plume transit decay time is ignored (exp(-,\iTr)=1).

Dja = RaTL

Q =the dose to the organ j (of eight) of age group a (of four) = 3700 m 3/yr = 0.00114 yrs [10 hrs I 8760 hrs I yr] = 5.13 E-6 sec/m 3 = 2. 78E3 pCi/sec [100 µCi

1 E6 pCi/µCi I (10 hrs*3600 sec I hr)] DFAija =1.91 E-3 mrem I pCi Dja= 3700* 0.00114* 5.l3E-6

2.78E3 *l.91E-3 Dja = l .15E -4mrem 2.5.3 INGESTION OF RADIOIODINES, PARTICULATES AND OTHER RADIONUCLIDES Dose from the ingestion pathways is more complex and is broken out here into multiple steps: 2.5.3.1 CONCENTRATION OF THE RADIONUCLIDE IN ANIMAL FORAGE AND VEGETATION

-OTHER THAN TRITIUM Where: Civ Qi D Q The concentration of a radionuclide in a foodstuff (other than tritium -see section 2.5.3.3 for tritium) is dependent on the atmospheric deposition, the biological uptake into the food, various decay times (plume travel, harvest to tablei etc.) and is generally of the form: = the concentration (pCi/kg) of radionuclide i in vegetation

= the release rate of isotope i in pCi/hr =The atmospheric deposition to the point of interest (the 'receptor')

in 1/m 2 from Table 2.5-1. 102015 CY-OC-170-301 Revision 7 Page 96 of 140 Civ = D

+ Biv(l-EXP_(-JdTb))}EXP(-}dTh)EXP(-JdTr)

Q YvAEz PA-z r =the retention coefficient for deposition onto vegetation surfaces (1.0 for iodines, 0.2 . for particulates)

Id =the decay constant of radionuclide i; 0.693/half life in hours AEi =the effective removal constant which is the sum of Ai + AW where AW is the weathering constant, 0.0021/hr Te =duration of crop exposure during the growing season in hours. This is not the entire duration of the growing season, and is different for leafy vegetable and fruit/grain/vegetables.

Provided in Table E-15 of Reg. Guide 1.109 or Table B-1. Yv = agricultural yield Kg of vegetation per m 2 , typically

0. 7 kg/m 2 Biv = soil uptake concentration factor for transfer of the radionuclide i from the soil to the vegetation through normal root uptake processes in pCi/kg in vegetation per pCi/Kg in soil. Values are provided in Reg. Guide 1.109 Table E-1. Tb = the length of time the soil is exposed to contaminated inputs -nominally 30 years (2.63E5 hr) P =effective soil density in kg/m 2 normally 240 kg/m 2 Th =holdup time, the time the foodstuff is in transit between harve$t and consumption in hours Tr =plume transit time from release to receptor in hours 2.5.3.2 EXAMPLE CALCULATION OF CONCENTRATION OF THE RADIONUCLIDE IN ANIMAL FORAGE AND VEGETATION

-OTHER THAN TRITIUM. Calculate the forage and vegetation concentration from a ground level release of 100 µCi of Co-60 in 10 hours1.157407e-4 days 0.00278 hours 1.653439e-5 weeks 3.805e-6 months (plume transit time is ignored Tr=O, EXP(-AiTr)=1):

Civ= D

+

Q YvAE'z PA,z D/Q = 1.67E-8 m 2 Qi = 1 E7 pCi/hr [1 OOµCi

1 E6 pCi/µCi I 10 hr] r = 0.2 Ai = 1.5E-5/hr

[0.693 I (5.27yr

8760 hr/yr)] AEi = 2.12E-3 /hr [1.5E-5 + 0.0021] Te = 720 hr [grass-cow-milk-man pathway value] 102015 Yv = 0.7 kg/m 2 Biv = 9.4E-3 Tb = 2.63E5 hr P =240 kg/m 2 Th = 24.1 hours1.157407e-5 days 2.777778e-4 hours 1.653439e-6 weeks 3.805e-7 months 0.2 *(l-EXP(-2.l2E-3

720))

CY-OC-170-301 Revision 7 Page 97 of 140 Civ=l.67E-8*lE7 0.7*2.l 2 E-3 . EXP(-l.5E-5*0) 9.4E -3 * (1-EXP(-l.5E -5

2.63£5)) 240*l.5E-5 Civ = 1.67 E -8

lE7 0.2 * (1-EXP (-1.53)) + l.48E -3 EXP (-0) 9.4E -3 * (1-EXP (-3.95)) 3.6E -3 Civ = 1 .67 E -1

1 {105 .9 +} 2.56 Civ = 18 . 0 pCi I Kg 2.5.3.3 CONCENTRATION OF TRITIUM IN ANIMAL FORAGE AND VEGETATION Where: Since tritium is assumed to be released as tritiated water (HTO), the concentration of tritium in a foodstuff is dependent on atmospheric dispersion like a gas, rather than particulate deposition as for other radionuclides for foodstuff uptake. Further; the concentration of tritium in food is assumed to be based on equilibrium between the concentration of the tritium in the atmospheric water and the concentration of tritium in the water in the food. Concentration of tritium in vegetation can be calculated generally in the form (a plume transit decay term: EXP(-A-iTr) is ignored since plume travel times are very short compared to the half life):* Ctv = lOOOQt X

0.75

0.5 Q H Ctv = the concentration (pCi/kg) of tritium in vegetation 1000 = g per kg Qt = the release rate of the tritium in pCi/ sec 102015 CY-OC-170-301 Revision 7 Page 98 of 140 XIQ =the atmospheric dispersion at the vegetation point, sec/m 3 from Table 2.5-1 0. 75 = the fraction of vegetation that is water 0.5 = the effective ratio between the atmospheric water concentration and the vegetation concentration H =the absolute humidity g/m 3. Absolute humidity is seasonally dependent, varying from as little as 1 in the winter to as much as 20 in the summer. Monthly average values derived from historical data are provided in Table B-2. 2.5.3.4 EXAMPLE CALCULATION OF CONCENTRATION OF TRITIUM IN ANIMAL FORAGE AND VEGETATION.

Calculate the forage and vegetation concentration from a ground level release of 100 µCi of H-3 in 10 hours1.157407e-4 days 0.00278 hours 1.653439e-5 weeks 3.805e-6 months . Plume transit decay time is ignored (exp(-A.iTr)=1):

Ctv = lOOOQt X

0.75

0.5 Q H Qt = 2778 pCi/sec [1 OOuCi

1 E6 pCi/uCi I (1 Ohrs*3600sec/hr)]

XIQ = 5.13E-6 sec/m 3 H = 5 g/m 3 (assumed for this example) Ctv = 2778*1000*

5.13E -6* 0.75

0.5 5 Ctv = 1.07 pCil kg 2.5.3.5 CONCENTRATION OF THE RADIONUCLIDE IN MILK AND MEAT Where: Meat and milk animals are assumed to eat both pasture grass and stored feed. During a fraction of the year, they may be assumed to be exclusively on stored feed, outside of the growing season. If using annual average release, the fraction of stored and fresh feed must be accounted for with fractions, otherwise (as in this ODCM), the fresh pasture pathway is turned on or off depending on the growing season. The concentration of a radionuclide in the animal feed is calculated as follows: Civ = FpCis+ (l-Fp)Cis(l-Fs)

+ CipFs(l-Fp)

Fp =the growing season pasture factor: 1 if not growing season, 0 if in growing season 102015 CY-OC-170-301 Revision 7 Page 99 of 140 Fs =the fraction of the daily feed from fresh pasture from Table 8-1 or Exhibit E-15 from Reg. Guide 1.109. Cip = the concentration in the fresh pasture feed (Civ from section 2.5.3.2 with Th = 0 for immediate consumption)

Cis = the concentration in stored feed (Civ from section 2.5.3.2 with Th = 90 days) The concentration in the milk is then based on this feed concentration:

Cim = FmCivQ/EXP

(-}dTf) Where: Cim = the concentration in milk pCi/I Fm =the transfer coefficient of intake to concentration in the milk (d/I) from Reg. Guide 1.109 Table E-1. Qf =feed intake rate Kg/d from Reg. Guide 1.109 Table E-3. A.i =radionuclide i decay constant in 1/days Tf = transport time from milk production to consumption (2 days for milk) The Goat milk pathway may be similarly evaluated:

Cim = FgCivQ/EXP

(-A,iTf) Where: Fg =the transfer coefficient of intake to concentration in the milk (d/I) for goats from Reg. Guide 1.109 Table E-2. And for meat: Cif = FfCivQ/EXP

(-1iTs) Where: Ff =the transfer coefficient of intake to concentration in the meat d/kg from Reg. Guide 1.109 Table E-1. Ts =the transport time from slaughter to consumption (20 days) 102015 CY-OC-170-301 Revision 7 Page 100of140 2.5.3.6 EXAMPLE CALCULATION OF CONCENTRATION OF THE RADIONUCLIDE IN MILK AND MEAT Calculate the concentration in cow milk from a ground level release of 100 µCi of Co-60 in 10 hours1.157407e-4 days 0.00278 hours 1.653439e-5 weeks 3.805e-6 months . Plume transit decay time is ignored (exp{-A.iTr)=1):-

Civ = FpCis + (1-Fp )Cis(l -Fs) + CipFs(l -Fp) Assume animals are on pasture and receive half of their food from stored feed. Cip = 18.0 pCi/kg as previously calculated in section 2.5.3.2 Fp = 0 . Fs = 0.5 Cis is calculated by applying a 90 day decay term to the Cip value previously calculated, since the previous decay correction was for 0 time as shown in 2.5.3.2. Cis = 18.0* (exp(-0.693

90 /(5.27 *365))) Cis = 17.4pCi/ kg Civ is then: Civ = 0*17.4 +(1-0)17.4*

(1-0.5)+ 18.0* 0.5 * (1-0) Civ = 17.7 pCil kg The concentration in milk is given by: Cim = FmCivQIEXP

(-JdTf) Fm =1.0E-3 d/I Qf = 50 Kg/d A.i = 3.6E-4/d [0.693 I (5.27 yrs*365 days/yr)]

Cim= l.OE-3*17.7*50*

EXP(-3.6E-4*2)

Cim = 0.88pCi/ l The concentration in meat given by: Cif = FfCivQ/EXP

(-A-iTs) Ff =1.3E-2 d/kg 102015 CY-OC-170-301 Revision 7 Page 101 of 140 Qf = 50 Kg/d A,i = 3.6E-4/d Cif = l.3E-2*17.7*50*

EXR.._-3.6E-4*20)

Cif = 11.5 pCi I kg 2.5.3.7 DOSE FROM CONSUMPTION OF MILK, MEAT, AND VEGETABLES Where: The environmental pathway ingestion dose is the sum of the milk, meat, and vegetation ingestion pathways.

There are two separate pathways for vegetation:

fresh leafy vegetables and a combination of fruits, non-leafy vegetables, and grains. These differ only in the decay and buildup processes applied to account for the environmental exposure, and transportation delay decay represented by Te and Th as shown in section 2.5.3.1. For long half-life isotopes (e.g. Co-60) the decay differences have little impact on the dose. Dose from the environmental ingestion pathways is generally of the form: Dja = TLDFiijc{_UavFgCiv+

UamCim + Ua/Cif + UalF/Cil]

i Dja = the dose to organ j of age group a -mrem T = fraction of year of release duration DFlija =the ingestion dose factor for isotope i to organ j for age group a -mrem/pCi from Reg. Guide 1.109 Appendix E Uav = Ingestion rate (usage factor) for non-leafy vegetables, grains, and fruits for age-group a from Reg. Guide 1.109 Table E-5 or Table 8-1. Fg =the fraction of vegetables, grains, and fruits from the location of interest:

0.76 in Reg. Guide 1.109. Civ = the concentration of isotope i in the vegetables, fruits, and grains calculated from section 2.5.3.2. Uam =Ingestion rate (usage factor) for milk for age group a: from Table B-1 or Reg. Guide 1.109 Table E-5. Cim = the concentration of isotope i in milk calculated from section 2.5.3.5. Uaf =the ingestion rate for meat for age group a: from Table B-1 or Reg. Guide 1.109 Table E-5. 102015 CY-OC-170-301 Revision 7 Page 102of140 Cif = the concentration of isotope i in meat calculated from section 2.5.3.2. Ual =the ingestion rate for leafy vegetables for age group a: from Table B-1 or Reg. Guide

1.109 Table E-5: Fl =the fraction of annual leafy vegetable ingestion from the location of interest:

1.0 in Reg. Guide 1.109. Cil = concentration of isotope i in the leafy vegetables for direct human consumption:

Civ calculated from section 2.5.3.2 with Th=O. 2.5.3.8 EXAMPLE CALCULATION-DOSE FROM CONSUMPTION OF MILK, MEAT, AND VEGETABLES Calculate the ingestion dose to child whole body from a ground level release of 100 µCi of Co-60 in 10 hours1.157407e-4 days 0.00278 hours 1.653439e-5 weeks 3.805e-6 months . Plume transit decay time is ignored (exp(-P.ffr)=1):

Dja = TLDFlijd._UavFgCiv+

UamCim+ UafCif + UalFZCilJ i Where: T = 0.00114 yr [1 Ohrs I 8760 hrs/yr) DFlija = 1.56E-5 mrem/pCi Uav = 520 Fg = 0.76 Civ = 17.6 [18.0*EXP(-A.*60) using 60 day delay for ingestion]

Uam = 330 Cim = 0.88 Uaf = 41 Cif = 11.5 Ual = 26 Fl = 1 Cil = 17.7 Dja =

0.76*17.6

+ 330* 0.88+ 41*11.5+26*

1 *17.7] i Dja= .00114Ll.56E-5[6956+290+472+460]

i Dja = l .45E -4mrem: child: wholebody

2.5.4 GROUND

PLANE DEPOSITION IRRADIATION Dose from ground plane deposition is estimated by determining the surface activity resulting from the release. 102015 CY-OC-170-301 Revision 7 Page 103of140 2.5.4.1 GROUND PLANE CONCENTRATION Where: Cig D Q Qi Tb The ground surface activity is estimated as: Cig = 0-EXP(-A.iTb))

=ground plane concentration of radionuclide i in pCi/m 2 = local,atmospheric release deposition factor in 1/m 2 from Table 2.5-1 = release rate in pCi/sec =radiological decay constant in 1/sec = long term buildup time 30 years (9.46E8 sec) Note: Qi, Id and Tb can utilize any time units as long as they are all the same 2.5.4.2 . EXAMPLE GROUND PLANE CONCENTRATION CALCULATION D Q Qi A.i Tb I Calculate the ground plane concentration from a 100 µCi release of Co-60 over 10 hours1.157407e-4 days 0.00278 hours 1.653439e-5 weeks 3.805e-6 months from a ground level release point. Cig = (1-EXP(-A.iTb

)) = 1.67E-8 /m 2 = 2778 pCi/sec [1 OOµCi/1 Ohrs/3600sec/hr]

= 4.17E-9/sec

[0.693/(5.27yr*8760hr/yr*3600sec/hr)]

= 9.46E8 sec Cig = 1.67 E -8 2778 (1-EXP(-4.17 E -9

9.46E8)) 4.17E-9 Cig = 1.09E4 pCi I m2 102015 CY-OC-170-301 Revision 7 Page 104of140

2.5.4.3 GROUND PLANE DOSE Where: Djg 8760 T Sf DFGij 2.5.4.4 Annual dose from the ground plane deposition is of the form: Djg = 8760

T

SfL CigDFGij i = the annual dose (mrem) from ground plane pathway (g) to the total body or skin 0) =hours in a* year =fraction of year release is in progress =shielding factor accounting for shielding from dwelling from Table B-1 =Ground plane dose factor for skin or total body (j) for radionuclide i from, Table E-6 of Reg. Guide 1.109 in mrem/hr I pCi/m 2. EXAMPLE GROUND PLANE DOSE Calculate the ground plane Total Body dose from a 100 µCi release of Co-60 over 10 hours1.157407e-4 days 0.00278 hours 1.653439e-5 weeks 3.805e-6 months from a ground level release point. Djg 8760

T *Sf L CigDFGij i T = 0.00114 [10/8760]

Sf = 0.7 DFGij = 1. 7E-8 Cig = 1.09E4 Djg = 8760*0.00114*0.7Ll.09E4*1.7E-8 i Djg = l .30E -3mremTotalB ody 2.6 PROJECTED DOSES -GASEOUS The projected doses in a 31 day period are equal to the calculated doses from the current 31 day period. 3.0 TOTAL DOSE TO MEMBERS OF THE PUBLIC-40 CFR 190 The Radiological Environmental Monitoring Report (REMPf submitted by May 1st of each year shall include an assessment of the radiation dose to the likely most exposed MEMBER OF THE PUBLIC for reactor releases and other nearby uranium fuel cycle 102015 CY-OC-170

.. 301 Revision 7 Page 105of140 sources (including dose contributions from effluents and direct radiation from on-site sources).

For the likely most exposed MEMBER OF THE PUBLIC in the vicinity of Oyster Creek, the sources of exposure need only consider the Oyster Creek Generating Station. No other fuel cycle facilities would contribute significantly to the MEMBER OF THE PUBLIC dose for the Oyster Creek vicinity, however, both plant operation and ISFSI sources must be included in the dose assessment.

To assess compliance with CONTROL 3.11.4, calculated organ and total body doses from effluents from liquid pathways and atmospheric releases as well as any dose from direct radiation will be summed. As appropriate for demonstrating/evaluating compliance with the limits of CONTROL 3.11.4 (40 CFR 190), the results of the environmental monitoring program may be used for providing data on actual measured levels of radiation and I or radioactive material and resultant dose to the MEMBER OF THE PUBLIC in the actual pathways of exposure.

3.1 EFFLUENT

DOSE CALCULATIONS For purposes of implementing the surveillance requirements of CONTROL 3/4.11.4 and the reporting requirements of Technical Specification 6.9.1.d (ARERR), dose calculations for the Oyster Creek Generating Station may be performed using the calculation methods contained within the ODCM; the conservative controlling pathways and locations from the ODCM or the actual pathways and locations as identified by the land use census (CONTROL 3/4.12.1) may be used. Average annual meteorological dispersion parameters provided herein or meteorological conditions concurrent with the release period under evaluation may be used. 3.2 DIRECT EXPOSURE DOSE DETERMINATION Any potentially significant direct exposure contribution to off-site individual doses may be evaluated based on the results of environmental measurements (e.g., dosimeter) and/or by the use of radiation transport and shielding calculation methodologies.

4.0 RADIOLOGICAL

ENVIRONMENTAL MONITORING PROGRAM The operational phase of the Radiological Environmental Monitoring Program (REMP) is conducted in accordance with the requirements of CONTROL 3.12.1. The objectives of the program are: -To determine whether any significant increases occur in the concentration of radionuclides in the critical pathways of exposure in the vicinity of Oyster Creek -To determine if the operation of the Oyster Creek Generating Station has resulted in any increase in the inventory of long lived radionuclides in the environment;

-To detect any changes in the ambient gamma radiation levels; and -To verify that OCGS operations have no detrimental effects on the health and safety of the public or on the environment.

The REMP sample locations are presented in Appendix E. 102015 CY-OC-170-301 Revision 7 Page 106of140 APPENDIX A -DERIVED DOSE FACTORS AND RECEPTOR LOCATIONS 102015 CY-OC-170-301 Revision 7 Page 107of140 Table A-1 Dose Conversion Factors for Deriving Radioactive Noble Gas Radionuclide-to-Dose Equivalent Rate Factors* Radionuclide Factor DFSi for Factor DFVi for Stack Release* Ground-level or Vent Release**

mrem-sec mrem-m 3 µCi-year µCi-year Kr83m 9.21E-10 7.56E-02 Kr85m 1.46E-04 1.17E+03 Kr85 2.58E-06 1.61E+01 Kr87 8.65E-04 5.92E+03 Kr88 2.16E-03 1.47E+04 Kr89 2.06E-03 1.66E+04 Kr90 1.56E+04 Xe131m 3.13E-05 9.15E+01 Xe133m 2.50E-05 2.51E+02 Xe133 2.15E-05 2.94E+02 Xe135m 4.81E-04 3.12E+03 Xe135 2.51E-04 1.81E+03 Xe137 1.79E-04 1.42E+03 Xe138 1.37E-03 8.83E+03 Xe139 2.14E-04 5.02E+03 Ar41 1.67E-03 8.84E+03

Based on meteorology applicable at 229 meters SW of stack. ** For exposure to a semi-infinite cloud of noble gas. 102015 CY-OC-170-301 Revision 7 Page 108of140 Table A-2 Noble Gas Radionuclide-to-Dose Eguivalent Rate Factors* I Radionuclide PySi** PyVi*** AyVi*** SBi*** mrem mrem-m 3 mrad-m 3 mrem-m 3 µCi µCi-sec (Ki) µCi-sec (M) µCi-sec (Li) Kr83m 2.92E-17 2.40E-09 6.13E-07 Kr85m 4.64E-12 3.71E-05 3.90E-05 4.63E-05 Kr85. 8.18E-14 5.11E-07 5.46E-07 4.25E-05 Kr87 2.74E-11 1.88E-04 1.96E-04 3.09E-04 Kr88 6.84E-11 4.67E-04 4.83E-04 7.52E-05 Kr89 6.53E-11 5.27E-04 5.49E-04 3.21E-04 Kr90 4.95E-04 5.17E-04 2.31E-04 Xe131m 9.92E-13 2.90E-06 4.95E-06 1.51E-05 Xe133m 7.94E-13 7.97E-06 1.04E-05 3.16E-05 Xe133 6.83E-13 9.33E-06 1.12E-05 9.71E-06 Xe135m 1.53E-11 9.90E-05 1.07E-04 2.26E-05 Xe135 7.97E-12 5.75E-05 6.10E-05 5.90E-05 Xe137 5.69E-12 4.51E-05 4.79E-05 3.87E-04 Xe138 4.34E-11 2.BOE-04 2.92E-04 1.31E-04 Xe139 6.79E-12 Ar41 5.30E-11 2.81E-04 2.95E-04 8.54E-05 *All of these dose factors apply out-of-doors.

- Based on meteorology at 229 meters SW of effluent stack. ***Derived from Reg Guide 1.109, Revision 1, Table B-1. 102015 CY-OC-170-301 Revision 7 Page 109of140 Table A-3 Air Dose Conversion Factors for Effluent Noble Gas Radionuclide AySi** mrad µCi Kr83m 1.33E-16 Kr85m 6.89E-12 Kr85 1.24E-13 Kr87 4.13E-11 Kr88 1.03E-10 Kr89 9.82E-11 Kr90 Xe131m 1.50E-12 Xe133m 1.23E-12 Xe133 1.03E-12 Xe135m 2.31E-11 Xe135 1.20E-11 Xe137 8.59E-12 Xe138 6.51E-11 Xe139 1.02E-11 Ar41 7.94E-11 ** Based on meteorology at 229 meters SW of effluent stack. *** Derived from Reg Guide 1.109, Revision 1, Table 8-1. AyVi*** Af3i*** mrad-m3 mrad-m3

µCi-sec(M)

µCi-sec (Ni) 6.13E-07 9.14E-06 3.90E-05 6.25E-05 5.46E-07 6.19E-05 .1.96E-04 3.27E-04 4.83E-04 9.30E-05 5.49E-04 3.37E-04 5.17E-04 2.49E-04 4.95E-06 3.52E-05 1.04E-05 4.?0E-05 1.12E-05 3.33E-05 1.0?E-04 2.35E-05 6.10E-05 7.81E-05 4.79E-05 4.03E-04 1.51 E-04 2.95E-04 1.04E-04 102015 Effluent Table A-4 Locations Associated with Maximum Ex osure of a Member of the Public* Distance (meters) Location CY-OC-170-301 Revision 7 Page 110of140 Direction (to) Liquid U.S. Route 9 Bridge at Discharge Canal Airborne Iodine and Particulates 937 SE Tritium 937 SE Noble Gases 937 SE Irradiation by OCGS Site Boundary All Noble Gas g Air Dose 937 SE Noble Gas B Air Dose 937 SE Note: the nearby resident experiencing the maximum exposure to airborne effluent from the Station is located 937 meters SE of the OCGS. The nearby resident (part-time) experiencing the maximum exposure to gamma radiation directly from the Station is located 618 meters WSW of the OCGS. The most exposed member of the public is assumed to be exposed by irradiation from the OCGS, by inhaling airborne effluent, by irradiation by the airborne effluent, by irradiation by the airborne plume of the noble gas, by radionuclides deposited onto the ground, by irradiation by shoreline deposits, and by eating fish and shellfish caught in the discharge canal. *The age group of the most exposed member of the public is based on Reg. Guide 1.109, Revision 1. 102015 CY-OC-170-301 Revision 7 Page 111of140 Table A-5 Critical Receptor Noble Gas Dose Conversion Factors* Radionuclide Kr83m Kr85m Kr85 Kr87 Kr88 Kr89 Kr90 Xe131m Xe133m Xe133 Xe135m Xe135 Xe137 Xe138 Xe139 Ar41 PySi** mrem µCi 4.61E-17 2.13E-12 3.38E-14 1.08E-11 2.76E-11 2.02E-11 5.05E-13 3.95E-13 3.88E-13 5.82E-12 3.51 E-12 1.74E-12 1.72E-11 9.30E-13 2.0?E-11 Py Vi*** mrem-m 3 µCi-sec( Ki) 2.40E-09 3.71E-05 5.11E-07 1.88E-04 4.67E-04 5.27E-04 4.95E-04 2.90E-06 7.97E-06 9.33E-06 9.90E-05 5.75E-05 4.51E-05 2.80E-04 2.81E-04

All of these dose factors apply out-of-doors.

AyVi*** mrad-m 3 µCi-sec(Mi) 6.13E-07 3.90E-05 5.46E-07 1.96E-04 4.83E-04 5.49E-04 5.17E-04 4.95E-06 1.04E-05 1.12E-05 1.0?E-04 6.10E-05 4.79E-05 2.92E-04 2.95E-04 ** Based on meteorology at 937 meters SE of effluent stack. ***Derived from Reg Guide 1.109, Revision 1, Table B-1 AySi** mrad µCi 1.77E-14 3.16E-12 5.12E-14 1.63E-11 4.14E-11 3.03E-11 8.03E-13 6.50E-13 6.13E-13 8.BOE-12 5.25E-12 2.64E-12 2.58E-11 1.40E-12 3.10E-11 SBi*** mrem-m 3 µCi-sec(L1) 4.63E-05 4.25E-05 3.09E-04 7.52E-05 3.21E-04 2.31E-04 1.51 E-05 3.16E-05 9.71E-06 2.26E-05 5.90E-05 3.87E-04 1.31E-04 8.54E-05 102015 APPENDIX B -MODELING PARAMETERS CY-OC-170-301 Revision 7 Page 112of140 102015 CY-OC-170-301 Revision 7 Page 113of140 Table B-1-OCGS Usage Factors For Individual Dose Assessment . Effluent Ingestion Parameters Fraction Of Produce From Local Garden Soil Density In Plow Layer (Kgtm 2) Fraction Of Deposited Activity Retained On Vegetation Shielding Factor For Residential Structures Period Of Buildup Of Activity In Soil (hr) Period of Pasture Grass Exposure to Activity (hr) Period Of Crop Exposure to Activity (hr) Delay Time For Ingestion Of Stored Feed By Animals (hr) Delay Time For Ingestion Of Leafy Vegetables By Man (hr) Delay Time For Ingestion Of Other Vegetables By Man (hr) Transport Time Milk-Man (hr) Time Between Slaughter and Consumption of Meat Animal (hr) Grass Yield Wet Weight (Kgtm 2) Other Vegetation Yield Wet-Weight (Kgtm 2) Weathering Rate Constant For Activity on Veg. (h(1) Milk Cow Feed Consumption Rate (Kg/day) Goat Feed Consumption Rate (Kg/day) Beef Cattle Feed Consumption Rate (Kg/day) Milk Cow Water Consumption Rate (L/day) Goat Water Consumption Rate (L/day) Beef Cattle Water Consumption Rate (L/day) Environmental Transit Time For Water Ingestion (hr) Environmental Transit Time For Fish Ingestion (hr) Environmental Transit Time For Shore Exposure (hr) Environmental Transit Time For Invertebrate Ingestion (hr) Usage Factor 7.6E-1 2.4E+2 2.5E-1 7.0E-1 1.31E+5 7.2E+2 1.44E+3 2.16E+3 2.4E+1 1.44E+3 4.8E+1 4.8E+2 7.0E-1 2.0 2.1E-3 5.0E+1 6.0 5.0E+1 6.0E+1 8.0 5.0E+1 1.2E+1 2.4E+1 0 2.4E+1 102015 Table 8-1 (Continued)

OCGS Usage Factors for Individual Dose Assessment Effluent Ingestion Parameters Water Ingestion (L/yr) a. Adult b. Teen c. Child d. Infant Shore Exposure (hr/yr) a. Adult b. Teen c. Child d. Infant Salt Water Sport Fish Ingestion (Kg/yr) a. Adult b. Teen c. Child d. Infant Salt Water Commercial Fish Ingestion (Kg/yr) a. Adult b. Teen c. Child d. Infant Salt Water Invertebrate Ingestion (Kg/yr) a. Adult b. Teen c. Child d. Infant Irrigated Leafy Vegetable Ingestion (Kg/yr) a. Adult b. Teen c. Child d. Infant CY-OC-170-301 Revision 7 Page 114of140 Usage Factor 7.3E+2 5.1E+2 5.1 E+2 3.3E+2 1.2E+1 6.7E+1 1.4E+1 0 2.1E+1 1.6E+1 6.9 0 2.1 E+1 1.6E+1 6.9 0 5.0 3.8 1.7 0 6.4E+1 4.2E+1 2.6E+1 0 102015 Table B-1 (Continued)

OCGS Usage Factors for Individual Dose Assessment Effluent Ingestion Parameters Irrigated Other Vegetable Ingestion (Kg/yr) a. Adult b. Teen c. Child d. Infant Irrigated Root Vegetable Ingestion (Kg/yr) a. Adult b. Teen c. Child d. Infant Irrigated Cow and Goat Milk Ingestion (Uyr) a. Adult b. Teen c. Child. d. Infant Irrigated Beef Ingestion (Kg/yr) C/ a. Adult b. Teen c. Child d. Infant Inhalation (m 3/yr) a. Adult b. Teen c. Child d. Infant Cow and Goat Milk Ingestion (Uyr)' a. Adult b. Teen c. Child d. Infant Meat Ingestion (Kg/yr) a. Adult b. Teen c. Child d. Infant CY-OC-170-301 Revision 7 Page 115of140 Usage Factor 5.2E+2 6.3E+2 5.2E+2 0 5.2E+2 6.3E+2 5.2E+2 0 3.1E+2 4.0E+2 3.3E+2 3.3E+2 1.1E+2 6.5E+1 4.1E+1 0 8.0E+3 8.0E+3 3.7E+3 1.4E+3 3.1E+2 4.0E+2 3.3E+2 3.3E+2 1.1 E+2 6.5E+1 4.1 E+1 0 102015 Table B-1 (Continued)

OCGS Usage Factors for Individual Dose Assessment Effluent Ingestion Parameters Leafy Vegetable Ingestion (Kg/yr) a. Adult . b. Teen c. Child d. Infant Fruits, Grains, & Other Vegetable Ingestion (Kg/yr) a. Adult b. Teen c. Child d. Infant CY-OC-170-301 Revision 7 Page 116of140 Usage Factor 6.4E+1 4.2E+1 2.6E+1 0 5.2E+2 6.3E+2 5.2E+2 0 102015 Table B-2 Monthly Average Absolute Humidity g/m 3 (derived from historical climatological data) Average Absolute Month Humidity (g/m 3) January 3.3 February 3.3 March 4.5 April 6.1 May 9.4 June 12.8 July 15.2 August 15.6 September 12.4 October 7.9 November 5.9 December 3.8 CY-OC-170-301 Revision 7 Page 117of140 102015 APPENDIX C -REFERENCES CY-OC-170-301 Revision 7 Page 118of140 102015 Table C-1 -REFERENCES

1) Oyster Creek Updated Final Safety Analysis Report 2) Oyster Creek Facility Description and Safety Analysis Report 3) Oyster Creek Operating License and Technical Specifications CY-OC-170-301 Revision 7 Page 119of140 4) NUREG 1302 "Off Site Dose Calculation Manual Guidance:

Standard Radiological Effluent Controls for Boiling Water Reactors" -Generic Letter 89-10, Supplement No. 1,April 1991 5) Reg Guide 1.21 "Measuring, Evaluating, and Reporting Radioactivity in Solid Wastes and Releases of radioactive materials in Liquid and Gaseous Effluents from Cooled Nuclear Power Plants" Rev.1, June 1974 6) Reg Guide 1.23 7) Reg Guide 1.97 8) Reg Guide 1.109 "Calculation of Annual Doses to Man from Routine Releases of Reactor Effluents for the Purpose of Evaluating Compliance With 10 CFR 50, Appendix I", Rev 1, October, 1977 9) Reg Guide 1.111 "Methods for Estimating Atmospheric Transport and Dispersion of Gaseous Effluents in Routine Releases From Light-Water-Cooled Reactors", Rev.1, July, 1977 10) Reg Guide 4.8 " Environmental Technical Specifications for Nuclear Power Plants" 11) NRC Radiological Assessment Branch Technical Position, Rev 1, November 1979 (Appendix A to NUREG1302)

12) NUREG-0016

13) NUREG-0133

14) Licensing Application, Amendment 13, Meteorological Radiological Evaluation for the Oyster Creek Nuclear Power Station Site. 15) Licensing Application, Amendment 11, Question IV-8. 16) Evaluation of the Oyster Creek Nuclear Generating Station to Demonstrate Conformance to the Design Objectives of 10CFR50, Appendix I, May, 1976, Tables 3-10 17) XOQDOQ Output Files for Oyster Creek Meteorology, Murray and Trettle, Inc. 102015 CY-OC-170-301 Revision 7 Page 120of140 18) Hydrological Information and Liquid Dilution Factors Determination to Conform with Appendix I Requirements:

Oyster Creek, correspondence from T. Potter, Pickard, Lowe and Garrick, Inc. to Oyster Creek,. July, 1976. 19) Carpenter, J. J. "Recirculation and Effluent Distribution for Oyster Creek Site",

Carpenter Consultants, Baltimore, Maryland, 1964. 20) Nuclear Regulatory Commission, Generic Letter 89-01, "Implementation of Programmatic Controls for Radiological Effluent Technical Specifications in the Administrative Controls Section and Relocation of the Procedural Details of RETS to the ODCM or PCP", January, 1989. 21) Ground Water Monitoring System (Final Report), Woodward-Clyde Consultants, March, 1984. 22) Meteorology and Atomic Energy, Department of Energy, 1981. 23) SEEDS Code Documentation through V & V of Version 98.8F (Radiological Engineering Calculation No. 2820-99-005, Dated 3/23/99) 24) Lynch, Giuliano, and Associates, Inc., Drawing Entitled, "Minor Subdivision, Lots 4 and 4.01 Block 1001", signed 13 Sep 99. 25) Currie, L.A., "Lower Limit of Detection:

Definition and Elaboration of a Proposed Position for Radiological Effluent and Environmental Measurements" . 26) NUREG/CR-4007 (September 1984). 27) HASL Procedures Manual, HASL-300 (revised annually).

28) Regulatory Guide 1.113, "Estimating Aquatic Dispersion of Effluents from Accidental and Routine Reactor Releases for the Purposes of Implementing Appendix I," April 1977 29) Reg. Guide 4.13 30) 10CFR20, Appendix B, Table 2, Annual Limits on Intake (ALis) and Derived Air Concentrations (DACs) of Radionuclides for Occupational Exposure; Effluent Concentrations; Concentrations for Release to Sewerage 31) Conestoga Rovers and Associates, Hydrogeologic Investigation Report, Fleet wide Assessment, Oyster Creek Generating Station, Forked River, New Jersey, Ref. No. 045136(18), September, 2006. 32) Letter date April 23, 2013 from Murray and Trettel, Incorporated

33) Letter dated January 10, 2013 titled "Meteorology and Dose Factor Update -ODCM Revision 6" 102015 APPENDIX D -SYSTEM DRAWINGS CY-OC-170-301 Revision 7 Page 121of140 102015

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s. .s Off Spec Recycle 25,000 gal ea* c:::>-.. HP-P-2A s . 50 *-100 GPM s {} CONDENSATE PUMP SUCTION S = Sample Point "Tl G5 c ::0 m c I ...i. I ...i. er r-i5 c c c en c-t ::o m )> -I -::0 Zm en )> -< -I en s: -Im mz s: -I :::c G') :::c "ti c ::0 )> z c m 0 c "ti s: m z -I Groundwater Source CY-OC-170-301 Revision 7 Page 124of140 FIGURE D-1-1c: GROUNDWATER REMEDIATION SYSTEM Intake Batch Tank Flow Monitor Composite Sampler Flow Monitor 102015 SL-T-2A Spent Resin CY-OC-170-301 Revis i on 7 Page 125of140 FIGURE D-1-2: SOLID RAD WASTE PROCESSING SYSTEM NV-09 Decant WC-T-lC Bottoms SL-T-3A Batch Tank-SL-T-008 UF Holdup SL-T-3B Tank Dewatered Fluid From Process Liner SL-T-2B Spent Resin SL-T-009 Retentate Tank Bottoms UF Skid Penneate ,__ __ , Prefiltration Rapid Dewatering

________ Skid Water Biocide Injection Skid Option A Process Liner or HIC OptionB Low Level Rad waste Stora e Burial Site i i ---------------..! Temp Mod B/C Filter . Sludge 1020 1 5 0 N 0 ...... CJ1 STACK ::J -.aov-s L"" WAt TO SEAL POTIN SUMP AIR RECYCLE LINE AOG SYSTEM FLOW DIAGRAM rev-...... ,.,,.,_ ...... ,.,,,_ ... .... *TO SUMP .,, G) c: ::ti m c I N I ... .. G) )> "' m 0 c: "' "' -t m -t ::ti m )> -t :s: m I z -t I I )> c: G) :s: m z -t m c 0 .,, .,, G) "'ti (') )> D) -< "' (Q I 0 "' ... ::ti (') - -* ....... -t 0 0 m -o I :s: ...::::J ..........

60 min D e l ay Liae Afi-er Co nd lnt e r Co nd TURBINE DECK STACK ....... -V -7' s * ( 1-6) TURBINE BUILDING FIGURE D-2-2: VENTILATION SYSTEM V-7-31 120CFM A u g mented Offgas H V-11 4 HV-l .... <: <I) ._: .... ci a3 <I) II) i-: _, It: c <: Ef-1-7 __....,, EF-1-6 69,000n0 , 500 CFM 70 , SOOCFM EF-1-5 .,..._____,.

.___. .... ::.. ai ct HARDENED VENT PATH STANDBY GAS TREATMENT SYSTEM V-28-19 STACK CY -OC-170-301 Revision 7 Page 127of140 V-2. -22 V-2 -2 1 Dry well V-27-2 V-27-1 102015 Figure D-2-3 AOG Ventilation System DIPH I H V-S-058 RAD MONI T OR A RAD 'V HI H V-S-10 FUME HOOD V A UL T S CY-OC-170-301 Revision 7 Page 128of140 102015 CY-OC-170-301 Revision 7 Page 129of140 APPENDIX E -RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM -SAMPLE TYPE AND LOCATION All sampling locations and specific information about the individual locations are given in Table E-1. Figures E-1, E-2 and E-3 show the locations of sampling stations with respect to the site. Figure E-4 shows the site layout. 102015 CY-OC-170-301 Revision 7 Page 130of140 TABLE E-1: REMP SAMPLE LOCATIONs<

1> 1. Direct Radiation DOS -Inner Ring at or near site boundary Code {miles} {degrees}

Description 1 0.4 219 SW of site at OCGS Fire Pond, Forked River, NJ 51 0.4 358 North of site, on the access road to Forked River Site, Forked River, NJ 52 0.3 333 NNW of site, on the access road to Forked River Site, Forked River, NJ 53 0.3 309 NW of site, at sewage lift station on the access road to the Forked River Site, Forked River, NJ 54 0.3 288 WNW of site, on the access road to Forked River Site, Forked River, NJ 55 0.3 263 West of site, on Southern Area Stores security fence, west of OCGS Switchyard, Forked River, NJ 56 0.3 249 WSW of site, on utility pole east of Southern Area Stores, west of the OCGS Switchyard, Forked River, NJ 57 0.2 206 SSW of site, on Southern Area Stores access road, Forked River, NJ 58 0.2 188 South of site, on Southern Area Stores access road, Forked River, NJ 59 0.3 166 SSE of site, on Southern Area Stores access road, Waretown, NJ 61 0.3 104 ESE of site, on Route 9 south of OCGS Main Entrance, Forked River, NJ 62 0.2 83 East of site, on Route 9 at access road to OCGS Main Gate, Forked River, NJ 63 0.2 70 ENE of site, on Route 9, between main gate and OCGS North Gate access road, Forked River, NJ 64 0.3 42 NE of site, on Route 9 North at entrance to Finninger Farm, Forked River, NJ 65 0.4 19 NNE of site, on Route 9 at Intake Canal Bridge, Forked River, NJ 66 0.4 133 SE of site, east of Route 9 and south of the OCGS Discharge Canal, inside fence, Waretown, NJ 112 0.2 178 S of site, along Southern access road, Lacey Township, NJ 102015

1. CY-OC-170-301 Revision 7 Page 131of140 TABLE E-1: REMP SAMPLE LOCATIONS (CONTINUED)

Direct Radiation (Continued)

DOS -Inner Ring at or near site boundary Code (miles) (degrees}

Description 113 0.3 90 E of site, along Rt. 9 North, Lacey Township, NJ T1 0.4 219 SW of site, at OCGS Fire Pond, Lacey Township, NJ DOS -Outer Ring at 6 -8 km 4 4.6 213 SSW of Site, Garden State Parkway and Route 554, Barnegat, NJ 5 4.2 353 North of Site, Garden State Parkway Rest Area, Forked River, NJ 6 2.1 13 NNE of site, Lane Place, behind St. Pius Church, Forked River, NJ 8 2.3 177 South of site, Route 9 at the Waretown Substation, Waretown, NJ 9 2.5 230 WSW of site, where Route 532 and the Garden State Parkway meet, Waretown, NJ 22 1.6 145

SE of site, on Long John Silver Way, Skippers Cove, Waretown, NJ 46 5.6 323 NW of Site, on Lacey Road adjacent to Utility Pole BT 259 65 47 4.6 26 NNE of Site, Route 9 and Harbor Inn Road, Berkeley Township, NJ 48 4.5 189 South of Site, Intersection of Brook and School Streets, Barnegat, NJ 68 1.3 266 West of site, on Garden State Parkway North at mile marker 71.7, Lacey Township, NJ 73 1.8 108 ESE of site, on Bay Parkway, Sands Point Harbor, Waretown, NJ 74 1.8 88 East of site, Orlando Drive and Penguin Court, Forked River, NJ 75 2.0 71 ENE of site, Beach Blvd. and Maui Drive, Forked River, NJ 78 1.8 2 North of site, 1514 Arient Road, Forked River, NJ 79 2.9 160 SSE of site, Hightide Drive and Bonita Drive, Waretown, NJ 82 4.4 36 NE of site, Bay Way and Clairmore Avenue, Lanoka Harbor, NJ 84 4.4 332 NNW of site, on Lacey Road, 1.3 miles west of the Garden State Parkway on siren pole, Lacey Township, NJ 102015

1. CY-OC-170-301 Revision 7 Page 132of140 TABLE E-1: REMP SAMPLE LOCATIONS (CONTINUED)

Direct Radiation (continued)

DOS -Outer Ring at 6 -8 km (continued)

Code (miles) {degrees}

Description 85 3.9 250 WSW of site, on Route 532, just east of Wells Mills Park, Waretown, NJ 86 5.0 224 SW of site, on Route 554, 1 mile west of the Garden State Parkway, Barnegat, NJ 98 1.6 318 NW of site, on Garden State Parkway at mile marker 73.0, Lacey Township, NJ 99 1.5 310 NW of site, on Garden State Parkway at mile marker 72.8, Lacey Township, NJ 100 1.4 43 NE of site, Yacht Basin Plaza South off Lakdeside Dr., Lacey Township, NJ 101 1.7 49 NE of site, end of Lacey Rd., East, Lacey Township, NJ 102 1.6 344 NNW of site, end of Sheffield Dr., Barnegat Pines, Lacey Township, NJ 103 2.4 337 NNW of site, Llewellyn Parkway, Barnegat Pines, Lacey Township, NJ 104 1.8 221 SW of site, Rt. 532 West, before Garden State Parkway, Ocean Township, NJ 105 2.8 222 SW of site, Garden State Parkway North, beside mile marker 69.6, Ocean Township, NJ 106 1.2 288 WNW of site, Garden State Parkway North, beside mile marker 72.2 Lacey Township, NJ 107 1.3 301 WNW of Site, Garden State Parkway North, beside mile marker 72.5, Lacey Township, NJ 109 1.2 141 SE of site, Lighthouse Dr., Waretown, Ocean Township, NJ 110 1.5 127

SE of site, Tiller Drive and Admiral Way, Waretown, Ocean Township, NJ DOS -Special Interest 11 8.2 152 SSE of site, 80th and Anchor Streets, Harvey Cedars, NJ 71 1.6 164 SSE of site, on Route 532 at the Waretown Municipal Building, Waretown, NJ 72 1.9 25 NNE of site, on Lacey Road at Knights of Columbus Hall, Forked River, NJ 102015

1. CY-OC-170-301 Revision 7 Page 133of140 TABLE E-1: REMP SAMPLE LOCATIONS (CONTINUED)

Direct Radiation (continued)

DOS -Special Interest (continued)

Code (miles} 81 3.5 88 6.6 89 6.1 90 6.3 92 9.0 3 6.0 DOS -Background c 24.7 14 20.8 (degrees}

201 125 108 75 46 97 313 2 Description SSW of site, on Rose Hill Road at intersection with Barnegat Boulevard, Barnegat, NJ SE of site, eastern end of 3rd Street, Barnegat Light, NJ ESE of site, Job Francis residence, Island Beach State Park ENE of site, parking lot A-5, Island Beach State Park NE of site, at Guard Shack/Toll Booth, Island Beach State Park East of site, near old Coast Guard Station, Island Beach State Park Special Interest Area NW of site, JCP&L office in rear parking lot, Cookstown, NJ North of site, Larrabee Substation on Randolph Road, Lakewood, NJ 2. Airborne -Radioiodines and Particulates APT, AIO -At or near site boundary in highest D/Q Sectors 20 0. 7 95 East of site, on Finninger Farm on south side of access road, Forked River, NJ 66 0.4 133 SE of site, east of Route 9 and south of the OCGS Discharge Canal, inside fence, Waretown, NJ 111 0.3 64 ENE of site, Finninger Farm property along access road, Lacey Township, NJ APT, AIO -Special Interest 71 1.6 164 72 1.9 25 73 1.8 108 3 6.0 97 SSE of site, on Route 532 at the Waretown Municipal Building, Waretown, NJ NNE of site, on Lacey Road at Knights of Columbus Hall, Forked River, NJ ESE of site, on Bay Parkway, Sands Point Harbor, Waretown, NJ East of site, near old Coast Guard Station, Island Beach State Park Special Interest Area 102015 CY-OC-170-301 Revision 7 Page 134of140 TABLE E-1: REMP SAMPLE LOCATIONS (CONTINUED)

2. Airborne -Radioiodines and Particulates (continued)

APT, AIO -Backgound(continued)

Code (miles) (degrees) c 24.7 313 3. Waterborne SWA -Surface 23 3.6 24 2.1 33 0.4 SWA -Backgound 94 20.0 GW-Ground W-3C 0.4 MW-24-3A 0.8 DW -Drinking 1S 0.1 1N 0.2 38 1.6 114 0.8 DW -Backgound 37 2.2 AQS -Sediment 23 3.6 24 2.1 33 0.4 64 101 123 198 112 97 209 349 197 267 18 64 101 123 Description NW of site, JCP&L office in rear parking lot, Cookstown, NJ ENE of site, Barnegat Bay off Stouts Creek, approximately 400 yards SE of "Flashing Light 1" East of site, Barnegat Bay, approximately 250 yards SE of "Flashing Light 3" ESE of site, east of Route 9 Bridge in OCGS Discharge Canal SSW of site, in Great Bay/Little Egg Harbor ESE of site on Finninger Farm adjacent to Station 35, Lacey Township, NJ E of site on Finninger Farm on South side of access road, Lacey Township, NJ On-site southern domestic well at OCGS, Forked River, NJ On-site northern domestic well at OCGS, Forked River, NJ SSW of Site, on Route 532, at Ocean Township MUA Pumping Station, Waretown, NJ Well at Bldg 25 on Forked River site NNE of Site, off Boox Road at Lacey MUA Pumping Station, Forked River, NJ ENE of site, Barnegat Bay off Stouts Creek, approximately 400 yards SE of "Flashing Light 1" East of site, Barnegat Bay, approximately 250 yards SE of "Flashing Light 3" ESE of site, east of Route 9 Bridge in OCGS Discharge Canal 102015 CY-OC-170-301 Revision 7 Page 135of140 TABLE E-1: REMP SAMPLE LOCATIONS (CONTINUED)

3. Waterborne (continued)

AQS -Backgound Code (miles) (degrees) 94 20.0 198 4. Ingestion FISH -Fish 93 0.1 FISH -Backgound 94 20.0 CLAM-Clams 23 3.6 24 2.1 CLAM -Backgound 94 20.0 CRAB-Crabs 33 0.4 93 0.1 VEG -Vegetation 35 0.4 66 0.4 115 0.3 VEG -Backgound 36 23.1 242 198 64 101 198 123 242 111 133 96 319 Description SSW of site, in Great Bay/Little Egg Harbor WSW of site, OCGS Discharge Canal between Pump Discharges and Route 9, Forked River, NJ SSW of site, in Great Bay/Little Egg Harbor ENE of site, Barnegat Bay off Stouts Creek, approximately 400 yards SE of "Flashing Light 1" East of site, Barnegat Bay, approximately 250 yards SE of "Flashing Light 3" SSW of site, in Great Bay/Little Egg Harbor ESE of site, east of Route 9 Bridge in OCGS Discharge Canal WSW of site, OCGS Discharge Canal between Pump Discharges and Route 9, Forked River, NJ ESE of site, east of Route 9 and north of the OCGS Discharge Canal, Forked River, NJ SE of site, east of Route 9 and south of the OCGS Discharge Canal, inside fence, Waretown, NJ East of Site, on Finninger Farm NW of site, at "U-Pick" Farm, New Egypt, NJ 102015 SAMPLE MEDIUM IDENTIFICATION KEY APT = Air Particulate AIO = Air Iodine VEG = Vegetables SWA = Surface Water AQS = Aquatic Sediment CLAM= Clams DW = Drinking Water DOS = Dosimeter FISH= Fish CRAB =Crab CY-OC-170-301 Revision 7 Page 136of140 GW = Ground Water (1) Samples may not be collected from some locations listed in this table, as long as the minimum number of samples listed in Table 3.12.1-1 is collected.

102015

\ / l / II FIGURE E-1 Oys er Creek Generating Sta.tion REi P S mple Loca tions within a 1 ile Rad i us a.1:. D ILll-CY-OC-170-301 Revision 7 Page 137of140 s 102015 w FIGURE E-2 Oyster Creek Generating Sta ion RE P S mple llocati.ons within a 1 to 5 . ile Radms 0.7. D U I CY-OC-170-301 Revision 7 Page 138of140 s E * .,.i II 1'1 1 5 1020 1 5 FIGURE E-3 Oyster Creek Generating Station REMP Sample ll ocat i ons over a 5 Mile Radius !II _c::::i_:::::::J

___ _ CY-OC-170-301 Revision 7 Page 139of 1 40 N ** s 0'1te: -7 11 2 102015 FIGURE E-4 AREA PLOT PLAN OF SITE CY-OC-170-301 Revision 7 Page 140of140 SITE MAP DEFINING UNRESTRICTED AREAS AND SITE BOUNDARY FOR RADIOACTIVE GASEOUS AND LIQUID EFFLUENTS Sector s SSW SW WSW w WNW NW NNW Site Boundary Distances Distance in meters 348 291 229 260 239 284 364 474 Sector N NNE NE ENE E ESE SE SSE Distance in meters 584 621 373 338 360 491 544 395 102015 Exelon Generation RA-16-039 April 29, 2016 U.S. Nuclear Regulatory Commission Attn: Document Control Desk Washington , DC 20555 -0001 10 CFR 50.36a(a)(2) 10 CFR 72.44 ( d)(3) Technical Specification 6.9.1.d Oyster Creek Nuclear Generating Station Renewed Facility Operating License No. DPR-16 NRC Docket No. 50-219 lndependentSpent Fuel Storage Facility NRC Docket No. 72-15

Subject:

Annual Radioactive Effluent Release Report for 2015 Enclosed with this cover letter is the Annual Radioactive Effluent Release Report for the period January 1 to December 31 , 2015. This report includes the Oyster Creek Nuclear Generating Station Independent Spent Fuel Storage Facility.

If any further information or assistance i s needed , please contact John Renda , Chemistry Manager, at 609-971-2572.

Sincerely , Site Vice President Oyster Creek Nuclear Generating Station

Enclosure:

2015 Annual Radioactive Effluent Release Report cc: Administrator , USNRC Region I USNRC Senior Project Manager , Oyster Creek USNRC Senior Resident Inspector , Oyster Creek C r a i g Stewart , American Nuclear Insurers Exelon Generation Annual Radioactive Effluent Release Report 2015 Oyster Creek Generating Station Oyster Creek 2015 Annual Radioactive Effluent Release Report ANNUAL RADIOACTIVE EFFLUENT RELEASE REPORT January 1, 2015 through December 31, 2015 EXELON GENERATION COMPANY, llC OYSTER CREEK GENERATING STATION DOCKET NO. 50-219 (Oyster Creek Generating Station) DOCKET NO. 72-15 (Independent Spent Fuel Storage Facility)

Submitted to The United States Nuclear Regulatory Commission Pursuant to Renewed Facility Operating License DPR-16 Oyster Creek 2015 Annual Radioactive Effluent Release Report TABLE OF CONTENTS SECTION EXECUTIVE

SUMMARY

1. Sources of Rad i at i on Dose to the U.S. Populat i on 2. Exposure Pathways 3. Introduction

4. Supplemental Information A Regulatory Lim i ts B Effluent Concentration L i mits C Average Energy D Measurements and Approximations of Total Radioactivity E Batch Releases F Abnormal Releases G Revisions to the ODCM H Radiation Effluent Monitors Out of Service More Than 30 Days Releases from the Independent Spent Fuel Storage Facility J Program Dev i ations Appendix A -Effluent and Waste D i sposal Summary Appendix B -Solid Waste and Irradiated Fuel Sh i pments Appendix C -Radiological Impact to Man Appendix D -Meteorolog i ca l Data Appendix E -ODCM Rev i sions Appendix F -ERRATA ii PAGE 3 5 7 8 8 9 9 9 13 13 13 13 14 14 15 22 29 32 106 107 Oyster Creek 2015 Annual Radioactive Effluent Release Report (Page Intentionally Left B l ank) iii Oyster Creek 2015 Annual Radioactive Effluent Release Report EXECUTIVE

SUMMARY

Effluents are strictly monitored to ensure that radioactivity released to the env i ronment is as low as reasonably achievable and does not exceed regulatory limits. Effluent control includes the operation of monitoring systems , in-plant and environmental sampling and analyses programs , quality assurance programs for the effluent and environmental programs , and procedures covering all aspects of effluent and environmental mon i toring. Both radiological environmental and effluent monitoring indicate that the operation of Oyster Creek Generating Station (OCGS) does not result in significant rad i ation exposure to the people or the environment surrounding OCGS and is well below the applicable levels set by the Nuclear Regulatory Commission (NRC) and the Environmental Protection Agency (EPA). There were liquid radioactive effluent releases during 2015 of concentrations of trit i um too low to detect at an LLD of 200 picocuries per liter (pCi/L) at the New Jersey Pollution Discharge Elimination System (NJPDES) permitted main condenser outfall. The releases were part of nearly continuous pumping of groundwater at approximately 70 gpm containing low levels of tritium and no detectable gamma. Exelon and the State of New Jersey Department of Environmental Protection (NJDEP) agreed to this remediation action instead of natural attenuat i on to address concentrations of tritium in groundwater. Well 73 and supporting equipment and piping were installed to pump groundwater to the intake structure at the inlet of the main circulating water pumps. Provis i ons were established for both batch and continuous releases of groundwater. Continuous releases occurred approximately 277 days in 2015. The nearly continuous releases occurred from January 1 , 2015 through January 30 , 2015 and April 27 , 2015 through December 31 , 2015 with a total of 2. 78E+07 gallons of groundwater pumped resulting in 2.08E-01 Ci of tritium released to the discharge canal. The dose to the most limiting member of the public due to the release of groundwater was 9.86E-07 mrem. There were no liquid abnormal releases during 2015. There were no gaseous abnormal releases during 2015. The maximum calculated organ dose (Bone) from iodines , tritium , carbon-14 (C-14), and particulates to any individual due to gaseous effluents was 5.53E-01 mrem , which was approximately 3.69E+OO percent of the annual limit of 15 mrem. The majority of organ dose from gaseous effluents was due to C-14. The maximum calculated gamma air dose in the UNRESTRICTED AREA due to noble gas effluents was 4.86E-03 mrad , which was 4.86E-02 percent of the annual 10 CFR 50 Appendix I , As Low As Reasonably Achievable (ALARA) limit of 10 mrad. For comparison , the background radiation dose averages approximately 620 mrem per year to the average person in the United States. The Independent Spent Fuel Storage Installation (ISFSI) is a closed system and the only exposure is due to direct radiation. Based on offsite TLD readings , dose due to direct radiation from the ISFSI was less than 1 mrem for 2015. Because it is a sealed unit , no radioactive material was released. 1 Oyster Creek 2015 Annual Radioactive Effluent Release Report Comparison of environmental sampling results to iodine and particulate gaseous effluents released , showed no radioactivity attributable to the operation of OCGS. Both elevated and ground-level release paths were considered in this review , with total iodines released of 4.30E-03 Ci and total particulates with half-lives greater than 8 days less C-14 released of 2.69E-02 C i. Joint Frequency Tables of meteorological data , per Stability Classification Category , as well as for all stability classes , are included. All data was collected from the on-site Meteorological Facility. Data recoveries for the 380-foot data and the 33-foot data were 99.8 percent and 99.8 percent , respectively. The UFSAR commits to Regulatory Guide (RG) 1.23 for Meteorological Facility data recovery. RG 1.23 requires data recovery of at least 90% on an annual basis. 2 Oyster Creek 2015 Annual Radioactive Effluent Release Report 1 Sources of Radiation Dose to the U.S. Population Note: The information in th i s section is from the following NRC report: Radioactive Effluents from Nuclear Power Plants: Annual Report 2007 For comparison with Nuclear Power Plant (NPP) effluents , this section provides a perspective on the doses that Americans typically receive on average from natural and background rad i ation. In March 2009 , the National Council on Radiation Protection and Measurements (NCRP) published Report No. 160 as an update to the 1987 NCRP Report No. 93 , Ionizing Radiation Exposure of the Population of the United States (Refs. 28 , 29). Report No. 160 describes the doses to the U.S. population from all sources of ionizing radiation for 2006 , the most recent data available at the time the report was written. The report also includes information on the variability of those doses from one individual to another. The NCRP estimated that the average pe r son i n the United States receives the equivalent of about 620 mrem of radiation dose each year. NCRP Report No. 160 describes each of the sources of radiation that contr i bute to this dose , including: 1. naturally-occurring sources (natural background) such as cosmic rad i ation from space , terrestrial radiat i on from rad i oactive materials i n the earth , and naturally occurring radioactive materials in food people eat and air people breathe; 2. medical sources from diagnosis and treatment of health disorders using radioactive pharmaceuticals and radiation-producing equipment; 3. consumer products; 4. industrial processes , secur i ty devices , educational tools , and research activities

5. exposures of workers that result from their occupations. Figure 1.1 is a pie chart showing the relative contribut i ons of these sources to radiat i on dose to the U.S. popu l at i on. La r ge r r elat iv e cont ri butors to dose are represented by proportionally larger sl i ces of the pie. Doses to the publ i c from nuclear power generation are included in the industrial category; doses to workers from nuclear power generation are included in the category of occupational dose. Doses to the public due to effluents from NPPs are less than 0.1 % of what the average person rece i ves each year from all sources of radiation.

Doses to workers from occupational exposures , including those rece i ved from work at NPPs , also are less than 0.1 % of the average dose to a member of the public from all sources. 3 Oyste r Creek 2015 Annua l Radioact i ve Effluent Release Report FIGURE 1.1 Sou r ces of Rad i ation Exposure to the U.S. Population Indu s trial Ra don & th o ron (b a ck gr oun d) 37% inclu des doses to the public from nuclear power generation

<0.1% O ccup a ti o nal i ncludes doses to w orkers from nuclear power generation

<0.1% Con sume r 2% Conven ti ona l r ad iogr a phy I fluoroscopy (m ed ic a l) 5% Sp a ce (back g roun d) 5% l nte rv e n t i o n a l flouroscopy (med i caQ 7% In te rn al (bacf(ground) 5% T e rr e stri a l (b ackg round) 3% N ucl e ar m e dicine (m edical) 12% C ompu te d tomogr a phy (medical) 24% Percent contribut i on of various so u rces of exposure to the total collect i ve effective dose and the total effective dose per i ndividual in the U.S. population for 2006. Percent values have been rounded to the nearest 1 %, except fo r those <1 % [less than 1 %]. Credit: Mod i ficat i on to i mage courtesy of National Counc i l on Radia ti on Protection and Measurements. 4 Oyster Creek 2015 Annual Radioactive Effluent Release Report 2 Exposure Pathways Radiological exposure pathways define the methods by which people may become exposed to radioactive material.

The major pathways of concern are those which could cause the highest calculated radiation dose. These projected pathways are determined from the type and amount of radioactive material released , the environmental transport mechanism, and the use of the environment.

The e nvi ro n me n tal tra n sport mechan i sm includes consideration of physical factors , such as the hydrological (water) and meteorological (weather) characteristics of the area. An annual average of the water flow , wind speed , and wind direction are used to evaluate how the radionuclides will be distributed in an area for gaseous or liquid releases. An important factor in evaluating the exposure pathways is the use of the environment.

Many factors are considered such as dietary intake of residents, recreational use of the area , and the locations of homes and farms in the area. The external and internal exposure pathways considered are shown in Figure 2.1. The release of radioactive gaseous effluents involves pathways such as external whole body exposure , deposition of radioactive material on plants , deposition on soil , inhalation by animals destined for human consumption , and inhalation by humans. The release of radioactive material in liquid effluents involves pathways such as drinking water, fish , and direct exposure from the water at the shoreline while swimming. Although radionuclides can reach humans by many different pathways, some result in more dose than others. The critical pathway is the exposure route that will provide , for a specific radionuclide , the greatest dose to a population , or to a specific group of the population called the critical group. The critical group may vary depending on the radionuclides involved , the age and diet of the group, or other cultural factors. The dose may be delivered to the whole body or to a specific organ. The organ receiving the greatest fraction of the dose is called the critical organ. 5 Oyster Creek 2015 Annual Radioactive Effluent Release Report FIGURE 2.1 Exposure Pathways ,,,.. I nhalation.

tnlnspiralion and submersion D ri n king Surfac e W a t e r or G r oun-This simple diagram demonstrates some potential exposure pathways from Oyster Creek Generating Station. 6 Oyster Creek 2015 Annual Radioactive Effluent Release Report 3 Introduction In accordance with the reporting requirements of Technical Specification 6.9.1.d applicable during the reporting period, this report summarizes the effluent release data for OCGS for the period January 1, 2015 through December 31, 2015. This submittal complies with the format described in Regulatory Guide 1.21, "Measurin.Q, Evaluatin.Q and Reporting Radioactivity in Solid Wastes and Releases of Radioadiw Mafetiafs fn tfqufd and Gaseous Effluents from Water-Cooled Nuclear Power Plants", Revision 1, June 1974. Meteorological data was reported in the format specified in Regulatory Guide 1.23, Revision 1, "Meteorological Monitoring Programs for Nuclear Power Plants". All vendor results were received and included in the report calculations.

Therefore the 2015 report is complete.

7 Oyster Creek 2015 Annual Radioactive Effluent Release Report 4 Supplemental Information Oyster Creek Generating Station Exelon Generation Company, LLC A. Regulatory Limits: LimJt UnJts 1. Noble Gases: a. .::5.500 mrem/yr Total Body .::5.3000 mrem/yr Skin b. ,::5.5 mrad AirGamma .::: 10 mrad Air Beta c. .::: 10 mrad AirGamma ,::5.20 mrad Air Beta d. <5 mrem Total Body (Gamma) < 15 mrem Skin (Beta) 2. Iodines, Tritium, Particulates with Half Life > 8 days: ODCM and lO CFR 50, Appendix I Design Objective Limits ODCM Control 3.11.2.1 Quarterly air dose limits ODCM Control 3.11.2.2 Yearly air dose limits ODCM Control 3.11.2.2 10 CFR 50, Appendix I, Section ll.B.2(b)

a. .::, 1500 mrem/yr Any Organ ODCM Control 3.11.2.1 b. .::. 7.5 mrem Any Organ Quarterly dose limits ODCM Control 3.11.2.3 c. .::. 15 mrem Any Organ

Yearly dose limits ODCM Control 3.11.2.3 3. Liquid Effluents: