ML022890509

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Revision to Emergency Plan Implementing Procedures for R.E. Ginna Nuclear Power Plant
ML022890509
Person / Time
Site: Ginna Constellation icon.png
Issue date: 10/08/2002
From: Watts R
Rochester Gas & Electric Corp
To: Clark R
Document Control Desk, NRC/NRR/DLPM/LPD1
References
Download: ML022890509 (35)
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Text

I A A Subsidiary of RGS Energy Group, Inc www rge corn ROCHESTER GAS AND ELECTRIC CORPORATION

  • 89 EAST AVENUE, ROCHESTER, N Y 14649-0001 @ 716 546-2700 October 8, 2002 U.S. Nuclear Regulatory Commission Document Control Desk Washington, DC 20555 Attn: Mr. Robert Clark (Mail Stop O-8-E9)

Project Directorate I-1

Subject:

Revision to Emergency Plan Implementing Procedures R.E. Ginna Nuclear Power Plant Docket No. 50-244 Gentlemen:

In accordance with 10 CFR 50.4(b)(5), enclosed are revisions to Ginna Station Emergency Plan Implementing Procedures (EPIP).

do We have determined, per the requirements of 10 CFR 50.54(q), that the procedure changes not decrease the effectiveness of our Nuclear Emergency Response Plan.

Very truly yours, Richard J. Watts Manager, Nuclear Training Department Enclosures xc: USNRC Region 1 (2 copies of letter and 2 copies of each procedure)

Resident Inspector, Ginna Station (1 copy of letter and 1 copy of each procedure)

RG&E Nuclear Safety and Licensing (1 copy of letter)

Dr. Robert C. Mecredy (2 copies of letter only)

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U.S. Nuclear Regulatory Commission October 8, 2002 Page 2 of 2 PROCEDURE REVISION NUMBER EPIP 2-14 15 EPIP 2-15 6 EPIP 3-1 19 EPIP 3-7 10 EPIP 4-3 11 EPIP 4-8 0 EPIP 4-9 0 EPIP 5-9 7

( -C C GINNA NUCLEAR POWER PLANT 10/08/02 PAGE: 1 REPORT NO. 01 REPORT: NPSP0200 PROCEDURES INDEX DOC TYPE: PREPIP EMERGENCY PLAN IMPLEMENTING PROCEDURE PARAMETERS: DOC TYPESS - PREPIP STATUS: EF 5 (EARS ONLY:

EFFECT LAST NEXT PROCEDURE REVIEW REVIEW REV DATE ST NUMBER PROCEDURE TITLE 028 05/15/02 05/15/02 05/15/07 EF EPIP-1-0 GINNA STATION EVENT EVALUATION AND CLASSIFICATION 003 11/02/01 11/02/01 11/02/06 EF EPIP-1-1 UNUSUAL EVENT 004 11/02/01 11/02/01 11/02/06 EF EPIP-1-2 ALERT 005 12/09/96 01/23/98 01/20/03 EF EPIP-1-3 SITE AREA EMERGENCY 005 11/02/01 11/02/01 11/02/06 EF EPIP-1-4 GENERAL EMERGENCY 050 08/09/02 08/09/02 08/09/07 EF EPIP-1-5 NOTIFICATIONS 014 08/09/02 08/09/02 08/09/07 EF EPIP-1-6 SITE EVACUATION 009 11/02/01 11/02/01 11/02/06 EF EPIP-1-7 ACCOUNTABILITY OF PERSONNEL 005 12/20/01 12/20/01 12/20/06 EF EPIP-1-8 SEARCH AND RESCUE OPERATION 021 12/20/01 12/20/01 12/20/06 EF EPIP-1-9 TECHNICAL SUPPORT CENTER ACTIVATION 011 08/09/02 08/09/02 08/09/07 EF EPIP-1-1O OPERATIONAL SUPPORT CENTER (OSC) ACTIVATION 027 08/30/02 08/30/02 08/30/07 EF EPIP-1-11 SURVEY CENTER ACTIVATION 009 12/20/01 12/20/01 12/20/06 EF EPIP-1-12 REPAIR AND CORRECTIVE ACTION GUIDELINES DURING EMERGENCY SITUATIONS 003 08/04/95 01/23/98 01/23/03 EF EPIP-1-13 LOCAL RADIATION EMERGENCY 005 04/24/96 03/03/99 03/03/04 EF EPIP-1-15 USE OF THE HEALTH PHYSICS NETWORK HPN 004 02/13/98 02/13/98 02/13/03 EF EPIP-1-16 RADIOACTIVE LIQUID RELEASE TO LAKE ONTARIO OR DEER CREEK 002 06/21/00 06/21/00 06/21/05 EF EPIP-1-17 PLANNING FOR ADVERSE WEATHER 005 08/30/02 08/30/02 08/30/07 EF EPIP-1-18 DISCRETIONARY ACTIONS FOR EMERGENCY CONDITIONS 019 06/04/01 06/04/01 06/04/06 EF EPIP-2-1 PROTECTIVE ACTION RECOMMENDATIONS 012 07/01/02 07/01/02 07/01/07 EF EPIP-2-2 OBTAINING METEOROLOGICAL DATA AND FORECASTS AND THEIR USE IN EMERGENCY DOSE ASSESSMENT 07/01/02 07/01/02 07/01/07 EF EMERGENCY RELEASE RATE DETERMINATION 015 EPIP-2-3 013 07/20/01 07/20/01 07/20/06 EF EPIP-2-4 EMERGENCY DOSE PROJECTIONS - MANUAL METHOD 014 05/15/02 05/15/02 05/15/07 EF EPIP-2-5 EMERGENCY DOSE PROJECTIONS PERSONAL COMPUTER METHOD 011 06/21/00 06/21/00 06/21/05 EF EPIP-2-6 EMERGENCY DOSE PROJECTIONS - MIDAS PROGRAM

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REPORT NO. 01 GINNA NUCLEAR POWER PLANT 10/08/02 PAGE- 2 REPORT: NPSP0200 PROCEDURES INDEX DOC TYPE: PREPIP EMERGENCY PLAN IMPLEMENTING PROCEDURE PARAMETERS: DOC TYPES - PREPIP STATUS: EF 5 YEARS ONLY:

PROCEDURE EFFECT LAST NEXT NUMBER PROCEDURE TITLE REV DATE REVIEW REVIEW ST EPIP-2-7 MANAGEMENM OF EMERGENCY SURVEY TEAMS 011 08/09/02 08/09/02 08/09/07 EF EPIP-2-8 VOLUNTARY ACCEPTANCE OF EMERGENCY RADIATION EXPOSURE 005 05/16/00 05/16/00 05/16/05 EF EPIP-2-9 ADMINISTRATION OF POTASSIUM IODIDE (KI) 006 08/30/02 08/30/02 08/30/07 EF EPIP-2-10 INPLANT RADIATION SURVEYS 004 08/09/02 08/09/02 08/09/07 EF EPIP-2-11 ONSITE SURVEYS 019 05/15/02 05/15/02 05/15/07 EF EPIP-2-12 OFFSITE SURVEYS 022 05/15/02 os/15/02 05/15/07 EF EPIP-2-13 IODINE AND PARTICULATE ACTIVITY DETERMINATION FROM AIR SAMPLES 008 07/27/99 07/27/99 07/27/04 EF EPIP-2-14 POST PLUME ENVIRONMENTAL SAMPLING 015 10/08/02 10/08/02 10/08/07 EF EPIP-2-15 POST PLUME EVALUATION OF OFFSITE DOSES DUE TO DEPOSITION 006 10/08/02 10/08/02 10/08/07 EF EPIP-2-16 CORE DAMAGE ESTIMATION 012 07/01/02 07/01/02 07/01/07 EF EPIP-2-17 HYPOTHETICAL (PRE-RELEASE) DOSE ESTIMATES 007 03/01/02 03/01/02 03/01/07 EF EPIP-2-18 CONTROL ROOM DOSE ASSESSMENT 014 05/15/02 05/15/02 05/15/07 EF EMERGENCY OPERATIONS FACILITY (EOF) ACTIVATION AND OPERATIONS 019 10/08/02 10/08/02 10/08/07 EF EPIP-3-1 ENGINEERING SUPPORT CENTER (ESC) 010 08/09/02 08/09/02 08/09/07 EF EPIP-3-2 EPIP-3-3 IMMEDIATE ENTRY 008 12/20/01 12/20/01 12/20/06 EF EMERGENCY TERMINATION AND RECOVERY 008 03112/01 03/12/01 03/12/06 EF EPIP-3-4 SECURITY DURING EMERGENCIES 010 10/08/02 10/08/02 10/08/07 EF EPIP-3-7 PUBLIC INFORMATION RESPONSE TO AN UNUSUAL EVENT 006 02/13/98 02/13/98 02/13/03 EF EPIP-4-1 ACCIDENTAL ACTIVATION OF GINNA EMERGENCY NOTIFICATION SYSTEM SIRENS 011 10/08/02 10/08/02 10/08/07 EF EPIP-4-3 009 08/31/01 08/31/01 08/31/06 EF EPIP-4-6 JOINT EMERGENCY NEWS CENTER ACTIVATION 020 06/11/02 06/11/02 06/11/07 EF EPIP-4-7 PUBLIC INFORMATION ORGANIZATION STAFFING 000 10/08/02 10/08/02 10/08/02 EF EPIP-4-9 ACTIVATION OF GINNA EMERGENCY SIRENS FROM THE TECHNICAL SUPPORT CENTER OFFSITE EMERGENCY RESPONSE FACILITIES AND EQUIPMENT PERIODIC INVENTO RY 026 08/30/02 08/30/02 08/30/07 EF EPIP-5-1 CHECKS AND TESTS

C 1.____ C REPORT NO. 01 GINNA NUCLEAR POWER PLANT 10/08/02 PAGE: 3 REPORT: NPSP0200 PROCEDURES INDEX DOC TYPE: PREPIP EMERGENCY PLAN IMPLEMENTING PROCEDURE PARAMETERS: DOC TYPES - PREPIP STATUS: EF 5 YEARS ONLY:

PROCEDURE EFFECT LAST NEXT NUMBER PROCEDURE TITLE REV DATE REVIEW REVIEW ST EPIP-5-2 ONSITE EMERGENCY RESPONSE FACILITIES AND EQUIPMENT PERIODIC INVENTORY 029 08/30/02 08/30/02 08/30/07 EF CHECKS AND TESTS EPIP-5-5 CONDUCT OF DRILLS AND EXERCISES 014 07/01/02 07/01/02 07/01/07 EF EPIP-5-6 ANNUAL REVIEW OF NUCLEAR EMERGENCY RESPONSE PLAN (NERP) 004 05/28/99 05/28/99 05/28/04 EF EPIP-5-7 EMERGENCY ORGANIZATION 038 08/30/02 08/30/02 08/30/07 EF EPIP-5-9 TESTING THE OFF HOURS CALL-IN PROCEDURE AND QUARTERLY TELEPHONE NUMBER 007 10/08/02 10/08/02 10/08/07 EF CHECK EPIP-5-10 EMERGENCY RESPONSE DATA SYSTEM (ERDS) 006 03/28/02 03/28/02 03/28/07 EF NERP GINNA STATION NUCLEAR EMERGENCY RESPONSE PLAN 020 03/21/01 03/21/01 12/09/04 EF TOTAL FOR PREPIP 54

ROCHESTER GAS AND ELECTRIC CORPORATION GINNA STATION CONTROLLED COPY NUMBER -23 PROCEDURE NO. EPIP 2-14 REV. NO. 15 POST PLUME ENVIRONMENTAL SAMPLING RE &PONS/BLE GER 10E V DATE EEFFFFCTIVE DATE Category 1.0 This procedure contains 20 pages

EPIP 2-14:1 POST PLUME ENVIRONMENTAL SAMPLING

1.0 PURPOSE

1.1 The purpose of the procedure is to provide guidance for the survey teams in the collection of environmental sample media, e.g, snow, grass, soil, vegetation, air samples, water samples and TLD collection.

2.0 RESPONSIBILITY

2.1 The Dose Assessment Manager is responsible for implementing this procedure.

3.0 REFERENCES

3.1 Development References 3.1.1 Nuclear Emergency Response Plan 3.2 Implementing References 3.2.1 EPIP 2-11, Onsite Surveys 3.2.2 EPIP 2-12, Offsite Surveys 3.2.3 EPIP 2-8, Voluntary Acceptance of Emergency Radiation Exposure 3.2.4 EPIP 2-9, Administration of Potassium Iodine (KI) 3.2.5 RP-TLD-710A-OPS, Operation of Panasonic UD-710A TLD Reader

4.0 PRECAUTIONS

None.

5.0 PREREQUISITES

None.

6.0 ACTIONS

6.1 Team Briefing 6.1.1 Survey Center Manager or the Dose Assessment Manager brief the Survey Team Members.

EPIP 2-14:2 6.1.2 Ensure that the briefing covers the following items:

a. Team identification
b. Communications equipment and channel
c. Use of 3-way communications and the phonetic alphabet.
d. Protective equipment (including use of KI)
e. Authorized doses
f. Survey instructions
g. Type of data required
h. Survey equipment L. Job safety briefing 6.1.3 If dose authorization is required, implement EPIP 2-8, Voluntary Acceptance of Emergency Radiation Exposure.

6.1.4 Ifpotassium iodine (KI) administration is required, take one KI tablet at this time in accordance with EPIP 2-9, Administration of Potassium Iodine (KI),

6.2 Equipment Check/Team Preparation Assemble the following equipment which is not stored in the survey footlocker:

a. Personal thermoluminescent dosimeter (TLD) for each team member.
b. One 0-1500 mR dosimeter and 0-10R dosimeter for each team member.

Sign in on the dosimeter log sheet.

c. One full-face mask with charcoal filter and voice amplifier for each team member.
d. Pack of six environmental TLD's from lead storage container
e. Motorola GM 300 Mobile radio and magnetic mount antenna
f. Gilian air sampler with filter holder micro R meter
g. RM-25 (or equivalent) radiation monitor with HP-260 probe or
h. Eberline RO-20 dose rate meter
i. RADECO H-809C Portable High Volume Air Sampler with filter holder.
j. Tools for obtaining specific types of samples, as may be necessary

EPIP 2-14:3

k. Clean plastic bags for holding samples I. Cellular mobile phone 6.2.2 Check operation of the following equipment using the Equipment Check and Operation Instructions contained in Attachment 1-8 of EPIP 2-12, Offsite Surveys:
a. Radio System - Motorola GM 300 (Attachment 1)
b. NEC M3800 Cellular Mobile Telephone (Attachment 2)
c. Eberline Model RM-25 (or equivalent) Frisker with HP -260 probe (Attachment 3)
d. Eberline Model RO-20 Dose Rate Meter (Attachment 4)
e. Bicron Micro REM Meter (Attachment 5)
f. GILIAN HFS-1 13, HFS-513A and GILAIR-5 Low Volume Air Samplers (Attachment 6)
g. RADECO H-809C High Volume Air Sampler (Attachment 7)
h. VAS-2 Earmark "Loud Mouth" Voice Amplification System (Attachment 8) 6.2.3 Obtain transportation and check vehicle for contamination by performing a direct frisk survey on the horizontal surfaces with the HP-260 probe and count rate meter (RM 14 or equivalent) in accordance with Attachment 6.

6.2.4 If the vehicle survey indicates surface contamination greater than 250 cpm above background, contact the Survey Center Manager for instructions.

6.2.5 Load survey equipment into vehicle, fill in Survey Team Status Board, and inform Survey Center Manager you are ready for departure. (Alternatively, team may be deployed from EOF by Dose Assessment Manager).

6.2.6 Log time, date, and survey team members on survey map.

6.2.7 Establish radio communications with Technical Support Center or EOF Radio Operator as appropriate and advise of teams departure.

6.2.8 If directed by the Dose Assessment Manager, don protective clothing and full face masks with iodine filters.

EPIP 2-14:4 REFER TO THE FOLLOWING SECTIONS FOR SPECIFIC SAMPLING TASKS:

Section 6.3 - TLD Placement and Collection Section 6.4 - Post Accident Environmental Monitoring Section 6.5 - Water Sampling Section 6.6 - Milk Sampling Section 6.7 - Snow Sampling Section 6.8 - Land Sampling for Contamination Section 6.9 - Grass Sampling Section 6.10 - Non Grass Areas Section 6.11 - Vegetation Sampling 6.3 TLD Placement and Collection 6.3.1 Place or replace environmental TLD's at the locations shown on Attachment 2 6.3.2 TLDs may be collected as deemed necessary by the Dose Assessment Manager, to evaluate the radiation doses to the environs. Consider collecting TLDs after 4 hours4.62963e-5 days <br />0.00111 hours <br />6.613757e-6 weeks <br />1.522e-6 months <br />, 1 day or 7 days depending on release duration and release magnitude.

6.3.3 Refer to Attachment 1 for direction and distance of permanent TLDs.

6.4 Post-Accident Environmental Monitoring 6.4.1 The Dose Assessment Manager may send individuals to collect these filters as he deems necessary.

6.4.2 Instructions for changing the filters are included inside of each sample station.

Attachment 3 shows onsite air monitoring stations.

6.4.3 Fall out precipitation collectors may be exchanged and analyzed before the scheduled time in order to aid in evaluating the releases.

6.4.4 Refer to Attachment 1 for direction and distance of sample stations.

6.5 Water Sampling NOTE: NO RADIOACTIVITY IS NORMALLY FOUND IN WATER SAMPLES WITH THE EXCEPTION OF NATURALLY OCCURRING K-40.

6.5.1 Water samples from Deer Creek and/or Lake Ontario should be taken as appropriate for the type and direction of release as deemed necessary by the Dose Assessment Manager.

EPIP 2-14:5 6.5.2 Refer to Attachment 1 for direction and distance of Water Sampling locations normally a 1 gallon sample is appropriate.

6.6 Milk Sampling NOTE: NO RADIOACTIVITY IS NORMALLY FOUND IN MILK SAMPLES WITH THE EXCEPTION OF NATURALLY OCCURRING K-40.

6.6.1 Milk collection points are shown in Attachment 4 from which appropriate sample points should be selected and samples collected as deemed necessary by the Dose Assessment Manager.

6.6.2 Refer to Attachment 1 for direction and distance of Milk Sampling locations normally a 1 gallon sample is appropriate.

6.7 Snow Sampling NOTE: SNOW SAMPLES ARE DEPENDENT UPON SEVERAL WEATHER RELATED VARIABLES; A) RATE OF SNOWFALL AT, AND SINCE TIME OF RELEASE; B) AIR TEMPERATURES SINCE SNOWFALL OF INTEREST OCCURRED; C) WIND SPEED AND DIRECTION; D) SUNSHINE, RAIN OR OTHER WEATHER CONDITIONS OCCURRING AFTER SNOWFALL OF INTEREST.

6.7.1 Select the area to be sampled from the general location requested by the Dose Assessment Manager. Choose a location that has not been subjected to non meteorological disturbances (plowing, snowmobiles, pedestrians, etc.).

NOTE: SNOW FALLING OR SNOW ON GROUND AT TIME OF DEPOSITION MAY HAVE DRIFTED. MELTING AND FREEZING AND/OR RAIN MAY MEAN THE SNOW DEPOSITION IS FIXED IN AN ICE LAYER AND NOT AFFECTED BY WINDS. THESE POSSIBILITIES MUST BE CONSIDERED AND EXISTING WEATHER CONDITIONS USED TO DETERMINE AREA TO BE SAMPLED.

6.7.2 Take radiation reading with survey meter(s) three inches and three feet above surface of snow, record on the Environmental Data Sheet (Attachment 5).

6.7.3 Measure the selected area to be sampled in units of square feet.

NOTE: IF A CURRENT LAYER MAY HAVE FORMED ON AN EARLIER SNOWFALL, COLLECT SNOWFALL FROM SURFACE TO THIS CRUST. IF SNOW OF INTEREST MAY BE BELOW A CRUST LAYER FORMED LATER, SWEEP LOOSE SNOW AWAY TO THIS CRUST LAYER AND THEN SAMPLE THE CRUST LAYER AND LOOSE SNOW TO THE NEXT CRUST LAYER.

6.7.4 Sample up snow to a depth sufficient to collect snow of interest.

EPIP 2-14:6 6.7.5 Sample volume of melted snow should be equal to the amount necessary to fill a one gallon container. Loose snow volume is 4 times its liquid volume. Icy snow is approximately twice its liquid volume. The snow should be packed in the collection bag.

6.7.6 Measure the depth of snow in inches.

6.7.7 Securely close the sample bag to prevent leakage. It is recommended that all samples be double bagged to prevent leakage as snow melts.

6.7.8 Re-measure radiation levels at three inches and three feet. Record on the Environmental Data Sheet (Attachment 5).

6.7.9 Record the following data on the environmental Data Sheet (Attachment 5):

a. Location requested
b. Specific area selected
c. Area sampled in square feet
d. Depth sampled
e. Direction and approximate feet from permanent reference object
f. Weather conditions
g. Time of sample
h. Radiation readings at one centimeter and one meter before and after sampling 6.8 Land Sampling for Contamination 6.8.1 Restrict passage through the area when possible by cordoning off with ropes.

6.8.2 Establish a grid system of reasonable size squares in area to be surveyed: i.e. 20 ft.

by 20 ft. square for low contamination; 10 ft. by 10 ft. square for moderate contamination; 5 ft. by 5 ft. square for heavy contamination.

6.8.3 Slowly walk along centerline of grid squares holding survey instrument three feet above ground or as directed by the Dose Assessment Manager. Note readings of instrument for deviations from background measurements.

6.8.4 Record reading at center point of each square.

6.8.5 Prepare a map of area surveyed using recorded readings and approximate area of contamination.

6.8.6 If the Survey Area involves hard surfaces (e.g. sidewalk, driveways, rooftops, large rock surfaces) and Dose Assessment requests smears taken, smear surfaces in accordance with instructions in Contamination Surveys. (Attachment 6).

EPIP 2-14:7 6.9 GRASS SAMPLING 6.9.1 Take samples at locations identified for environmental sampling.

6.9.2 Survey three inches and three feet above the surface to determine maximum activity in general area of interest.

6.9.3 Select specific area to be sampled determined by size of sample necessary.

6.9.4 Measure selected sampling area in units of square feet.

6.9.5 Take radiation readings three inches and three feet above the surface of area to be sampled.

6.9.6 Clip grass in sample area as close to the roots as possible without including dirt in the sample. Grass sample should fill approximately a volume of one gallon if possible.

NOTE: DO NOT PULL UP CLUMPS OF GRASS AND DIRT AND SUBMIT AS SAMPLE. THIS SAMPLE WOULD BE MEANINGLESS FOR DETERMINATION OF CONTAMINATION.

NOTE: NO RADIOACTIVITY IS NORMALLY FOUND IN GRASS SAMPLES WITH THE EXCEPTION OF NATURALLY OCCURRING K-40.

6.9.7 Collect top 1 inch of soil from area in which grass was clipped as a second sample.

6.9.8 Re-measure radiation levels at three inches and three feet above surface.

6.9.9 Record the following on the Environmental Data Sheet (Attachment 5):

a. Sample location
b. Area sampled in square feet
c. Depth of soil sampled
d. Location on grid or number of feet and direction from permanent reference object.
e. Time of Sample
f. Radiation readings before and after sampling
g. Sample identification
h. Survey meter used 6.9.10 Tag sample bag to clearly identify sample.

EPIP 2-14:8 6.10 Non-Grass Areas NOTE: NO RADIOACTIVITY IS NORMALLY FOUND IN ENVIRONMENTAL SAMPLES WITH THE EXCEPTION OF CS-137 AT 160 pCi/kg AND NATURALLY OCCURRING K-40.

6.10.1 Take sample at locations identified for environmental sampling.

6.10.2 Survey three inches and three feet above the surface.

6.10.3 If leaves and/or other debris, other than sticks are in the selected area, they should be collected as a separate sample.

6.10.4 Re-measure radiation levels if leaves have been collected for sample.

6.10.5 Collect top 1/2 inch of soil from area selected if level. Collect small plugs of soil if roughly plowed field. Plugs can cover larger area but give approximate square feet area approximately 1 gallon container should be collected.

6.10.6 Re-measure radiation levels at three inches and three feet.

6.10.7 Record the following on the Environmental Data Sheet (Attachment 5):

a. Sample location
b. Area sampled in square feet
c. Depth of soil sampled
d. Location on grid or number of feet and direction from permanent reference object.
e. Time of Sample
f. Radiation readings before and after sampling
g. Sample identification 6.10.8 Tag sample bag to clearly identify sample.

6.11 Vegetation Sampling NOTE: NO RADIOACTIVITY IS NORMALLY FOUND IN VEGETATION SAMPLES WITH THE EXCEPTION OF NATURALLY OCCURRING K-40.

6.11.1 Choose vegetation to be sampled based on deposition possibilities and availability for sufficient sample size.

EPIP 2-14:9 NOTE: LEAVES SHOULD BE SAMPLED FROM TOP MOST PART OF TREE. DEPOSITION IS UNLIKELY ON LEAFY AREAS UNDER TALLER TREES OR BUSHES. GROUND COVERS SUCH AS BURDOCK, LETTUCE OR FLOWERS SHOULD BE SELECTED FROM OPEN AREAS. LARGE LEAFY VEGETATION IS BETTER THAN SMALL. IF RAIN HAS OCCURRED SINCE THE RELEASE, DEPOSITED CONTAMINATION MAY HAVE BEEN WASHED OFF.

6.11.2 Take as large a sample as possible considering that it will be compressed into a 1 gallon container.

6.11.3 Record the following on the Environmental Data Sheet (Attachment 5):

a. Location of sample
b. Type of sample
c. Time of sample
d. Other data necessary for full descriptive purposes 6.11.4 Tag sample bag to clearly identify sample.

6.12 Decontamination/Sample Return 6.12.1 Inform Survey Center Manager of team return.

6.12.2 Upon returning to the Survey Center, perform a personnel frisk in accordance with Attachment 6. Document results on Survey Team Attachment Form (Attachment 7).

6.12.3 If any contamination greater than 100 CPM above background is found, contact the Survey Center Manager for decontamination instructions.

6.12.4 Conduct a vehicle contamination survey by direct frisk in accordance with Attachment 6. Document results on Attachment 7.

6.12.5 If any contamination greater than 250 cpm above background is found, contact the Survey Center Manager for decontamination instructions.

6.12.6 Return all samples and data sheets and Survey Team Attachment Forms to the Survey Center Manager.

6.12.7 TLD's are processed in accordance with RP-TLD-710A-OPS, Operation of Panasonic UD-710A TLD Reader.

6.12.8 Dispose of contaminated and potentially contaminated waste in an approved manner.

6.12.9 Re-stock and inventory survey team equipment foot-locker. Stow equipment in its designated location.

EPIP 2-14:10 6.12.10 Return radio system, cellular phone, portable air sampler, radiation count rate meter and dose rate meter to the Survey Center equipment area and place on charge as appropriate. Response check all survey meters prior to returning to storage. Notify the Survey Center Manager if any meters do not response check properly.

6.12.11 Return 0-1500mR and 0-1OR dosimeters and sign-out on dosimeter log sheet.

7.0 ATTACHMENTS

1. Direction And Distance To Sample Points
2. Post Accident TLD Locations For Survey Teams
3. Permanent Post Accident TLD Locations
4. Location Of Dairy Farms
5. Environmental Data Sheet
6. Contamination Surveys
7. Survey Team Attachment Form

EPIP 2-14:11 Attachment 1, Rev. 15 Page 1 of 1 DIRECTION AND DISTANCE TO SAMPLE POINTS All directions given in degrees and all distances given in miles.

Air Sample Stations TLD Location Direction Distance Direction Distance

  1. 2 87 0.20 #2 87 0.20
  1. 3 110 0.26
  1. 3 110 0.26
  1. 4 140 0.16
  1. 4 140 0.16
  1. 5 185 0.10
  1. 5 185 0.10
  1. 6 232 0.14
  1. 6 232 0.14
  1. 7 257 0.14
  1. 7 257 0.14
  1. 8 258 11.9
  1. 8 258 11.98
  1. 9 235 7.1
  1. 9 235 7.1
  1. 10 185 8.1
  1. 10 185 8.1
  1. 11 123 7.1
  1. 11 123 7.1
  1. 12 93 15.6
  1. 12 93 15.6
  1. 13 292 0.14
  1. 13 194 0.43
  1. 14 292 0.48
  1. 15 272 0.53
  1. 16 242 0.56 WATER SAMPLE LOCATIONS #17 208 0.31
  1. 18 193 0.40 DIRECT DIST. 0.25
  1. 19 177 15.9 #20 165 0.42 Russell Station 270 145 0.37
  1. 21 Ontario Water District 128 0.50 1.4 #22 Intake 70 107 0.42
  1. 23 Circ Water 90 0.39 0.26 #24 Intake 0 8.9
  1. 25 247 Circ Water 9.2 0.08 #26 223 Discharge 15 9.1 0.16 #27 202 Deer Creek 105
  1. 28 145 11.0 Well B 150 0.40
  1. 29 104 8.6 Tap Onsite Sink 103 12.7 110 0.26 #30 Rainfall #3 4.5 0.10 #31 263 Rainfall #5 185
  1. 32 246 4.3 Rainfall #8 258 11.9
  1. 33 220 4.9 Rainfall #10 185 8.1
  1. 34 205 4.3 Rainfall #12 93 15.6
  1. 35 193 4.7
  1. 36 174 3.5 MILK SAMPLE LOCATIONS 3.7
  1. 37 158
  1. 38 137 4.4 DIRECT DIST. 4.1
  1. 39 115
  1. 40 87 4.1 Farm A 113 0.60 Farm B 242 3.4 Farm C 156 3.1 Farm D 132 15.6 Fish Samples Indicator Samples Lake Ontario Discharge Plume Background Samples Russell Station Produce Samples Indicator Samples Grown on property surrounding Plant Background Samples Purchase from farms > 10 miles

EPIP 2-14:12 Attachment 2, Rev. 15 Page 1 of 2 POST ACCIDENT TLD LOCATIONS FOR SURVEY TEAMS INTERSECTION NUMBER LOCATION 2 ESE Lake Road and Knickerbocker Road 2 SE Knickerbocker Road and Brick Church Road 2S Ontario Center Road and Brick Church Road 2 SSW Slocum Road and Brick Church Road 3 SW Lakeside Road and Boston Road 2 WSW Lake Road and Lakeside Road 2W Roder Parkway and Ontario Drive 3 ESE-2 Fisher Road and Shepard Road Fisher Road and Trimble Road Arbor Road and Trummonds Road Walworth 6E Pultneyville Tuckahoe Road and Salmon Creek Road 5SW -1 County Line Road and Berg/Schlegel Road 9SW-2 State Road and Route 250 Plank Road and Salt Road Penfield Road (Route 441) and Five Mile Line Road 6 WSW Salt Road and Schlegel Road Lake Road and Route 250 8 SSW - 1 Plank Road and County Line Road Route 21 and Farnsworth Road Route 21 and Pound Road 4SE Kenyon Road and Furnace Road Plank Road and Five Mile Line Road Eddy Ridge Road and Ridge Road

EPIP 2-14:13 , Rev. 15 Page 2 of 2

EPIP 2-14:14 Attachment 3, Rev. 15 Page 1 of 2 PERMANENT POST ACCIDENT TLD LOCATIONS

  1. 1 Not used
  1. 2 - Onsite - Manor House yard
  1. 3 - Onsite - In field 200 ft. SE of Station #2
  1. 4 - Onsite - Training Center yard driveway circle
  1. 5 - Onsite - Between creek and plant entry road
  1. 6 - Onsite - SW side of plant parking lot
  1. 7 - Onsite - Power pole along west plant fence
  1. 8* - Topper Drive - Irondequoit, Seabreeze Substation #51
  1. 9* - Phillips Road - Webster - Intersection with Highway #104, Substation #74
  1. 10* - Walworth, Substation #230
  1. 11 - W. Main St. - Williamson, behind Cheetam Ins. Agency Bldg, Substation #207
  1. 12 - Seaman Ave. - Sodus Point - Off Lake Road by Sewer District, Substation #209
  1. 13 - At corner of plant restricted area fence and dogleg to west
  1. 14 - NW corner of field along lake shore
  1. 15 - Field across road, west side of orchard, -3000 ft. west of plant
  1. 16 - SW corner of orchard, - 3000 ft. west of plant, - 200 ft. north of Lake Road
  1. 17 - Power pole in orchard, - 75 ft. north of Lake Road
  1. 18 - - 30 ft. north of NE corner of Substation #13A fence
  1. 19 - - 100 ft. east of plant access road, behind house
  1. 20 - - 150 ft. west of Ontario Center Road and - 170 ft. south of Lake Road by RG&E property marker
  • Requires special lock key for substations.

EPIP 2-14:15 Attachment 3, Rev. 15 Page 2 of 2 PERMANENT POST ACCIDENT TLD LOCATIONS

  1. 21 - North side of Lake Road, - 200 ft. east of Ontario Center Road
  1. 22 - North side of Lake Road, SE property corner
  1. 23 - East property line, midway between Lake Road and Lake Shore
  1. 24 - Lake shore near NE corner of property
  1. 25 - Substation #73, Klem Road adjacent to 897 Klem Road
  1. 26 - Service center; Plank Road west of 250
  1. 27 - Atlantic Ave at Wayne-Monroe County Line, Penfield side
  1. 28 - Substation #193, Marion, behind Stanton Ag. Service, North Main Street
  1. 29 - Substation #208, Town Line Road (CR 118); 1000 ft. north of 104
  1. 30 - District Office, Sodus; fence near gas pumps at rear
  1. 31 - Lake Road, pole 20 ft. north of road; 500 ft. east of Salt Road
  1. 32 - Woodard Road at County Line Road. Pole northwest corner
  1. 33 - County Line Road at R.R. Tracks; pole - 100 ft. east along tracks
  1. 34 - Lincoln Center Road, pole midway between Ridge Road and Rt. 104
  1. 35 - Transmission Right of Way; northside of Clevenger Road
  1. 36 - Substation #205, Rt. 104, east of Ontario Center Road, SW corner of fence
  1. 37 - Railroad Ave., pole at 2048
  1. 38 - Fisher Road at R.R. Tracks, Pole east of road
  1. 39 - Seeley Road; pole southside, 100 ft. west of intersection with Stony Lonesome Road
  1. 40 - Lake Road at Stoney Lonesome, pole at SE corner

EPIP 2-14:16 Attachment 4, Rev. 15 Page 1 of 1 I

zT>-J-J.

.1

EPIP 2-14:17 Page 1 of 1 Attachment 5, Rev. 15 I DOCUMENTATION FORM I

I (Use EPIP 2-15 for evaluation of results)

ENVIRONMENTAL DATA SHEET Type of Sample: Sample Number:

Time:

Date:

Person taking sample:

Location:

Survey Meter used: Serial No.:

Draw Map Reference Object:

Direction:

Distance: ft. ft.

Area: sq. ft. Depth: inches BEFORE SAMPLING: AFTER SAMPLING:

Radiation Reading @ 3" Radiation Reading @ 3" Radiation Reading @ 3' Radiation Reading @ 3' Weather conditions:

Other comments:

EPIP 2-14:18 Attachment 6, Rev. 15 Page 1 of 2 CONTAMINATION SURVEYS COLLECTING AND COUNTING SMEAR SAMPLES NOTE: DO NOT TOUCH THE METER PROBE TO ANY SURFACE BEING SURVEYED. PROBE CONTAMINATION MAY RESULT.

PERSONNEL FRISK

1. Obtain a RM-25 with a HP-260 pancake probe or equivalent survey meter.
2. Check the background count rate.
3. Slowly pass the meter probe over a person (i.e., within 1/2 inch from the person) moving it at a rate of 1 to 2 inches per second.
4. Listen to the audible count rate and watch the meter for any increases.
5. Resurvey areas showing an increased count rate.
6. When contamination is suspected, hold the detector over that area for 15 seconds to obtain the gross count rate.
7. Subtract the background count rate from the gross count rate. This is the net count rate in CPM.
8. Notify the Survey Center Manager if the net count rate is greater than 100 CPM.

DIRECT FRISK SURVEY (OBJECTS)

1. Obtain a RM-25 with a HP-260 pancake probe or equivalent survey meter.
2. Check the background count rate.
3. Slowly pass the meter probe over an object or area surface (i.e., within 1/2 inch from it) moving it at a rate of 1 to 2 inches per second.
4. Listen to the audible count rate and watch the meter for any increases.
5. Resurvey areas showing an increased count rate.
6. When contamination is suspected, hold the detector over that area for 15 seconds to obtain the gross count rate.

EPIP 2-14:19 Attachment 6, Rev. 15 Page 2 of 2

7. Subtract the background count rate from the gross count rate. This is the net count rate in CPM.
8. Notify the Survey Center Manager if the net count rate is greater than 250 CPM.

SMEAR SURVEY

1. Obtain cloth smears with adhesive backing mounted on waxed paper.
2. Obtain a RM-25 with a HP-260 pancake probe or equivalent survey meter.
3. Check the background count rate.
4. Mark the smears with sequential numbers (e.g. 1,2,3 .......
5. Holding the smear paper between the thumb, index and middle fingers and applying medium pressure, smear an area 100 cm2 (approximately 4 inches by 4 inches). A 16-.

inch "S"pattern can also be used.

6. Record the smear location by writing the smear number on the map and circling it.
7. Hold the smear paper within 1/2 of the meter probe until the meter indication stabilizes.

This is the gross count in CPM.

8. Subtract the background count rate from the gross count rate. This is the net count rate in CPM.
9. Record the net count as CPM 100 cm 2 on the back of the map next to the corresponding smear number.

NOTE: STEP 10 DOES NOT APPLY TO ENVIRONMENTAL SMEARS.

2

10. Notify the Survey Center Manager if the net count rates exceed 1000 CPM 100 cm .
11. Return completed contamination surveys and smears to the Survey Center Manager.

EPIP 2-14:20 Attachment 7, Rev. 15 Page 1 of 1 SURVEY TEAM ATTACHMENT FORM SURVEY TEAM:

DATE TIME INITIALS METER REMARKS TYPE/NO.

____ .1 I I

_____ I- *I* I

_ _ _ I 1. - I I *I I I

____ 1. 4 1

____ 1 4 1

_____ 4 1 +

.1 I I.

I I I I. 4 USE THIS FORM TO DOCUMENT INFORMATION REGARDING SURVEY TEAM COVERAGE NOT DOCUMENTED ON SURVEY MAPS OR FORMS

ROCHESTER GAS AND ELECTRIC CORPORATION GINNA STATION CONTROLLED COPY NUMBER P.

PROCEDURE NO. EPIP 2-15 REV. NO. 6 POST PLUME EVALUATION OF OFFSITE DOSES DUE TO DEPOSITION RESFFCTVEDAGER EFFECTIVE DATE Category 1.0 This procedure contains 8_ pages

EPIP 2-15:1 EPIP 2-15 POST PLUME EVALUATION OF OFFSITE DOSES DUE TO DEPOSITION

1.0 PURPOSE

1.1 This procedure provides methods of estimating dose resulting from the deposition of radioactive material transported by a plume. Deposition of radioactive material can result in exposure to people through ingestion of contaminated food or water, external exposure from standing on contaminated ground, and inhalation of re-suspended radionuclides.

1.2 This procedure provides protective action recommendations (PARs) that can be made based on measured area deposition, forage concentration and milk activity. The preventive Protective Action Guide (PAG) establishes levels that cause minimal impact on the food supply by preventing or reducing the concentration of radioactivity in food or animal feed. The preventive PAG is used when projected doses from ingestion can exceed 0.5 rem to the whole body or 1.5 rem to the thyroid.

1.3 The emergency PAG establishes levels at which contaminated food should be isolated from commerce because of greater projected health hazards.

1.4 The emergency PAG is used when projected doses from ingestion can exceed 5 rem to the whole body or 15 rem to the thyroid.

2.0 RESPONSIBILITY

The TSC or EOF Dose Assessment Manager is responsible for implementing this procedure.

3.0 REFERENCES

3.1 Developmental References 3.1.1 Nuclear Emergency Response Plan 3.1.2 NYS Radiological Emergency Preparedness Plan 3.1.3 EPA-400, Manual of Protective Action Guides and Protective Actions for Nuclear Incidents (1991) 3.1.4 USNRC Regulatory Guide 1.109 3.1.5 FDA "Accidental Radioactive Contamination of Human Food and Animal Feeds: Recommendations for State and Local Agencies", August 13, 1998

EPIP 2-15:2 3.2 Implementing References 3.2.1 EPIP 2-14, Post Plume Environmental Sampling

4.0 PRECAUTIONS

None.

5.0 PREREQUISITES

None.

6.0 ACTIONS

6.1 Ingestion Pathway Sampling 6.1.1 State, Federal and RG&E environmental survey teams will collect field samples so the offsite levels of radioactive deposition can be determined. The results of the isotopic analysis of samples collected by RG&E and results of surveys made by RG&E will be provided to New York State. The State will use all sample results to determine whether any protective actions are warranted to limit exposure to the public through the food and water pathways.

6.2 Implementation of Protective Action Recommendations 6.2.1 The State will determine if any protective actions are necessary to limit exposure to the public based on the Federal Drug Administration Protective Action Guides. Ifthe protective action guides are exceeded the State will implement necessary protective actions. RG&E Dose Assessment should perform an independent determination and advise the State if the protective action guides are exceeded.

6.3 Protective Action Revision and Termination 6.3.1 The State decides whether protective actions should be revised or terminated.

6.4 Predetermined Protective Action Recommendations 6.4.1 Ifa Site Area Emergency is declared the State will issue an immediate advisory to place all milk animals within two miles on stored feed.

6.4.2 If a General Emergency is declared, the State will issue an immediate advisory to place all milk animals within ten miles on stored feed.

EPIP 2-15:3 6.5 External Dose from Surface Contamination 6.5.1 The external dose from deposition can be determined by surveying the ground surface to obtain the dose rate and multiplying by the projected exposure time.

6.5.2 Surveys are conducted using a dose rate meter and taking readings three feet from the surface. A micro-R meter can be used to survey areas of low level surface contamination.

6.5.3 Compile ground survey readings to establish the preliminary deposition "footprint". Provide ground survey data summaries to the State for use in re entry, relocation and long term recovery 6.5.3.1 The protective action recommended is dependent on the half-life of the contaminant, the nature of the contaminated surface, weather conditions and the magnitude and extent of the contamination. The protective actions range from washing of the contamination by simple hosing to sheltering, followed by evacuation, depending on the severity of the contamination problem.

6.5.3.2 If personal contamination of the public is anticipated prior to taking shelter, recommendations will be made to wash exposed parts of the body, shower and change clothes as soon as practical.

6.6 Projection of Deposition 6.6.1 Determine the area for which the protective action analysis is to be made.

6.6.2 Determine the projected ground deposition activity. This is done by obtaining Xu/Q values from EPIP 2-4. Then, multiplying the release rate of the isotope in pCi/sec, the Xu/Q, the deposition velocity of 0.01 m/sec, 1E6 jiCi/Ci, and the release duration.

Ci/sec x __sec-mph/m3 x 0.01 in/sec x 1 E+6 pLCi/Ci sec = - uCVm 2 6.6.3 Measured ground activity levels and sample results may not be available for hours or days. Ground deposition activity can be measured by surveying with a HP-260 GM probe or equivalent. Survey at three inches from the surface and multiply net cpm by 2.5E-03 to obtain mCi/ m2 . Survey at three feet from the surface and multiply net cpm by 33 to obtain mCi m2 .

6.6.4 Indicate on USGS topographical maps, or equivalent, the location where the sample originated.

6.7 Sample Collection 6.7.1 Samples are collected by Survey Teams using EPIP 2-14 by RG&E survey teams or an equivalent State procedure.

EPIP 2-15:4 6.8 Sample Analysis 6.8.1 Samples should be analyzed using a gamma spectrometer. The analysis can be performed by RG&E at the Ginna site, by New York State environmental lab in Albany, or by a contractor such as the NYPA laboratory in Fulton, NY.

6.8.2 There is normally no measurable radioactivity normally in the environment with the exception of naturally occurring K-40 and Cs-137 from previous fall-out.

Cs-1 37 in soil which has an average value of 160 pCi/kg around Ginna.

6.8.3 Use the following table to assess samples. Ifthe values in the sample are above the table values, recommend to New York State to prevent ingestion of the food sampled.

Recommended Derived Intervention Levels (DIL) or Criterion for Each Radionuclide Group(a),

(b)

All Components of the Diet Radionuclide Group (Bq/kg) (pCi/kg)

Sr-90 160 4300 1-131 170 4600 Cs-1 34 + Cs-1 37 1200 32,000 Pu-238 + Pu-239 + Am- 2 54 241 Ru-1 03 + Ru-1 06(c) (C06800) + (C1450) <1 (Cu/1.8E5) + (Cdl.2E4) <1 Notes:

(a) The DIL for each radionuclide group (except for Ru-1 03 + Ru-106) is applied independently. Each DIL applies to the sum of the concentrations of the radionuclides in the group at the time of measurement.

(b) Applicable to foods as prepared for consumption. For dried or concentrated products such as powdered milk or concentrated juices, adjust by a factor appropriate to reconstitution, and assume the reconstituted water is not contaminated. For spices, which are consumed in very small quantities, use a dilution factor of 10.

(c) Due to the large difference in DILs for Ru-1 03 and Ru-1 06, the individual concentrations of Ru-1 03 and Ru-1 06 are divided by their respective DILs and then summed. The sum must be less than one. C3 and C6 are the concentrations, at the time of measurement, for Ru-1 03 and Ru-1 06 respectively.

EPIP 2-15:5 NOTE: These DILs apply to consumable foods sampled. The FDA DILs provide a large margin of safety for the public because each DIL is set according to a conservatively safe level for the most vulnerable group of individuals. In addition, food would be restricted if radionuclide concentrations reach or exceed a DIL at any point in time, even though the concentrations need to be sustained for an extended period of time for the dose to actually reach the PAG. Food with concentrations below the DILs is permitted to move in commerce without restrictions. Food with concentrations at or above the DILs is not normally permitted into commerce. However, State and local officials have the flexibility in whether or not to apply restrictions.

6.8.4 Assessment of the effective days of intake should consider the specific food, the population involved, the food distribution system and the radionuclide. Whether the food is distributed to the retail market or produced for home use will significantly affect the intake in most instances. While assessment of intake should be on a case-by-case basis, some general comments may be useful in specific circumstances.

6.8.5 For short half-life radionuclides, radioactive decay will limit the ingestion of radioactive materials and the effective "days of intake". The "effective" days of intake in this case is 1.44 times the radiological half-life. For iodine-1 31 (half-life of 8.05 days), the effective "days of intake" is 11 days.

6.8.6 Where the food product is being harvested on a daily basis, it may be reasonable to assume reduction of contamination due to weathering. As an initial assessment, it may be appropriate to assume a 14-day weathering half life (used for forage in pasture/cow/milk pathway) pending further evaluation. In this case, the effective "days of intake" is 20 days. A combination of radioactive decay and weathering would result in an effective half-life for iodine-131 of 5 days and reduce the "days of intake" to 7 days.

6.8.7 In the case of food which is sold in the retail market, the effective "days of intake" would probably be limited by the quantity purchased at a given time. For most food, especially fresh produce, this would probably be about a 1 week supply. In some cases, larger quantities would be purchased for home canning or freezing. For most foods and members of the public, an effective "days of intake" of 30 days is probably conservative.

6.9 Protective Action Recommendations 6.9.1 Recommend any of the following protective actions to reduce the exposure from ingestion for the milk pathway.

Farms Remove lactating dairy animals from contaminated pasturage, move the animals in-doors, and provide uncontaminated feed (had been stored in doors or covered out-of-doors)

EPIP 2-15:6

  • Provide animals with uncontaminated water. Sources may be covered wells, covered cisterns, and closed storage tanks. Do not use surface water such as streams, ponds or open reservoirs.

0 If individual milkings cannot be stored in separate tanks, take a representative one-gallon sample from each milking, label and refrigerate. Samples will be picked up by a survey team.

  • Store for a prolonged period of time at reduced temperature.

0 Prevent introduction of milk supplies into commerce.

Processor

  • Withhold contaminated milk from the market to allow radioactive decay of the short-lived radionuclides. This may be achieved by storing frozen fresh milk, frozen concentrated milk, frozen concentrated milk products.
  • Store for a prolonged period of time at a reduced temperature in conjunction with a special pasteurization process using ultra high temperatures.
  • Divert the production of fluid milk for the production of dry whole milk, non-fat dry milk, butter or evaporated milk.
  • Attempt to store all incoming shipments in separate tanks and segregate milk not originating in the 50-mile EPZ.
  • Take a one-gallon representative sample of each incoming shipment, label (source, date/time of arrival, carrier, volume, in-plant storage tank, etc) and refrigerate. Samples will be picked up by a survey team.

Public

  • Fresh milk on hand prior to the advisory and stored in closed containers may be used.

Dry or canned milk in closed containers may be used.

6.9.2 Recommend any of the following protective actions to reduce the exposure from ingestion for the drinking water pathway.

All

  • Do not use surface water (streams, lakes, ponds) for human or animal consumption.
  • Limit the ingestion of potable water (either for drinking or cooking) until the source has been checked and approved for consumption.

0 Water stored in closed containers or vessels prior to the incident may be ingested. This includes refrigerator storage, closed tanks, covered wells, etc.

0 Bottled water and canned beverages and juices may be used as water sources Farms

  • Do not use surface water for human or animal consumption. Surface water may be used for sanitary and other non-consumption purposes.

EPIP 2-15:7 Other water sources identified as contaminated should not be consumed but may be used for other purposes.

Water stored in closed tanks or vessels prior to the advisory may be consumed.

Commerce

  • Water identified as contaminated should not be used for processing of materials (consumables, containers) which enter the food chain.
  • Contaminated water may be used for other industrial and commercial operations if so advised.

Public 0 Secure outlets of wells for water identified as contaminated. Do not use reservoir water identified as contaminated. Do not use water for consumption that has not been checked. If approved, this water may be used for sanitary and other purposes.

Use alternate sources of liquid such as: water drawn and stored in closed containers prior to the advisory, bottled water, bottled/canned beverages and juices and water provided by emergency organizations such as the American Red Cross and the National Guard. Arrangements for alternate, emergency water will be made by the County or State authorities.

6.9.3 Recommend any of the following protective actions to reduce the exposure from ingestion for the fresh fruits and vegetables pathway, fin fish and shell fish pathway, animal feeds pathway (other than pasture grass). This includes crops in the field, in transit to market, roadside stands, markets and in homes.

Commerce 0 Remove surface contamination by washing, brushing, scrubbing or peeling.

0 Food in sealed packages, cans, cartons, barrels etc. needs no treatment.

  • Suspend fishing operations until resumption is recommended. Check each catch made on the day of the advisory. Keep catch covered until transported outside the area of possible contamination.

0 Prevent introduction of food type into commerce if it has been identified as contaminated.

  • Consider other sources of food originating outside the 50-mile EPZ.

0 Do not process or vend unpackaged food if the operations area is contaminated.

0 Stay alert for public information bulletins.

Public 0 Ifstored in the open, remove surface contamination by washing, brushing, scrubbing or peeling.

0 Food in sealed packages, in refrigerators or closets are otherwise protected, and need no treatment.

EPIP 2-15:8

  • Preserve food before contamination by canning, freezing and dehydration.

0 Cooked or raw food may be stored in a refrigerator, closet, box or other closed container.

0 Store food to permit radioactive decay of short-lived radionuclides.

a Restrict diet to foods stored in closed containers prior to the advisory or packaged, sealed foods.

0 Stay alert for public information bulletins.

7.0 ATTACHMENTS

None.

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