ML20083Q150

Public Version of Rev 1 to Emergency Plan Implementing Procedure EP-IP-044, Emergency Environ Sampling

ML20083Q150
Person / Time
Site:	Susquehanna
Issue date:	01/21/1983
From:	PENNSYLVANIA POWER & LIGHT CO.
To:
Shared Package
ML17139B365	List: ML17139B364 ML17139B366 ML20083Q150
References
EP-IP-044-01, EP-IP-44-1, NUDOCS 8302250035
Download: ML20083Q150 (65)

Text

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O-PROCEDURE COVER SHEET

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PENNSYLVANIA F0WER & LIGHT CO.

SUSQUEHANNA STEAM ELECTRIC STATION EP-IP-044 EMERGENCY ENVIRONMENTAL SAMPLING Revision 1 Page 1 of 65

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Effective Date I / /- f 8 Expiration Date /.4/-fS i

Revised Expiration Date CONTROLLED P

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Date I A - /5' -4 %-

Prepared by Reviewed by

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M4 Date

/a -/I' C PORC Review ir Ye, (

No ( )

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o Approved by

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Sectfdn Tiiad i/

PORC Meeting Number 63-cog Date

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$ Wola Date

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, Superintendent of ~ Plant O

FORM AD-QA-101-1, Rev. 1 Page 1.of 1 8302250035 830216 PDR ADOCK 05000387 F

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(3 K-

EP-IP-044 Revision 1 Page 2 of 65 TABLE OF CONTENTS SECTION PAGE 1.0 PURPOSE 3

2.0 SCOPE 3

3.0 REFERENCES

3 4.0 RESPONSIBILITIES 3

5.0 DEFINITIONS 4

6.0 INSTRUCTIONS 4

ATTACHMENTS q

ATTACHMENT PAGE A

Action Step - RADIATION PROTECTION COORDINATOR 6

B Action Step - CHEMISTRY STAFF 7

C Action Step ~ RADIATION SUPPORT MANAGER 8

0 Action Step - ENVIRONMENTAL SAMPLING SUPERVISOR 10 E

Action Step - ENVIRONMENTAL SAMPLER COLLECTORS 13 F

Action Step - ADMINISTRATIVE SUPPCRT MANAGER 16 G

Calculation of River Transit Time to Danville, 17 Oflution Factor, and Concentration at Danville H

Data Sheet (Form EP-IP-044-1) 25 I

Sample Collection Procedures 27 J

R.M.C. Supplemental Sample Collection Procedures 35 K

Data Sheet (Form EP-IP-044-2) j.L)

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EP 'P-044 Revision 1 Page 3 of 65 EMERGENCY ENVIRONMENTAL SAMPLING i

1.0 PURPOSE The purpose of this procedure is to describe the methods and responsibilities for conducting environmental monitoring during and after an

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EMERGENCY.

2.0 SCOPE This procedure includes all sampling and analyses to scoport assesmnt of environmental impact in the event of an abnormal gaseous or liquid release leading to or during an emergency at SSES. Provisions are included for returning to the routine radiological environmental monitoring program as described in NSI-QA-4.1.

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3.0 REFERENCES

3.1 SSES Emergency Plan 3.2 EPA Protective Action Guides 3.3 NSI-QA-4.1 Radiological Environmental Monitoring Program 3.4 Radiation Management Corporation, Procedure - T46 3.5 Radiation Monitor,ing Data Analysis Verification Program M4nual -

Appendix I, part C 3.6 Ecological studies of the Susquehanna river in the vicinity of SSES, Ichthyological Associates, Annual Report for 1976 4.0 RESPONSIBILITIES 4.1 In the event of a liquid release, it is the responsibility of the RADIATION PROTECTION COORDINATOR to assess initial results of the liquid sample taken by the CHEMISTRY STAFF and to take appropriate actions.

4.2 In the event of a liquid release, it is the responsibility of the CHEMISTRY STAFF to collect liquid samples from the blowdown line composite sampler located in the sewage treatment plant and to analyze these samples in accordance with this procedure.

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EP-IP-044 Revision 1 Page 4 of 65 4.3 It is the responsibility of the RADIATION SUPPORT MANAGER to direct the ENVIRONMENTAL SAMPLING SUPERVISOR once the EOF has been manned.

4.4 It is the responsibility of the ENVIRONMENTAL SAMPLING SUPERVISOR to direct the ENVIRONMENTAL SAMPLE COLLFCTORS and to arrange for the analyses of the samples which are collected during and after the EMERGENCY.

4.5 It is the responsibility of the ENVIRONMENTAL SAMPLE COLLECTORS to perform the sampling required by the ENVIRONMENTAL SAMPLIhG SUPERVISOR.

4.6 It is the responsibility of the ADMINISTRATIVE SUPPORT MANAGER to dispatch couriers to transport samples to the analyses laboratory upon request by the ENVIRONMENTAL SAMPLING SUPERVISOR.

5.0 DEFINITIONS 5.1 pCi picocurie 5.2 cpm - counts per minute 5.3 NRC - U.S. Nuclear Regulatory Commission 5.4 EPA - U.S. Environmental Protection Agency 5.5 Pa. DER /BRP - Pennsylvania Department of Environmental Resources / Bureau of Radiation Protection 5.7 EOF - Emergency Operations Facility 5.8 REMP - Radiological Environmental Monitoring Program 6.0 INSTRUCTIONS 6.1 Upon notification of an emergency, the RADIATION PROTECTION C00RDINATOR will follow the Instructions in Attachment A, Action Step. RADIATION PROTECTION COORDINATOR.

6.2 At the direction of the RADIATION PROTECTION COORDINATOR the CHEMISTRY STAFF will follow Instructions in Attachment 8, Action Step, CHEMISTRY STAFF.

Upon arrival, at the EOF the RADIATION SUPPORT MANAGER will follow 6.3

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Instructions in Attachment C, Action Step, RADIATION SUPPORT MANAGER.

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EP-IP-044 Revision 1 Page 5 of 65 6.4 Upon notification by the RADIATION SUPPORT MANAGER, the ENVIRONMENTAL SAMPLING SUPERVISOR will follow Instructions in Attachment D, Action Step, ENVIRONMENTAL SAMPLING SUPERVISOR.

6.5 At the direction of the ENVIRONMENTAL SAMPLING SUPERVISOR, the ENVIRONMENTAL SAMPLE COLLECTORS will follow Instructions in Attachment E, Action Step,. ENVIRONMENTAL. SAMPLE COLLECTORS.

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6.6 Upon notification from the ENVIRONMENTAL SAMPLING SUPERVISOR, the ADMINISTRATIVE SUPPORT MANAGER will follow Instructions in Attachment F, Action Step, ADMINISTRATIVE SUPPORT MANAGER.

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Attachment A EP-IP-044 Revision 1 Page 6 of 65

~ ACTION STEP RAOIATION PROTECTION COORDINATOR A.1.0 In the event of a liquid release during an EMERGENCY the RADIATION PROTECTION COORDINATOR will:

A.1.1 Obtain.results of the initial liquid sample analysis

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performe'd by the CHEMISTRY ' STAFF.

A.1.2 Notify the Danville Water Authority of the release.

Notification of the release.should be made to the Superintendent of Water or supervisor on duty, Danville Borough at o

' Initial instructions for Danville should be to continue normal operation until river flow calculations can provide data needed to make decisions on protective actions'to be taken.

A.1.3 Direct the CHEMISTRY ' STAFF to centinue sampling as necessary.

A.1.4 Inform'the RADIATION SUPPORT MANAGER of the liquid sample analysis and of the actions already taken.

Include the l

amount of liquid released, time of release, termination time, and the initial concentration of radioactivity released in the discharge.

A.1.5 Inform the EMERGENCY DIRECTOR of the'results of Steps A.1.1 through A.1.4.

4 A.1.6 When the EOF is not manned:

a.

Perform liquid release calculations as per Attachment G -

of this procedure, b.

Provide DER /BRP with all results.

c.

Advise DER /8?P, based on the results, of any protective actions which should be taken by Danville.

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Page 1 of 1 4

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i Attachment B ~

EP-IP-044 Revision 1 Page 7 of 65 ACTION STEP CHEMISTRY STAFF B.1.0 In the event of a liquid release the CHEMISTRY STAFF will:

8.1.1 Upon notification from the EM.ERGENCY DIRECTOR, or designated M

COORDINATOR, report to the, Control Room for sampling instructions.

B.I.2 When instructed, proceed to the sewage treatment plant and collect a grab sample from the blowdown line composite sampler.

B.1.3 Take the sample back to the radiochemistry laboratory for a GAMMA scan analysis.

8.1.4 Report the following to the RADIATION PROTECTION COORDINATOR:

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B.1.4.1 GAML scan results B.1.4.2 Volume of release (gal.)

B.1.4.3 Length of release (time) 8.1.5 Each sample should be labeled with the following information:

B.1.5.1 TIME SAMPLE WAS TAKEN 8.1.5.2 TIME SAMPLE WAS ANALYZED

.s B.1.5.3 LOCATION OF SAMPLE B.1.5.4 AMOUNT OF SAMPLE B.1.5.5 CONCENTRATION IN SAMPLE I

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Page 1 of 1

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r Attachr.ent C',

EP-IP-044 Revision 1 Page 8 of 65 ACTION STEP RADIATION SUPPORT MANAGER C.1.0 The RADIATION SUPPORT MANAGER will:

LIQUID RELEASE C.1.1 Obtain, from the RADIATION PROTECTION COORDINATOR, dischtrge information such as amount of liquid released, time for release to be terminated, and the initial conce.1tration of radioactivity in the discharge. Relay this information directly to the ENVIRONMENTAL SAMPLING SUPERVISOR.

C.1.2 Direct the ENVIRONMENTAL SAMPLING SUPERVISOR to-implement off-~ site liquid monitoring activities as needed based on initital concentration results'.

C.1.3 Provide the DER /8RP with the results of the liquid calculations.

C.I.4 Advise the Pa. OER/8RP, based on the results of the liquid calculations, of any protective ' action which should be taken by Danville.

GASEOUS RELEASE C.2.0 Direct the ENVIRONMENTAL SAMPLING SUPERVISOR to implement the following off-site environmental monitoring activities as necessary:

C.2.1 Exchange of Emergency TLO's in the_ field and subsequent

. reading tr. the EOF.

C.2.2 Exchange of Quality Control TLD's once the EMERGENCY has been terminated. These will be-changed out and analyzed by the REMP Quality Control Laboratory.

' NOTE:

Quality Control TLO's will be changed out and analyzed by Penn State University. The phone number for_the analyses laboratory at Penn State is f(normal working hours).

C.2.3 Food product and vegetation sampling C.2.4 Air iodine cartridge and air particulate filter collection Page 1 of 2 0

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Atta:hment C.

EP-IP-044 Revision 1 Page 9 of 65 C.2.5 Milk collection - Begins approximately 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br /> after possible release of Iodine.

NOTE:

ASSURE THAT THE RADIATION LEVELS IN THE AREAS TO BE SAMPLED ARE SUCH THAT THE SAMPLE COLLECTORS WILL-NOT EXCEED THEIR QUARTERLY EXPOSURE LIMIT.

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' C. 2.'6

'Make a. recomniendation to DER /ERP to take appropriate protective action to affected farmers if the radioactivity in milk samples becomes 1.2 x 10" pCi/ liter, if the radioactivity in pasture samples becomes 2.7 x 105 pCi/kg, or if the projected dose to the infant thyroid reaches 1.5 rem, whichever comes first.

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r Attach.ent 0.

EP-IP-0441 Revision'l

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.-ACTION STEP.

ENVIRONMENTAL SAMPLING SUPERVISOR-0.1.0 The ENVIRC': MENTAL SAMPLING SUPERVISOR will:

LIQUID RELEASE-0.1.1 Upon notification.of-an emergency at SSES, contact the PROJECT DIRECTOR or alternate at Ichthyological Associates to notify-SAMPLE COLLECTORS to reoort to the Susquehanna Biological Laboratory g-O.1.2 Proceed to tha EOF and receive initial instructions from the-RADIATION. SUPPORT MANAGER.

0.1.3 Obtain the river level from a river level gauge in the

- Susquehanna Biological Laboratory.

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0.1.4 From the. RADIATION SUPPORT MANAGER, obtain:

0.1.4.1 Amount of-Liquid released 0.1. 4. 2 =

Time of release and termination time.

O.1.4.3 Initial concentration of activity in the discharge

0.1.5 Calculate

O.1.5.1 The dilution ~ factor in the Susquehanr2 river j;

0.1.5.2 The time for the plume to reach'0anville 0.1.5.3 Concentration of activity expected to reach Danville using the equations which are presented in Attachment G and Data Sheet contained in Attachment H.

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0.1.6 Give the ENVIRONMENTAL SAMPLE COLLECTORS the following in formation:

0.1.6.1 Where to sample (i.e., Danville Water Authority, Control location above discharge, location below

. discharge.)

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0.1.6.2 Type of sample (i.e., Composite or grab) l

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EP-IP-044 Revision 1 Page 11 of.65 0.1.6.3 Amount and frequency of sample (normal sampling -

100 ml/1/2 hr. for 2 hrs.)

0.1.6.4 Special instructions including a reminder to pick up SRO's and TLD's at the EOF.

0.1.7 Arrange for transportation and analysis of samples to the Analyses Laboratories and collection of sample results.

0.1.8 Notify the RADIATION SUPPORT MANAGER of sample results.

NOTE:

IN EMERGENCY SITUATIONS, RA0!ATION MANAGEMENT CORPORATION (RMC), PHILADELPHIA, PA., SHOULO BE USED FOR SAMPLE ANALYSES. THE TELEPHONE NUMBERS ARE:

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WEEKDAYS, 9AM - SPM ALL OTHER TIMES '

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's 0.1.9 Keep track of the ENVIRONMENTAL SAMPLE COLLECTORS' exposures by filling out Attachment K, Personnel Exposure of Environmental Sample Collectors.

GASEOUS RELEASE 0.2.0 Receive inital direction from RADIATION SUPPORT MANAGER.

0.2.1 Obtain the following release information:

0.2.1.1 Type of release 0.2.1.2 Direction of plume 0.2.1.3 Approximate radiation levels, if available 0.2.2 Contact ENVIRONMENTAL SAMPLE COLLECTORS and provide initial instructions:

0.2.2.1 Type of samples to be collected (i.e., milk, TLO's,

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food product and vegetation, air iodine and air particulates) 0.2.2.2 Locatica of samples I)

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Attachment D.

EP-IP-C44 Revision 1 Page 12 of 65 0.2.2.3 Exchange of TLD's - replacement TLD's should be picked up at the EOF

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D.2.2.4' Number of samples to be collected at each location 0.2.2.5 Special instructions (f.e., extra samples for Pa.

DER, NRC, EPA, etc.)

1 0.2.3 Contact the ADMINISTRATIVE SUPPORT MANAGER and arrange for transport couriers to pick up samples and transport them to the analysis laboratory.

D.2.4 Once analysis results are known, determine from the RADIATION SUPPORT MANAGER if future sampling is necessary. If further sampling is necessary follow Action Steps D.2.2 through D.2.4 D.2.5 Keep track of ENVIRONMENTAL SAMPLE COLLECTORS' exposures by filling out Attachment K, Personnel Exposure of Environmental

/~1 Sample Collectors.

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Attachment E'.

EP-IP-044 Revision 1 Page 13 of 65 ACTION STEP ENVIRONMENTAL SAMPLE COLLECTORS E.1.0 The ENVIRONMENTAL SAMPLE COLLECTORS will:

LIQUID RELEASE E.1.1 Obtain the following information upon initial contact with the ENVIRONMENTAL SAMPLING SUPERVISOR:

E.1.1.1 Location of sample E.1.1.2 Type of sample (i.e., composite or grab)

E.1.1.3 Amount and frequency of sample (normal sampling is 100 ml./1/2 hr. for 2 hrs.).

(D E.1.1.4 Phnne number to reach ENVIRONMENTAL SAMPL.NG U

SUPERVISOR E.1.1.5 Instructions for transporting samples to analysis laboratory.

E.1.2 Perform inventory of Sample Kits (located at Susquehanna Biological Laboratory:

E.1.2.1 Flashlight (with extra batteries)

E.1.2.2 Sample container E.1.2.3 Sample collector (i.e., water bucket, flask, etc.)

E.1.2.4 Plastic bags E.1.2.5 Gloves, rubber E.1.2.6 EP-IP-044 - Emergency Environmental Sampling E.1.2.7 Air cartridge and filter paper

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E.1.2.8 Sample receipt sheets, notebook, and 10 tags E.1.2.9 Map of area f])

E.1.2.10 TLD shields Page 1 of 3

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Attachment E.

EP-IP-044 Revision 1 Page 14 of 65 NOTE:

Extra Sample Kits are located in the EOF.

E.1.3 Before proceeding to initial sample locatio*:, pick up SRD's and TLD's from the ENVIRONMENTAL SAMPLING SUPERVISOR at the EOF.

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E.1. 4 '

Collect samples at the following location as directed by the ENVIRONMENTAL SAMPLING SUPERVISOR:

E.1.4.1 Danville Water Authority E.1.4.2 Control location above the discharge line E.1.4.3 Location below the discharge line E.1.5 When all samples have been collected, contact the ENVIRONMENTAL SAMPLING SUPERVISOR to arrange for transportation of the ssmples to the analysis laboratory.

Samples should b labeled with the following information before being transported:

E.1.5.1 Location of sample E.1.5.2 Type of sample E.1.5.3 Amount and frequency'of' sample E.1.5.4 Time sample was taken j

E.1.6 Wait for further instructions from the ENVIRONMENTAL SAMPLING SUPERVISOR.

GASEOUS RELEASE E.2.0 Upon notification of an EMERGENCY by the ENVIRONMENTAL SAMPLING SUPERVISOR obtain the following information:

l-E.2.1 Location of initial samples to be collected E.2.2 Type of samples to be :ollected E.2.3 Number of samples to be collecteo at each location E.2.4 Perform inventory of sample kits located at Susquehanna Biological Laboratory.

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pO Attachment E'.

EP-IP-044 Revision 1 Page 15 of 65 Refer to E.1.2.1-10 of this procedure.

E.2.5 Before proceeding to-initial sample location, pick up SRD's and TLD's from the ENVIRONMENTAL SAMPLING SUPERVISOR at the EOF.

E.2.6 Collect the environmental samples as_ directed by the ENVIRONMENTAL SAMPLING SUPERVISOR and in accordance with the sample collection procedures in Attachment I and the supplemental sample collection procedures in Attachment J.

E.2.7 When sample collection is complete, transport samples to the Susquehanna Biological Laboratory. The emergency TLD's should be placed in a TLD shield and transported to the EOF for analysis.

E.2.8 When all samples have been collected, contact the ENVIRONMENTAL SAMPLING SUPERVISOR to arrange for transportation of tb samples to the analysis laboratory.

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s-Attachment F -

EP-IP-044 Revision 1 Page 16 of 65 ACTION STEP ADMINISTRATIVE SUPPORT MANAGER F.1.0 The ADMINISTRATIVE SUPPORT MANAGER will:

F.1.1 Upon request from the ENVIRONMENTAL 3AMPLING SUPERVISOR, s

dispatch transport couriers to pick up environmental samples g..

and transport them to the analysis laboratory, Radiation Management Corporation. 3508 Market Street, Philadelphia, Pa., or, if requested, to the EGF.

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Page 1 of 1

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Attachment G EP-IP-044 Revision 1 1

Page 17 of.65 CALCULATIONS OF RIVER TRANSIT TIME Tp DANVILL2'FROM SSES G.1.0 Given a liquid discharge from the Susquehanna SES the following method will be used to determine the amount of time for the discharge to -

travel from SSES to the-Danville Water Authority.

G.1.1 Obtain the river' level, X; in meters above mean sea level, from the Susquehanna biological. laboratory personnel. This is read from_ a river, level gauge in the laboratory.

(Phone #

is.

s

../

Calculate the river flow velocity (Y), in meters /sec. by the use of the following equation:

52.8 0.356 (X)

Y (m/s)

=

The transit time (t) to Danville can then be calcolated by the following:

50,000 m Y (m/s)

+ 3600 sec./hr.

t =

where 50,000 m is' the river distance from SSES to the Danville Water Authority.

I Examole river level (x) 148.92 m

=

river flow velocity (y) = 0.356 (148.92m) - 52.8 (y) = 0.2205 m/s transit time (t) = 50,000 m

+ 3600 sec/hr = 63 hrs.

.2205 m/s G.2.0 Dilution Factor at Susquehanna SES Given a liquid discharge exceeding technical specification limits from the Susquehanna SES the following method will be used to determine the dilution factor in the river at the time of the discharge.

c Determine from the RADIATION SUPPORT MANAGER:

1.

The total volume (gallons) of the release, A.

2.

The total time (minutes) of release, 8.

Page 1 of 8

Attachment G.

EP-IP-044 Revision 1 page 18 of 65 Obtain! the river level, X, in meters above mean sea level from the Susquer.anr.a biological laboratory personnel.

Calculate the total release rate, C, by the following equation:

A (gal) 1 min-B- (min) x 60 sec.

C (gal./sec.)

=

where

= Total Release Volume (gal)

B = Total Release Time (min)

Calculate tFe river flow 0 (gal /sec), by converting the-river level, X,-

l to river flow E (M'/sec) with the use of the attached river, depth, flow, level conversion table. Then multiply by-the appropriate

-conversion factor:

(1 M' 264.2 gal)

=

( ))

O_(gal /sec)

E (M'/sec) x 264.2 (gal /M')

=

where:

E = river flow (M2/s); from the conversion table.

Calculate the dilution factor, F, by use of the following equation:

C (cal /sec)

F

=

0 (gal /sec)-

Example:

22,000 gal Total Volume of Release A =

Total Time of Release B 30 min

=

River Level X = 148.92 M.

A 22,000 gal min C=5=

30 min x 60 sec

= 12.22 gal /see P.tver Flow (E) (M2/sec)- = 205.6 M2/sec-(from conversion table.)

E (M2/sec) x 264.2 (gal /M')

River Flow 0, (gal /sec)

=

0 = 205.6 (M'/sec) x 264.2 (gal /M2)

,-s 0 = 54,320 gal /sec

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Attachment G EP-IP-044 Revision 1 Page 19 of 65 The dilution factor (F) may now be determined:

C 12.22 (gal /sec)

D = 54,320 (gal /sec)

F

=

2.25 x 10

• F

=

. NOTE:

FOR AN UNDETERMINED RELEASE TIME (B) OR QUANTITY OF DISCHARGE (A), A VALUE OF 1 MINUTE PER 10,000 GALLONS RELEASED SHOULD BE ASSUMED.

G.3.0 CONCENTRATION OF RADI0 ACTIVITY AT DANVILLE Obtain the initial radioactivity concentration in the water at the blowdown line from the RADIATION SUPPORT MANAGER (G).

Multiply this number by the dilution factor calculated in I.2.0 to obtain the concentration of radioactivity released into the Susquehanna river (H).

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O Attachment G '.

EP-IP-044 Revision 1 Page 20 of 65 To calculate the concentration which reaches Danville, obtain the dilution factor in the Susquehanna river to Danville from Table 5.2-19 which is attached at the. end of this section. Divide the concentration released into the Susquehanna by the dilution factor to Danville to obtain the calculation cf radioactivity expected to reach the Danville Water Authority.

Exampl':

e o

Initial concentration at blowdown time =

4.2 x 10 8 uCi/ml (G) o Dilution factor at Susquehanna SES =

3 x 10 * (F) o Concentration released to Susquehanna O

=rxo

= 1.26 x 10

• uCt/ml (H) o Dilution betwe n Susquehanna SES and Danville (far January) = 314 (I) o Concentration at Danville Water Authority

= ('l) + (I)

I

= 3.82 x 10

• uCi/nl O

Page 4 of 8 l

Attachment G.

EP-IP-044 Revision 1 Page 21 of 65 RIVER DEPTH, LEVEL, FLOW CONVERSION TABLE AT THE SUSQUEHANNA SES BIOLOGICAL LABORATORY Water Depth Level

_Flov Depth Level Flow (ft.)

(m above ms1)

(m3/s)

(ft.)

(m above ms1)

(m3/s) 2.0) 147.82 0.8 5.5) 148.89 196.5 2.1) 147.85 3.1 5.6) 148.92 205.6 2.2) 147.C8 5.5 5.7) 148.95 215.0 2.3) 147.91 8.1 5.8) 148.98 224.5 2.4) 147.94 10.9 5.9) 149.01 234.3 2.5) 147.97 13.9 6.0) 149.04 244.2 2.6) 148.00 17.1 6.1) 149.07 254.4 2.7) 148.03 20.5 6.2) 149.10 264.7 2.8) 148.06 24.2 6.3) 149.13 275.3

- bm) 2.9) 148.09 28.0 6.4) 149.16 286.0 3.0) 148.12 32.0 6.5) 149.19 297.0 3.1) 148.16 36.2 6.6) 149.22 308.1 3.2) 148.'19 40.6 6.7) 149.25 319.4 3.3) 148.22 45.2 6.8) 149.28 331.0 3.4) 148.25 50.0 6.9) 149.31 324.7 3.5) 148.28 55.0 7.0) 149.34 354.6 3.6) 148.31 60.2 7.1) 149.37 366.7 3.7) 148.34 65.6 7.2) 149.40 379.1 3.8) 148.37 71.1 7.3) 149.44 391.6 3.9) 148.40 76.9 7.4) 149.47 404.3 4.0) 148.43 82.9 7.5) 149.50 417.2 4.1) 148.46 89.1 7.6) 149.53 430.4 4.2) 148.49 95.5 7.7) 149.56 443.7 4.3) 148.52 102.1 7.8) 149.59 457.2 4.4) 148.55 108.8 7.9) 149.62 470.9 4.5) 148.58 115.8 8.0) 149.65 484.8 4.6) 148.61 123.0 8.1) 149.68 498.9 4.7) 148.64 130.4 8.2) 149.71 513.2 4.8) 148.67 137.9 8.3) 149.74 527.7 4.9) 148.70 145.7 8.4) 149.77 542.4 5.0) 148.73 153.7 8.5) 149.80 557.3 5.1) 148.76 161.8 8.6) 149.83 572.4 5.2) 148.80 170.2 8.7) 149.86 587.7 5.3) 148.83 178.8 8.8) 149.89 603.2 5.4) 148.86 187.5 8.9) 149.92 618.9 Page 5 of 8

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Attachnient G ~

EP-IP-044 Revision 1 Page 22 of 65 Water Depth Level Flow Depth Level Flow (ft.)

(m above ms1)

(m3/s)

(ft.)

(m above ms1)

(m3/s) 9.0) 149.95 634.8 12.8) 151.11 1385.4 9.1)-

149.98 650.9 12.9) 151.14 1409.0 9.2) 150.01 667.2 13.0) 151.17 1432.8 9.3) 150.05 683.7 13.1) 151.20 1456.9 9.4) 150.08 700.3 13.2) 151.23 1481.1 9.5) 150.11 717.2 13.3) 151.26 1505.5 9.6) 150.14 734.3 13.4) 151.29 1530.1 9.7) 150.17 751.6 13.5) 151.33 1554.9 9.8) 150.20 769.0 13.6) 151.36 1579.9 9.9) 150.23 786.7 13.7) 151.39 1605.1 10.0) 150.26 804.6 13.8) 151.42 1630.5 10.1) 150.29 822.7 13.9) 151.45 1656.1 10.2) 150.32 840.9 14.0) 151.48 1681.9

' /~ )

10.3) 150.35 859.4 14.1) 151.51 1707.9 10.4) 150.38 873.1 14.2) 151.54 1734.1 10.5) 150.41 896.9 14.3) 151.57 1760.5 10.6) 150.44 916.0 14.4) 151.60 1787.0 10.7) 150.47 935.2 14.5) 151.63 1813.8 10.8) 150.50 954.7 14.6) 151.66 1840.8 10.9) 150.53 974.4 14.7) 151.69 1868.0 11.0) 150.56 994.2 14.8) 151.72 1895.4 11.1) 150.59 1014.3 14.9) 151.75 1923.0 11.2) 150.62 1034.5 15.0) 151.78 1950.7 11.3) 150.65 1054.9 15.1) 151.81.I 1978.7 11.4) 150.69 1075.6 15.2) 151.84

• 2006.9 l

11.5) 150.72 1096.4 15.3) 151.87 2035.2 11.6) 150.75 1117.5 15.4) 151.90 2063.8 l

11.7) 150.78 1138.7 15.5) 151.93 2092.6 11.8) 150.81 1160.2 15.6) 151.97 2121.5 15.7) 152.00 2150.7 11.9) 150.84 1181.8 15.8) 152.03 21EG.1 12.0) 150.87 1203.6 15.9) 152.06 2209.6 12.1) 1b0.90 1225.7 16.0) 152.09 2239.4 12.2) 150.93 1247.9 16.1) 152.12 2269.3 12.3) 150.96 1270.3 16.2) 152.15 2299.5 12.4) 150.99 1292.9 16.3) 152.18 2329.8

~

12.5) 151.02 1315.8 16.4) 152.21 2360.4 12.6) 151.95 1338.8 16.5) 152.2d 2391.1 12.7) 151.08 1362.0

,()

l Page 6 of 8

O Attachment G~ ~

EP-IP-044 Revision 1 Page 23 of 65 Water Depth Level Flow Depth Level.

Flow (ft.)

(m above msl)

(m3/s)

(ft.)

(m above msl)

(m3/s) 16.6) 152.27 2422.1 20.4) 153.43 3744.8 16.7) 152.30 2453.2

~20.5) 153.46 3783.4 16.8) 152.33 2484.6 20.6) 153.49 3822.3 16.9) 152.36 2516.1 20.7) 153.52 3861.4 17.0) 152.39 2547.8 20.8) 153.55 3900.6 17.1) 152.42 2579.8 20.9) 153.58 3940.1 17.2) 152.45 2611.9 21.0) 153.61 3979.8 17.3) 152.48 2644.2 21.1) 153.64 4019.6 17.4) 152.51 2676.8 21.2) 153.67 4059.7 17.5) 152.54 2709.5 21.3) 153.70 4099.9 17.6) 152.57 2742.4 21.4) 153.73 4140.4 17.7) 152.61 2775.5 21.5) 153.76 4181.0 17.8) 152.64 2808.9 21.6) 153.79 4221.9 7 ')

'5'

22.4 21 7) 15.82 4262.9 CJ' 18.0) 152.70 2876.1 21.8) 153.86 4304.2.

18.1) 152.73 2910.0 21.9) 153.89 4345.6 18.2) 152.76 2944.1 22.0) 153.92 4387.3 18.3) 152.79 2978.5 22.1) 153.95 4429.1 18.4) 152.82 3013.0 22.2) 153.98 4471.1 18.5) 152.85.

3047.7 22.3)-

154.01 4513.4 18.6)-

152.88 3082.'6 22.4) 154.04 4555.8 18.7) 152.91 3117.7 22.5) 154.07 4598.4 18.8) 152.94 3153.0 22.6) 154.10 4641.3 18.9) 152.97 3188.5 19.0) 153.00 3224.2 22.7) 154.13 4684.3 19.1) 153.03 3260.1.

22.8) 154.16 4727.5 19.2) 153.06 3296.2 22.9) 145.19 4771.0 19.3) 153.09 3332.5 23.0) 154.22 4814.6 19.4) 153.12 3369.0 23.1) 154.22 4814.6.

19.5) 153.15 3405.7 23.2) 154.28 4902.4 19.6) 153.18 3442.5 23.3) 154.31 4946.6 19.7) 153.21 3479.6 23.4) 154.34 4991.1 19.8) 153.25 3516.9 23.5) 154.37 5035.7 19.9) 153.28 3554.4 23.6) 154.40

.'10.5 20.0) 153.31 3592.1 23.7) 154.43 5125.5 20.1) 153.34 3629.9 23.8) 154.46 5170.7

~

20.2) 153.37 3668.0 23.9) 154.50 5216.1 20.3) 153.40 3706.3 24.0) 154.53 5261.'

8 NOTE: 1 m /s = 264.18 gal /s Page 7 of 8 Ii i u m mi i i,

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Attacte nt G EP-IP-044 Revision 1 Pa9e 24 of 33 SusquillANNA SES-ER-OL IABLE 5.2-19 ESTIMATED MOHillLY DISPLitSION FACTORS FOR Ti4E SUSQUEllANNA RIVER DOWNSIREAM Of SUSQUEllANNA SES M l l.L S FROM YEARLY SITE D I SCllAltGE JAN IED MAR APR MAY.

JUN JUL AUG SEP OCT NOV DEC AVE.

WAPWAltOPEN.

1.6 82 99 181 161 105 T6 86

.31 33 44 70 99 86 4

EEACl4 ilAVEN 3.1 170 206 348 404 218.

121 64 8s3 47 (22 '

145 206 1 FO RESCOPECK 5.5 201 244 445 516 258 143 80 51 53 77 172 244 207 BERWICK 6.4 214 259 473 549 2T4 1 *>2 82 53 56 79 183 259 219 MIFILINVILLE 11.1 239 290 528 613 307.

175 92 60 62 88 204 290 246 ALMEDIA 15.s 257 312 556 646 331 184 101 66 68 97 221 312 263 BLOOMSBURG 18.9 270 328

$98 678 347 197 108 70 73 103 237 328 278 CATAWISSA 21.8 283 343 626 710 363 2U6 112 73 75 108' 247 343 291 DANVILLE 30.8 314 381 681 791 8:0 86 228 1 284 82 86 112 269 281 321 WOLVERTON STATION 37.0 333 404 723 823 428 242 133 87 92 128 285 404 340 NORTilUMBERLAND 8:3.0 38 5 419 751 872 884 251 137 90 93 1 38:

301 419 355 6

44 SUNOURY 83.5 352 42T 765 888 452 255 140 92 9T 136 307 427 368 4

Pigs 8 of 8 I

O Attachment H' '

EP-IP-044 Revision 1 Page 25 of 65 DATA SHEET I.

TRAINSIT TIME FG.t LIQUID OISCHARGE FROM SUSQ. SES TO DANVILLE River Level =

meters above mean sea level (X)

(m above msl)

' ?-

River Flow Velocity (meters /sec.') = 0.356(X)-52.795 meters /sec.

=

(Y)

Distance from Susquehanna SES to Danville = 50 km (River Distance)

Transit Time = 50,000 meters x 1 hr.

Y meters /sec. 3600 sec.

hrs. (t)

=

II. CONCENTRATION OF RADIOACTIVITY

"^

~In'itial Concentration in' Blowdown =

uCi/ml(A)

Volume of Release =

gal (d)

Time of Release to Length of Release =

min. (d)

Time Release will Arrive at Danville =

III. OETERMINATION OF DILUTION FACTOR Total Release Rate = B (gal ) x 1 min.

C (min.)

60 sec.

gal./sec. (0)

=

River Flow m /sec. (E) (from Conversion Table) 8 8

8 River Flow (gal./sec.) = E (m /sec.) x 264.3 (gal./m )

.- O

.=

gal./sec. (F)

Form EP-IP-044-1, Rev. O, Page 1 of 2

O..

v Attachment H'.

EP-IP-044 Revision 1 Page 26 of 65 Dilution Factor = D (gal./sec.)

F (gal./sec.)

(G)

=

IV. CONCENTRATION OF ACTIVITY AT DANVILLE Concentration at-Diffuser (SSES) = A~(uC1/ml) x G

~

uCi/ml (H)

=

Concentration at Danville = H (uCi/ml) + I (Danville Dilution Factor, Environmental Report Table 5.2-19) uCi/ml (J)

=

RECOMMENDATION:

O

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I Form EP-IP-044-1, Rev. O, Page 2 of 2

( )

( _./

Attachment I.

EP-IP-044 Revision 1 Page 27 of 65 SAMPLE COLLECTION PROCEDURE I.1. 0 -

Milk-Collection of milk samples will begin approximately 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br /> (1 day) after the possible release of iodine. Milk sampling frequency will initially be every' day for eight days. If milk fodine concentration has returned to less than 10 pCi/ liter, sample frequency will be reduced to once per three days. When the iodine concentration is less than 1 pCi/ liter, sampling will return to the routine environmental monitoring program sampling frequency.

In tabular form this is as follows:

Milk locine Concentration Milk Sampiing F,equency First 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br /> No Sample Nex eight days Dail9"

'J

>10 pC1/litor Every day

<10 pCi/ liter

.Every third day

<1 pCi/ liter Routine REMP (c.anthly)

This schedule may be applied on an individual farm basis or to all the farms listed as a group, as determined by the ENVIRONMENTAL SAMPLING l

SUPERVISOR.

I.1.1 Locations which may be sampled:

Sample Coas Farm Name Location SS-MLK-12B2 Schultz Farm 1.69 mi WSW SS-MLK-1283 Young Farm 1.96 mi WSW i

SS-MLK-6C1 Moyer Farm 2.7 mi ESE l

SS-MLK-1001 Ross Ryman Farm 3.02 mi SSW

~'

SS-MLK-1202 Dagostin Jug Milk 3.72 mi WSW SS-MLK-5El Bloss Farm 4.4 mi E

(^)

Page 1 of 8

l

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Attachment I.

EP-IP-044 Revision 1 Page 28 of 65 SS-MLK-13E3 Dent Farm 4.9 mi W SS-MLK-10G1 Davis Farm 14 mi SSW "L.

SS-GMK-801 Poltrock 3.19 mi SSE

• Goat Milk

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~

I.1.2 It is very important to note the following information for each milk sample taken.

I.1.2.1 Date I.1.2.2 Time I.1.2.3 Location I.1.2.4 Number of milkings represented in this sample (e.g., morning only, morning plus previous evening, hs..

plus previous morning, etc.).

I.1.2.5 Are the cows 1) on pasture, 2) confined to indoors, ej.>

3) outdoors not on pasture, 4) other.

I.1.3 Collect two gallons of milk (if possible) at each location --

carefully label each container with the above information.

I.1.4 When all samples have been collected, arrange-for transportation of the analysis laboratory (s) as soon as possible.

I.1.5 If requested by the ENVIRONMENTAL SAMPLING SUPERVISOR, obtain a separate sample for Pa. DER, NRC, EPA, or other agencies.

The ENVIRONMENTAL SAMPLING SUPERVISOR will provide fastruction on what to do with these samples.

I.1.6 Give the farmer all information you are sure of (e.g.,

results of previous analyses, samoling schedule, etc.).

NOTE:

IF NOT SURE OF REQUESTED INFORMATION CBTAIN CORRECT INFORMATION FROM THE ENVIRONMENTAL SAMPLING SUPERVISOR.

I.1.7 Contact the ENVIRONMENTAL SAMPLING SUPERVISOR on each i.

scheduled sampling day after the eight days to datermine future sampiing schedule.

.n O

Page 2 of 8

b Attachment I EP-IP-044 Revision 1 Page 29 of 65 I.1.8 Keep running' log of all samples.

I.1.9 For further instruction on the collection and shipment of milk samples, refer to Appendix f of Attachment J.

I.2.0 Food Products and Vegetation Discussion-One;of.1the earliest indications of-the presence of todine'

,.;t will be on the air iodine cartridget if available, and food products and vegetation samples. For this reason, these media, if available, will be collected on the first day. Suitable vegetat'on samples incluces grass, broccoli, cabbage, turnips, collards, skunk cabbage, corn apples, strawberries, etc.

I.2.1 If vegetation is available, cellect in accordance with the normal procedure RMC-T46.

I.2.2 Pasture grass, green leafy yeaetables or vegetation may oe collected at the following locations, or as directed by the

(,sc

)

ENVIRONMENTAL SAMPLING SUPERVISOR.

Sample Code Location Name Location m

SS-FPV-SS6 Biological Lab

.76 mi E SS-FPV-1281 Kisner Farm 1.15 mi WSW SS-FPV-1101 Zehner Bros. Farm 3.3 mi SW SS-FPV-1102 Lanning Farm 3.8 mi SW SS-FPV-12F4 Lupini Farm 8.3 mi WSW SS-FPV-12FS Seesholtz Farm 8.6 mi WSW SS-FPV-2H1 Yalicks Produce" 21 mi NNE SS-PAS-15Al-Serafin Farm

.87 mi NW SS-PAS-801 Poltrock Farm 3.19 mi SSE

• Control near Dallas, Pa.

I.2.3 Arrange for transportation to the analysis laboratory (s) as soon as possible.

?..

Page 3 of 8

O Atti.chment I '

EP-IP-044 Revision I Page 30 of 65 I.2. 4 Check with the ENVIRONMENTAL SAMPLING SUPERVISOR for resample frequency.

I.2.5 For.further instruction on the collection of food product and vegetation samples, refer'to Appendix 9 of Attachment J.

I.3.0 Air Iodine and Air Particulate

.~

Discussion:

In the event of an accident, selected REMP air todine catridges and air particulate filters may be samplee as indicated in accordance with Procedure RMC-T46 and as directed by the ENVIRONMENTAL SAMPLING SUPERVISOR.

I.3.1 For each locatien, note the following information on each sample and on the sample logs.

o Date Charcoal cartridge and/or air filter installed.

o Date of this collection.

\\

o Time of collection

.o Volume of.. air. sampled o Location I.3.2 Contact ENVIRONMENTAL SAMPLING SUPERVISOR to dete;mine l

collection frequency.

I I.3.3 Sampling' Frequency Air Particulate / Air Iodine Air Particulate Conenntration Sampling Frequency

<0.07 pCi/m Routing REMP (weekly) 2

<0.7 pCi/m 2X Routine REMF (twice per week) 8

<7.0 pCi/m 3X Routine REMP (every other day) 2

>7.0 pC1/m' Daily

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Attachment I.

EP-IP-044 Revision 1 Page 31 of 65 Air Iodine Concentration Sampling Frecuency

<0.02 pCi/m Routine REMP 2

<0.2 pCi/m Twice weekly 2

<2.0 pCi/m Every other day 2

. j7 -

>2.0 pCi/m Daily 2

I.3.4 Air Particulate and Air Iodine Locations Samole Ccde Location Name Location SS-APT-2S2 Energy Information 0.9 mi NNE Center SS-APT-SS4 West of Biological 0.8 mi E Consultants SS-APT-1152 Golomb House 0.4 mi SW SS-APT-981 Transmission Line South 1.3 mi S of Route 11 SS-APT-102 Near Mocanaqua Substation 4.0 mi N SS-APT-301 Pond Hill 3.4 mi NE SS-APT-12G1 Bloomsburg, PA 15 mi WSW

..s SS-APT-7H1 PP&L Roof, Allentown 47 mi SE I.3.5 For further instruction on the collection of air particulate filters and air iodine cartridges, refer to Appendix 10 of Attachment J.

1 l

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Attachment I.

EP-IP-044 Revision 1 Page 32 of 65 I.4.0 Thermoluminescent Dosimeters TLD's will be collected by ENVIRONMENTAL SAMPLE COLLECTORS under the direction of the ENVIRONMENTAL SAMPLING SUPERVISOR. Replacement TLO's will be picked up at the EOF and installed at each collection location.

I.4.1 The ENVIRONMENT,% SAMPLING SUPERVISOR,. upon request from the

. RADIAT. ION. SUPPORi 4% NAGER, will direct the ENVIRONMENTAL -

v..

SAMPLE COLLECTORS to exchange the emergency TLD's. The location of the TLD's to be exchanged will also be relayed through the ENVIRONMENTAL SAMPLING SUPERVISOR.

I.4.1.1 West Side River TLD Location Code Distance / Direction Location Descriotion SS-IDM-IS2E 0.24 mi N Security Fence SS-IDM-253E 0.20 mi NNE Security Fence SS-ICM-354E 0.30 mi NE Security Fence SS-IDM-453E

.0.20 mi_NNE Security Fence r

SS-ICM-557E 0.22 mi E Security Fence SS-IDM-654E 0.20 mi ESE Security Fence SS-IDM-753E 0.20 mi SE Security Fence SS-IDM-852E 0.20 mi SE Security Fence SS-IDM-951E 0.26 mi S Security Fence SS-IDM-1051E 0.40 mi WSW Security Fence SS-IDM-1153E 0.34 mi SW Security Fence SS-IDM-12S3E 0.40 mi WSW Security Fence SS-IDM-12E1E 4.68 mi WSW Berwick Hospital SS-10M-1352E 0.38 mi W Security Fence SS-IDM-14S2E 0.40 mi-WNW Security Fence 4.11 mi WNW Knouse Farm s)

SS-IDM-14E1E Page 6 of 8 a

,*s U

Attachment I '.

EP-IP-044 Revisien 1 Page 33 of 65 SS-IDM-15S3E 0.34 mi NW Security Fence SS-IDM-16S1E 0.30 mi NNW Security Fence SS-IDM-16FIE 7.81 mi NNW Hidlay Residence /

Huntington Mills

!*l

' I.'4.1. 2 ' East Side River r

T

~

TLD Location Code Distance / Direction Location Descriotion SS-IDM-2FIE 5.88 mi NNE St. Adalberts Cemetery SS-IDM-4E1E 4.8 mi ENE Pole #46422 N35-197 SS-IDM-6E1E 4.74 mi ESE St. James Church SS-IDM-SD2E 3.95 mi SSE Mowry Residence s

SS-IDM-10D2E 3.00 mi SSW Ross Ryman Residence I.4.2 The secondary (QC) TLD's will be picked up after the emergency has terminated as directed by the ENVIRONMENTAL

(

SAMPLING SUPER'!'.SOR. The location to be changed are as follows:

s I.4.2.1 West Side River TLD Location Code Distance / Direction Location Descriotion

j el SS-IDM-152Q 0.24 mi N Security Fence SS-IDM-3S4Q 0.30 mi NE Security Fence SS-IDM-557Q 0.22 mi E Security Fence SS-IDM-7530 0.20 mi SE Security Fence SS-IDM-951Q 0.26 mi S Security Fence SS-IDM-11S3Q 0.34 mi SW Security Fence SS-IDM-12E10 4.68 mi WSW Berwick Hospital 7

~s SS-IDM-13S2Q.

0.38 mi W Security Fence

(

)

v Page 7 of 8

Attachment I.

EP-IP-044 Revision 1 Page 34 of 65 SS-IDM-14E10 4.11 mi WNW Knouse Farm Securigy Fence SS-IDM-1553Q 0.34 mi NW SS-IDM-16F10 7.81 mi NNW Hidlay Residence /

Huntington Mills

I.4.2'.2 East. Side River.

4 G-TLD Location Code Distance / Direction Location Description SS-IDM-2P1Q 5.88 mi NNE St. Adalberts Cemetery SS-IDM-4E1Q 4.8 mi ENE Pole #46422 N35-197 SS-IDM-6E1Q 4.74 mi ESE St. James Church SS-IDM-802Q 3.95 mi SSE Mowry Residence

(])

SS-IDM-1002Q 3.00 mi SSW Ross Ryman Residence I.4.3 For further instruction on TLD exchange, refer to Appendix 11

.y of Attachment J to this procedure.

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Page 8 of 8 n

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- + - - - - - + -~

O Attachment J'.

EP-IP-044 Revision 1 Page 35 of 65 SUPPLEMENTAL SAMPLE COLLECTION PROCEDURES FOR-SUSQUEHANNA SES 1.0 PURPOSE The purpose of this procedure is to provide instructions for the collection of samples for analysis by RMC.

ge:, q, -

',~

s 2.0' SCOPE This procedure shall apply to all samples collected for Susquehanna SES Preoperational REMP which are to be analyzed by the Phila. Division of RMC.

3.0 DEFINITIONS N/A

4.0 REFERENCES

f'}

4.1 USNRC Regulatory Guide 4.1, Measuring and Reporting of Radioactivity in the Environs of Nuclear Power Plants.

4.Z USNRC Regulatory Guide 4.3, Measurements of Radionuclides in the Environment. Analysis of I-131 in Milk.

~

4.3 USNRC Regulatory Guide 4.8, Environmental Technical Specifications for.

Nuclear Power Plants (for comment).

4.4 H. A.S.L. Procedure Manual "HASL-300", ed. John Harley, Health and Safety Laboratory, New York, NY (1972).

4.5 ANSI-N13.1-1969, Guide to Sampling Airborne Radioactive Materials in Nuclear Facilities.

4.6 ORP/SID-72-2, Environmental Radioactivity Surveillance Guide, issued by the U.S. EPA.

5.0 PRECAUTIONS See Appendices 6.0 APPARATUS See Appendices Page'1 of 30

( \\

'u J Attachment J.

EP-Ip-044 Revision 1 Page 36 of 65 7.0 INSTRUCTIONS 7.1 The RMC sample identification system shall be used for all samples.

It consists of a three part code.

7.1.1 The first part is the power station identification coce consisting of two letters.

c.

7.1.2 The sec'ond part is three letters long, identifying the media

^

being sampled. The media codes are listed in Table 1.

7.1.2.1 Codes labeled with an

• require a comment that further describes the sample.

7.1.2.2 A complete description is required for any sample not covered by one of the cocas. A code will be assigned at RMC.

7.1.3 The third part is a location code based on direction and

(')

distance from the site and consists of four symbols.

v 7.1.3.1 The first one to two symbols represent the sixteen angular sectors of 22 1/2 degrees centered about

.g the reactor site.

Sector one is divided evenly by the North axis and the other sectors are numbered in a clockwise direction (i.e., 2 = NNE, 3 = NE, 4

= ENE, etc.)

7.1.3.2 The next symbol is a letter which represents the radial distance from the site (See Table 2).

7.1.3.3 The last symbol is the station numerical designation within each sector and zone (i.e., 1, 2,3...).

7.2 Sample designation, along with the remainder of the sampling information shall be recorded on the sample receipt sheet (provided by RMC).

7.2.1 Sample type and collection frequency shall be entered at the top of the sample receipt sheet.

~~

7.2.2 One line of the sample receipt area shall be completed for each sample collected.

.7.2.3 Sample codes 'shall be entered first, followed by the sampiing e,

( )

dates.

i Page 2 of 30 l

• p, V

Attachrent J ~

EP-IP-044 Revision 1 Page 37 of 65 7.2.4 For continuous samples (TLD, APT, AIO) both start and stop dates shall be given.

7.2.5 A single date in the."DATE STOPPED" column shall be used for grab samples.

7.2.6 The time spaces shall be completed if the sample is for air ar-a todine.. j,..

g y.

7.2.7 The name of the collector and deliverer shall be listed along with the date collected and delivered.

7.3 Sample Containers 7.3.1 Two gallon, new, polyethylene bottles shall be used for liquid samples.

7.3.1.1 These bottles shall be rinsed with the media to be sampled prior to sampling, whenever possible.

O 7.3.1.2 Bottles shall be sealed with a screw top.

', 7.3.2,

Solid samples shall.be. collected in new plastic jars or heavy duty plastic bags. Containers shall be sealed after collection.

7.4 Samples shall be delivered to the sample receiving area at RMC as soon as possible after callection.

7.4.1 If the possibility of spoilage exists, then samples shall be frozen (except milk).

7.4.2 No preservatives or additives shall be used with these samples unless authorized by RMC.

7.4.3 The U.S. Mail, other parcel services, or messenger may be used for sample delivery.

7.A.4 Any effluent sample or any sample that is suspected of containing levels of any radionuclide exceeding four times the level expected in background environmental samples shall be specifically labeled " ATTENTION HOT LAB".

7.5 Sample collection procedures. See Appendix I-15.

Page 3 of 30

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Attachment J.

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i-EP-IP-044 Revision 1 i

Page 38 of 65 l

8.0REddRDS i

All records shall be maintained in accordance to RMC Procedure No. T-44,

" Sample and Data Coordination Procedures".

t i

9.0 REPORTING t

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l. -, - _..... _,. - -, -.. _ - -. -., - -.. _ _ _.. _.,.. _ _. - _ _ _ - _. -.. _.. _. -., _.,,_ __._____ _. _.__ _

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Attachment J.

EP-IP-044 Revision 1 Page 39 of 65 TABLE 1 AIO - Air Iodine "FPB - Food Products APT - Air Particulate "GAX - Game CRB - Crab IDM - TLD-CaSO

• AQF - Fi sh MLK - Milk AQ1 - Aquatic'Invertegrates

.PWR.- Potable. Water-Raw CLM - Clams PWT - Potable Water-Treated OYS - Oysters RWA - Rain Water-Precipitation AQS - Sediment SWA - Surface Water AQP - Aquatic Plants FPB - Beef SQL - Soil GAD - Deer

• FPL - Green Leafy Vegetables WA - Well Water FPE - Eggs PAS - Pasture

• Requires a comment that further describes the sample.

O T^8's 2 S = On-site location E = 4-5 miles off-site A = 0-1 miles off-site F = 5-10 miles off-site B = 1-2 miles off-site G = 01-20 miles off-site C = 2-3 miles off-site H = >20 miles off-site D = 3-4 miles off-site l

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Attachment J.

EP-IP-044 Revision 1-Page 40 of 65 I

APPENDIX l' "-

SURFACE WATER, GRAB Rev 3

- Three (3) gallons to be collected Nov 80 2*"

Materials Needed

~

Rev 3 1.

Two two gallon, new polyethylene bottles with screw caps Nov 80 2.

Plastic sampling container and line (if required at the location) 3.

Labels 4.

Marking pencil 5.

Sample receipt sheets Sampling Procedure 1.

- Samples may be taken from a boat, jetty or bridge, or by wading into the water if care is taken not to disturb the sediment.

( })

2.

Rinse sample bottles three times with water to be sampled.

3.

Collect three gallons of the water sample in the sample bottles.

Rev 3 Nov 80 4.

Seal the containers.

5.

Put labels on the bottles and give the following information:

a.

Station number and sample code number b.

Type of sample c.

Date of sampling d.

Your name e.

Size of sample 6.

Log this information onto the sample receipt sheet provided.

Precautions 1.

Do not wear a tritium luminous dial watch, as it may contaminate the sample.

2.

Do not disturb the sediment in the sampling area.

If the sediment is disturbed, do not sample until the water is quiescent again.

/"N V

Page 6 of 30

O Atta.-hment J.

EP-1.4-044 Revision 1 Page 41 of 65 APPENDIX 2 SS-SWA-12H1 SURFACE WATER, MONTHLY COMPOSITE

.. y.

- Fiv_e hundred millil.,1ters_to be collected daily.

Materials Needed Rev 3 1.

Two two gallon new polyethylene bottles with screw caps Nov 80 2.

Labels 3.

Marking pencils 4.

Sample receipt sheet 5.

500 mi sampling bottle Samoling Procedure 1.

Turn on the continuous sampler tap - allow to run for three O-

'##tes-2.

Rinse the 500 ml. sample bottle three times with water to be sampled.

~

3.

Fill the bottle with the sample and pour into a five gallon container provided for the sample.

4.

Collect a monthly three gallon sample from the daily composites.

5.

Rinse sample bottles three times with water to be sampled.

Rev 3 Nov 80 6.

Collect three gallons of the water sample in the' sample bottles.

7.

Seal the :ontainers.

8.

Put labels on the bottles and give the following information.

a.

Station number and sample code number b.

Type of sample c.

Date of sampling d.

Your name e.

Size of sample 9.

Log this information onto the sample receipt shset provided.

O Page 7 of 30

h o

Attachment J.

EP-IP-044

-Revision 1.

Page 42 of 65 Precautions 1.

Do not wear a. tritium luminous dial. watch, as it.may contaminate.

the sample.

NOTES:

1)

Procedures 1 to 3 may be performed by treatment plant personnel.

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O Page 8 of 30 L

es Attachment J.

EP-IP-044 Revision 1 Page 43 of 65 APPENDIX 3 SS-SWA-SS8, 655.

SURFACE WATER, COMPOSITE

- Three,(3). gallons.to.be collected,

.Rev.3 Nov 80

~~

Materials Needed Rev 3 1.

Two two gallon, rew polyethylene bottles with screw caps Nov 80 2.

Sampling container with one quart capacity line 3.

Sample labels 4.

Marking pencils 5.

Sample receipt sheets Samoling Procedure r^T 1.

Samples are usually collected frorr[ 'a boat.

'O Rev 3 2.

Rinse sample bottles three times with water to be sampled at Nov'80 time of collection of'first quart.

3.

Rinse sampling container (one quart capacity) three ti.res with water to be sampled before sampling each quart.

4.

A three quart collection is taken once per week four times per month for a total volume of three gallons.

Rev 3

.I Nov 80 5.

Log the following information on the sample receipt sheei, and on the sample labels:

a.

Station and sample

[

b.

Type of sample c.

Size of sample I

d.

Date started and date stopped l

e.

Your name 1

Precautions l

1.

Do not wear a tritium luminous dial watch, as it may contaminate 7

the sample.

.2.

Do not disturb the sediment in the sampling area. If sediment is disturbed, do not sample until the water is quiescent again.

l N]

Page 9 of 30

Attachment J.

EP-IP-044 Revision 1 Page 44 of 65 4

APPENDIX 4 4

Rev 3 SS-WWA Nov 807 'SS-SWA-13E1 Rev 3

- Three (3) gallons to be collected Nov 80

.fS.

o.

Materials Needed Rev 3 1.

-Two two gallon new polyethylene bottles with screw caps Nov 80 2.

Labels 3.

. Marking pencil 4.

Sample receipt sheet Samoling Procedures 1.

Turn on the well pump - allow to run for three minutes.

2.

Rinse the sample bottles three times with the water to be sampled.

Rev _3 ~

3.

Collect three gallons of the water sample-in the sample bottles Nov 80 and seal them with screw caps.

4.

Put labels on the bottles that includes the following information:

a.

Station number and sample code number b.

Type of sample c.

Date of sampling

• 3 d.

Your name i

I e.

Size of sample 5.

Log this information onto the sample receipt sheet provided.

Precautions 1.

Do not wear a tritium luminous dial watch, as it may contaminate the sample.

l 4

O Page 10 of 30

p)

Attachment J '.

x'-

EP-IP-044 Revision 1 Page 45 of 65 APPENDIX 5 Rev 3 Nov 80-FISH

-.- n s

~

- At'least one (1) kg: of-fillets. from each species to be' analyzed

'~

should be coilacted Materials Needed 1.

Plastic bags.

2.

Collection equipment (A-C, 0-C electrofisher, trapnets, trotlines,etc.).

3.

Fillet knife, measuring board, scale, scaler.

4.

Manila tags with strings.

5.

Marking pencil.

6.

Sample receipt sheets.

p.

7.

Labels.

'd Sampling Procedure Samples are collected by the ecological consultant semi-annually 1.

in the spring and fall.

2.

Samples are collected and separated into species (agreed upon beforehand).

l 3.

Individual fish are weighed and measured (this information is recorded and forwarded in tabular form).

4.

Fish are scaled.

l 5.

Fillets are ebtained, placed into bags, sealed and labeled.

6.

Log the following information on the sample receipt sheet and l

on the manila tag:

l l

a.

Station and sample code number.

b.

Type of sample (including species).

c.

Size cf sample.

d.

Dates of sampling.

l e.

Your name.

H.

7 '.

Freeze the sample and s' hip it.

l 4 l

L..)

l Page 11 of 30

O k#

Attachment J '.

EP-i?-044 Revision i Page 46 of 65 Precautions 1.

Do not wear a tritium luminous dial watch, as it may contaminate the sample.

2.

No more than one pound of the sample should be taken from any individual fish. If a fish weighs : tore than one pound, a piece 6

of its midsection should:be used.

Ov l

of i

l 1

O Page 12 of 30 l

l l

Attachment J.

EP-IP-044 Revision 1 Page 47 of 63 APPENDIX 6 Rev 3 Nov 80 AQUATIC SEDIMENT, GRAB

~

Two (2), L gallon ~ replicates to be collected-Materials Needed 1.

One gallon jars with station designation labels.

2.

Collection equipment (these samples are usually collected by a scuba diver). Ia periods of low river levels, some stations can be samplea by wading into the appropriate area.

3.

Manila tags with strings.

4.

Marking pencil.

5.

Plastic bags.

6.

Sample receipt sheets.

rx 7.

Labels (inside and outside)

,G Sampling Procedure y <

1.

Samples are collected by the ecological consultant semi-annually in the spring and fall on same day.

2.

Sampling sites are usually reached via motor boat.

3.

1 gallon is collected by scraping sediment from the substrate into 1 gallon jars. Area covered by water.

4.

Jars are sealed with lids and transported back to the laboratory.

5.

All contents are emptied into separate plastic bags, sealed and labeled.

6.

Log the following information on the sample receipt sheet and on the manila tag:

a.

Station and sample code number.

b.

Type of sample.

c.

Size of sample.

d.

Date and time of sampling.

e.

Your name.

7.

Freeze the' sample'and ship it.

n ss/

Page 13 of 30

Attachment J.

EP-IP-044 Revision 1 Page 48 of 65 Precautions 1.

Do not wear a tritium luminous dial watch, as it may contaminate the sample.

f O

s D

Page 14 of 30

i l

O Attachment J'.

EP-IP-044 Revision 1 Page 49 of 65 APPENDIX 7 MILK Rev 1

- Three gallons (twelve liters) to be collected.

Aug 79 z.u.;,.

.?-

' Materials Needed Rev 1 1.

Two two gallon new polyethylene Lottle with a screw top.

Aug 79 2.

Labels 3.

Marking pencil.

4.

Sample receipt sheet.

5.

Ice or disposable freezer packs.

Sampling procedures 1.

If the sample it taken at a farm, ask the proprietor to turn o's the mixing tank before taking the sample.

2.

Fill the bottle with milk and seal with screw top.

3.

Put a label' on the bottl'e and give t'he following information:

~

a.

Station number and sample code number.

b.

Type of sample, c.

Date of sampling.

d.

Your name.

e.

Sl:e of sample.

4.

Log this information onto the sample receipt sheet provided.

5.

Ship in a cooler packed with ice or freezer packs.

pg 3utions 1.

Ship the sample to RMC immediately as analysis must be completed within 8 days.

n..

Page 15 of 30

/

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Attachment J.

EP-IP-044 Revision 1 Page 50 of 65 APPENDIX 8 Soil - 12 topsoil plugs to be collected (6" diameter, 0" - 2" depth)

Rev 2 12 subsoil cores to be collected (6" diameter, 2" - 6" depth)

Aug 80

_ater3als Needed M

1.

Soil auger (able to cut 6" deep) 2.

Widemouth plastic jars or plastic bags 3.

Sample locating line (rope or string) and stakes 4

Maps showing locations of soil collection points Rev 2 5.

Labels Aug 80 6.

Marking pens 7.

Sample receipt sheets Rev 4 8.

Flat blade knife Jan 81 9.

Rubber mallet (if necessary)

Rev 2 Twelve topsoil plug samples, 6" diameter and 2" deep and twelve subsoil

. (VO Aug 80 core samples, 6" diameter and 4" further down in the topsoil plug hole (2" - 6" deep) are to be taken at each of the sampling locations.

e6 Sampling Procedures-Rev 4 1.

Locate three reference points at the soil sampling locations.

Jan 81 These should be fixed land marks which are not likely.to

~

change within several years.

2.

Using the locating line equipped with large stakes at each end, l

establish a location for a fifteen to twenty foot straight l

line. Measure the line exactly.

Inclurie in the sketch, the distance from each end of the line to each reference point, six i

reference measurements (see Figure 2).

i "3.

Using the soil auger, force it into the ground to a depth of I

2" without twisting or disturbing the grass cover or surface soil in any way. This may best be accomplished by stepping on the rim of the cutter with both shoe heels.

If excessive vegetation is preser.t, this should be clipped off above the soil surface. The litter at the surface and the root mat are considered part of the soil sample.

Rev 2 4.

Gently twist the handle of the cutter to cleanly remove the Aug 80 topsoil plug.

a.c 1

V l

Page 16 of 30 l

l l

L

9

('~b

\\- >

Attachment J ~

EP-IP-044 Revision i Page 51 of 65 5.

Take all the topsoil plugs and place them in a plastic jar.

Sometimes it may not be possible to remove a 2" deep plug cleanly because of a deep root mat. A 4 or 6 inch deep cutter may be used to remove the topsoil by pounding it part way into the ground with the rubber mallet, until it is possible to remove the co*- Intact.

It is not possible to measure top soil depth accurately by this method.

~ j, Re'v 4 6.

N' ext, using the auger, take the subsoil samples down another d

Jan 81 4" (2" - 6").

Tap or scrape out the soil with a long flat blade knife.

It may not be possible to take out the entire subsoil plug in one step.

If this is the case, press and turn the auger as far dcwn as possible.

Remove the auger, scrape out the sample and repeat until a depth cf 6" is sampled.

• 7.

Using the locating line, continue to obtain soil samples 1 to 2 feet apart on the straight line.

8.

Place the soil in a plastic jar and label with the following information:

O, -s s

a.

Station number and sample code b.

Type of sample.

c.

Date of sampling d.

Your name e.

Size of sample f.

Depth Pev 2 9.

Log this information onto the sample receipt sheet provided.

i Aug 80

10. Document the exact location of all core samples in your log Rev 2 books, as shown in Figure 1.

The location of each end of'the l

Aug 80 sampling line must be identified by its distance from the same three reference points. Complete the form (> ketch) by identifying Rev 4 the sample station and number, the date and the sample number.

Jan 81 11.

Prepare the sample for shipment to the laboratory for analysis.

12.

Issue a copy of the core sample drilling locations to Radiation Management Corporation.

13.

If the sampling location is pasture or attended grass, fill all holes with topsoil and re-seed with grass.

(^\\

s.-

Page 17 of 30

4 0

Attachment J

~

EP-IP-044 Revision 1 Page 52 of 65 Where a fifteen foot straight line is impractical, any reasonable Rev 4 Jan 81 scattered set of samples can be taken, provided an accurate record of each core sample location is made, including reference to several fixed-(permanent) objects.

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l O Page 18 of 30 i.

L

~

Attachment J,

EP-IP-044 Revision 1 Page 53 of 65 FIGURE 1 SKETCH FOR LOCATING SOIL SAMPLES DATE OF SAMPLE

. STATION 4

~

SAMPLE NO.

Reference Hole to Two Landmarks i

O REMARKS:

w (signature)

SAMPLES TAKEN BY O

Page 19 of 30

i Attachment J EP-IP-044 FIGURE 2 Revision 1 e se se er es O

RP RP o

NO G

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O, R9 t

RP RP RP O.

Sample tine Page 20 of 30 T46-15 l

-O Attachment J.

EP-IF-044 Revision 1 Page 55 of 65 APPENDIX 9 VEGETATION

- Five pounds of edible portion to be collected

..J,3 Materials Needed 1.

Large plastic jar or bag and tape to seal.

2.

Labels.

3.

Marking pencil.

4.

Sample receipt sheet.

Sampling Procedures 1.

Collect enough edible portion of sample to equal five pounds and place in a plastic bag. Seal it with tape.

2.

Label the bag with the following information:

a.

Station number and sample code number.

'b.

Type of sample.

'L c.- 'Date of sampling.

d.

Your name.

e.

Size of sample.

3.

Log this information onto the sample receipt sheet provided.

Precautions 1.

Take extreme caution not to contaminate the sample with soil.

NOTE: 1) This class of sample includes edible vegetables and fruits, feedstuffs, and forage for livestock. Non-edible segetation may be substituted for unavailable leafy vegetables if leafy characteristics are similar, l

O Page 21 of 30 l

l

O Attachment J'.

EP-IP-044 Revision 1 Page 56 of 65 APPENDIX 10 AIR PARTICULATES & AIR IODINE Rev 4

- Filter or filter and cartridge to be collected.

Jan 81 3.,j Materials Neede'd 1.

Glassine evelope 2.

Plastic bag or paper envelope Rev 1 3.

Tweezers Aug 79 4.

Filter paper Rev 4 5.

Charcoal cartridge (for air iodine stations)

Jan 81 6.

Marking pencils 7.

Sample receipt sheet 8.

Assorted tools 9.

Log book Sampling Procedures s.

1.

Unlock the air sampler and look for any unusual conditions in the sampling equipment, e.g.,. loose hoses, pump not running, etc.

If problems are noted, refer to Procedure T-26.

It is very Rev 2 important that air samples not be missed. When problems are Aug 80 corrective, action.should start immediately. Every effort should be made to correct the problems prior to the next scheduled sampling period. Any unusual conditions should be noted in the log book and on the sample receipt sheet, a.

The dry gas meter has a six digit indicating mechanism, when read gives the volume of' air samples in cubic feet, during a specified sampling period.

a b.

The timers have a five or six digit indicating mechanism.

The first four digits record the number'of hours the sampler Rev 2 was on.

The fifth digit represents tenths of hours the Aug 80 sampler was on.

Those samplers with six digit timers record time to the hundredths of hours.

4 2.

Turn off the pump switch and record the dry gas meter reading.

Record the reading and runtime in the following places:

a.

Log book and/or sampler log (in air sampler) b.

Sample receipt sheet O

Page 22 of 30

Attachment J.

EP-IP-044 Revision 1 Page 57 of 65 Rev 2 3.

On the sample receipt sheet also record:

Aug 80 a.

Customer b.

Station number c.

Sample type Rev 3 d.

Date and time of sampling period

Aug 80

e., Your initials or your name Rev 2 4.

Unscrew the sample h'ead to expose 'the filters. Using tweezers Aug 80 remove the particulate filter carefully, so as not to tear the paper, and piace the filter in a glassine envelope.

If pieces of the particulate filter are stuck to the filter head, remove Rev 2 the pieces with the tweezers and put them in the glassine envelope, Aug 80 along with the the remainder of the filter. For those stations Rev 4 which have them, remove the charcoal cartridge, place it in a Jan 81 sample bag, and tie the bag shut.

Rev 4 5.

Replace filter paper and charcoal cartridge, if the station is Jan 81 so supplied, with new sampling media and insert into sempling j{ }

head. Return sampling head to sampler.

Rev 2 6.

Turn on the sampling pump and lock up the sampling station.

~

Aug 80 7.

Place all air particulate and air iodine samples in shipping-bag along with the sample receipt sheets.

Rev 2 8.

Mail to: Radiation Management Corporation Aug 80 P.O. Box 7940 Philadelphia, PA 19101 li'

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Page 23 of 30 1

4 e

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)

Attachment J.

EP-IP-044 Revision 1 Page 58 of 65 APPENDIX 11 DIRECT RADIATION

- Two TLDs to be collected.

Materials Needed

~

1.

Polyethylene bottie or " bird house".

2.

Marking pencil.

3.

Sample receipt sheet.

Samolina Procedure 1.

TLDs should be placed in the field as close as possible to the first day of the quarter.

Install all the TLDs on the same day or at least not on more than two days. When the T!.9 installation begins, place the two control TLD packets in the lead shield.

r~ )

L.,

2.

The sample station will be a brown polyethylene bottle or a formica " bird house". Unscrew the cap or unlock the " bird house".

3.

Remove the TLD packet from the sampling station. Confirm the sample location identification on the TLD packet.

4.

The accompanying sample receipt sheet lists the RMC sample ID number and the corresponding sample location identification.

Record on the sample receipt sheet for each TLD location:

Rev 5 a.

Date of sample removal.

Mar 81 b.

Time of sample removal, c.

Unusual conditions or changes concerning the TLDs or the station.

d.

Your name.

5.

Replace TLD removed with the appropriate new packet, placing the packet in the polyethylene bottle or " bird house".

Seal with a screw cap or lock the " bird house" 6.

Record on the new sample receipt sheet:

~'

a.

Date of sample installation.

b.

Time of sample installation.

7.

After all TLDs have been removed from the field, remove the t)

two control TLDs from the lead shield.

\\j Page 24 of 30

s O

Attachment J '.

EP-IP-044 Revision 1 Page 59 of 65 8.

If new TLDs have been installed,' determine the sample location identification and record on the receipt sheet.

9.

Ship the receipt sheet and the TLDs, including the control TLDs, to RMC immediately (same day) by surface carrier e.g., Greyhound,

.Co.nrail, Package Express or UPS.

Precautions ~

1.

Be sure the package is not damaged during or prior to removal.

2.

Do not enter the fenced in area of the site with the TLDs.

3.

Be certain that both the removed TLD packet and the installed TLD packet have the correct location identification.

4.

The control TLD, labeled site zero, is used to determine the intransit dose. The same intransit dose is used in the O

calculation of the dose to each TLD. For this reason,.it is Rev 5 important that the site zero TLD is in the lead shield during Mar 81 the same period that the sample TLDs are in the field. This is. accomplished by installing all..the TLDs as close as possible

'to the time that the site zero TLD is placed in the shield and removing the TLDs as close as possible to the time when the site zero TLD is removed-from the shield. Handle all TLDs in the same manner. This again assures the validity of using a single intransit dose for all TLDs.

5.

Do not expose the TLDs to heat radioactive materials or x-rays.

Do not open the sealed polyethylene packets.

Page 25 of 30

t

/'

(_mJ Attachment J.

EP-IP-044 Revision 1 Page 60 of 65 APPENDI'X 12 DRINKING WATER, GRAB Rev 3

- Three (3) gallons to be collected Nov 80 Materials Needed Rev 3 1.

Two two gallon new polyethylene bottles with screw caps.

Nov 80 2.

Labels 3.

Marking pencil 4.

Sample receipt sheet Sampliaq Procedures 1.

Turn on the finished water tap - allow to run for three minutes.

(_)

2.

Rinse the sample bottles three times with the water to be sampled.

3.

Collect three gallons of the water sample in the sample bottles Rev 3 seal them>with screw caps.

Nov 80 4.

Put labels on the bottles that include the following information:

a.

Station number and sample code number b.

Type of sample c.

Date of sampling d.

Your name e.

Size of sample 5.

Log this information onto the sample receipt sheet provided.

Precautions 1.

Do not wear a tritium luminous dial watch, as it may contaminate the sample.

-a

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Page 26 of 30

s O

Attachment J '.

EP-IP-044 Revision 1 Page 61 of 65 APPENDIX 13 SS-PWT-12H2 DRINKING WATER, MONTHLY COMPOSITE Rev 3. - Three hundred milliliters to be collected daily

/'

No'v 80 '

Materials Needed Rev 3 1.

Two two gallon new polyethylene bottles.with screw caps Nov 80 2.

Labels 3.

Marking pencils 4.

Sample receipt sheet 5.

100 m1 sampling bottle Samoling Procedures t]

1.

Turn on the finish water tap - allow to run for three minutes.

2.

Rinse the 100 mi sample bottle three times with water to be sampled.

3.

Fill the bottle with the sample and pour into a two gallon composite bottle. Repeat twice.

Rev 3 4.

Reseal the two gallon composite bottle. When the first two-Nov 80 gallon bottle is filled, fill the second bottle.

l

-5.

When 30 daily samples have been collected, replace the current l

sample container with a new empty container.

i 6.

Put labels on the composite bottles that includes the following information:

I a.

Station number and sample code number b.

Type of samp'.e c.

Dates of sampling d.

Your name e.

Size of sample 7.

Log this information onto the sample receipt sheet provided.

Page 27 of 30 i

O)

(

Attachment J.

EP-IP-044 Revision 1 Page 62 of 65 Precautions 1.

Do not wear a tritium luminous dial watch, as it may contaminate the sample.

NOTES: 1)

Procedures 1 to 5 may be performed by treatment plant personnel.

O v

Page 28 of 30

Attachment J.

EP-IP-044 Revision 1 Page 63 of 65 APPENDIX 14 MEAT, POULTRY AND GAME

- Five pounds of edible portion to be collected.

Materials Needed' 1.

Large plastic jar or bag and tape to seal.

2.

Labels.

3.

Marking pencil.

4.

Sample receipt sheet.

5.

Appropriate collecting license (for game).

Samoling Procedures 1.

Meat and poultry may be purchased from local suppliers.

Poultry

'(q-should be cleaned and dressed. Edible portions only of large animals should be sent.

~j 2.

Game may be trapped or shot if the appropriate collecting permit or license has been obtained.

3.

Small game should be cleaned and dressed. Edible portions only of large game should be sent.

In the case of large animals (e.g. deer) a portion of a road-kill secured from local game wardens is satisfactory.

4.

Collect enough edible portion of sample to equal five pounds and place in a plastic bag. Seal it with tape.

5.

Label the bag with the following information:

~

i li a.

Station number and sample code number.

l b.

Type of sample.

I c.

Date of sampling.

d.

Your name.

I e.

Size of sample.

6.

Log this information onto the sample receipt sheet provided.

7.

Freeze the sample and ship packed in ice or freezer packs.

l Precautions 1.

Take extreme caution not to contaminate the sample with soil.

y Page 29 of 30

Attachment J.

O EP-IP-044 Revision 1 Page 64 of 65 APPENDIX 15 If 2 gallons are not d

Precipitation - 2 gallons per station to be collecte.available, the Materials NeededNew two-gallon polyethyl_ene bottle with screw top

~

~

1.

2.

Labels Marking pencil 3.

Sample receipt sheet 4.

5.

Squeeze bottle i ing of Samoling Procedure Thoroughly shake the sample collection jug to assure m x le is available.

sample. Rinse the sample bottle if sufficient samp 1.

l with Empty contents of sample into the sample bottle an 2.

a screw top.

g 2-gallon sample bettle.

d sample collection Af ter emptying contents, rinse collection pan an Discard rinse.

Rev 2 3.

tub with distilled water.

f ation:

Put a label on the bottle and give the following in orm Aug 80 4.

Station number and station code number a.

Type of sample b.

Date and time of sample c.

d.

Your name Sample volume e.

Log this information onto the sample receipt sheet.

5.

Precautions Do not wear a tritium luminous dial watch as this may 1.

contaminate the sample.

Be careful, do not spill any sample.

2.

Page 30 of'30 g'

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