ML18142A335: Difference between revisions
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B. Objectives and Overview of the Surry Power Station Monitoring Program United States Nuclear Regulatory Commission (NRC) regulations (10 CFR r**-* | B. Objectives and Overview of the Surry Power Station Monitoring Program United States Nuclear Regulatory Commission (NRC) regulations (10 CFR r**-* | ||
50.34) require thai nuclear power plants be de~igned, constructed, and I | 50.34) require thai nuclear power plants be de~igned, constructed, and I | ||
i operated to keep levels of radioactive material in effluents to unrestricted areas as low as reasonably achievable (ALARA). To ensure that these criteria are met, the operating license for Surry Power | i operated to keep levels of radioactive material in effluents to unrestricted areas as low as reasonably achievable (ALARA). To ensure that these criteria are met, the operating license for Surry Power Station includes Technical* Specifications ~hich govern the release of I. ' | ||
Station includes Technical* Specifications ~hich govern the release of I. ' | |||
radi cacti ve effluents | radi cacti ve effluents | ||
* I .., In-plant monitoring is used to ensure that these predetermined release limits are not exceeded. However, as a precaution against unexpected and undefined processes which might allow undue accumulation of radioactivity in any sector of the human environment, a program for monitoring the plant environs is also included. | * I .., In-plant monitoring is used to ensure that these predetermined release limits are not exceeded. However, as a precaution against unexpected and undefined processes which might allow undue accumulation of radioactivity in any sector of the human environment, a program for monitoring the plant environs is also included. | ||
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* j i; | * j i; | ||
I , | I , | ||
. TABLE 1 (Page 4 of 4) | . TABLE 1 (Page 4 of 4) l SAMPLING PROGRAM L__ J Media Sampling Location Collection Frequency | ||
l SAMPLING PROGRAM L__ J Media Sampling Location Collection Frequency | |||
[__J Thermoluminescent Dow (DOW) (34) quarterly Dosimetry Lee Ha 11 (LEE HALL) ( 35 )° (continued) Goose Island (GI) (36) | [__J Thermoluminescent Dow (DOW) (34) quarterly Dosimetry Lee Ha 11 (LEE HALL) ( 35 )° (continued) Goose Island (GI) (36) | ||
Fort Eustis (FE) (37) | Fort Eustis (FE) (37) | ||
| Line 320: | Line 314: | ||
I , | I , | ||
L:~ | L:~ | ||
I' LAND BASED SAMPLES 8 | I' LAND BASED SAMPLES 8 | ||
| Line 463: | Line 456: | ||
i . 15 LJ | i . 15 LJ | ||
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| Line 645: | Line 637: | ||
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| Line 721: | Line 712: | ||
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---*f **-***-- . | ---*f **-***-- . | ||
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| Line 741: | Line 731: | ||
u June LEE HALL 06/01/83 LT 0.2 EPPS 06/01/83 LT 0.3 n CP 06/14/83 LT 0.3 LJ WMS JDKs 06/23/83 06/14/83 LT LT 0.6 0.,2. | u June LEE HALL 06/01/83 LT 0.2 EPPS 06/01/83 LT 0.3 n CP 06/14/83 LT 0.3 LJ WMS JDKs 06/23/83 06/14/83 LT LT 0.6 0.,2. | ||
~: **; | ~: **; | ||
'L__ | 'L__ | ||
Note: See footnotes at end of table. | Note: See footnotes at end of table. | ||
| Line 770: | Line 759: | ||
I,: | I,: | ||
~ ... WMS 12/20/83 LT o. 7 JDKs 12/16/83 LT 0.3 c: ~ | ~ ... WMS 12/20/83 LT o. 7 JDKs 12/16/83 LT 0.3 c: ~ | ||
; 4 LT = Less Than L, | ; 4 LT = Less Than L, | ||
(1) | (1) | ||
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1... J 1*, ! / Table 9 | 1... J 1*, ! / Table 9 | ||
\ .. | \ .. | ||
L_.*.a | L_.*.a (Page 2 of 3) | ||
(Page 2 of 3) | |||
* u Calcium in Milk VEPCO REMP - 1983 (Results in mg/1) | * u Calcium in Milk VEPCO REMP - 1983 (Results in mg/1) | ||
Sampling Calcium Month Location Date Concentration June LEE HALL 06/01/83 1200 r--- | Sampling Calcium Month Location Date Concentration June LEE HALL 06/01/83 1200 r--- | ||
| Line 912: | Line 895: | ||
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l( | l( | ||
| Line 1,162: | Line 1,144: | ||
Surry Dis. 09/27/8) LT 190 (3) LT 5 LT 3 LT 3 LT 3 LT 15 LT llO()) | Surry Dis. 09/27/8) LT 190 (3) LT 5 LT 3 LT 3 LT 3 LT 15 LT llO()) | ||
3 LT 3 LT 5 LT 7 LT 8 ND c. | 3 LT 3 LT 5 LT 7 LT 8 ND c. | ||
September Seo t land Wh. 10/18/83 LT 2'00 (3 ) LT 8 LT 4 LT 4 LT 3 LT 30 LT 120< > LT 4 LT 9 LT 11 LT 17 ND j?i Surry Dis. 10/18/83 LT 1200(3) 'LT 11 100< 3> | September Seo t land Wh. 10/18/83 LT 2'00 (3 ) LT 8 LT 4 LT 4 LT 3 LT 30 LT 120< > LT 4 LT 9 LT 11 LT 17 ND j?i Surry Dis. 10/18/83 LT 1200(3) 'LT 11 100< 3> | ||
LT 6 LT 5 LT 5 LT 40 LT LT 6 LT 12 LT 14 LT 20 ND October Scotland Wh. 11/22/83 3 | LT 6 LT 5 LT 5 LT 40 LT LT 6 LT 12 LT 14 LT 20 ND October Scotland Wh. 11/22/83 3 | ||
| Line 1,173: | Line 1,154: | ||
[..i'*: | [..i'*: | ||
November Scotland Wh. 11 /30/83 LT 60(3) LT 3 LT 2 LT *2 LT 2 LT 8 LT 30( 3 ) LT 2 LT 3 LT 6 I.T 6 ND i Surry Dis. l l /30/83 LT 10< 3 ) LT 3 3.8 + 1.3 LT 1. 9 2.6 + 0.9 LT 7 LT 40(3) 1:r 1. 7 LT 3 LT 4 LT 5 ND v* | November Scotland Wh. 11 /30/83 LT 60(3) LT 3 LT 2 LT *2 LT 2 LT 8 LT 30( 3 ) LT 2 LT 3 LT 6 I.T 6 ND i Surry Dis. l l /30/83 LT 10< 3 ) LT 3 3.8 + 1.3 LT 1. 9 2.6 + 0.9 LT 7 LT 40(3) 1:r 1. 7 LT 3 LT 4 LT 5 ND v* | ||
t*. | t*. | ||
December Scotland Wh. 12/31 /83 LT 30 LT 3 LT 2 J.T 2 LT 2 I.T 7. LT 15 LT 2 LT 3 LT 5 LT S ND f'*.*:1*; | December Scotland Wh. 12/31 /83 LT 30 LT 3 LT 2 J.T 2 LT 2 I.T 7. LT 15 LT 2 LT 3 LT 5 LT S ND f'*.*:1*; | ||
| Line 1,218: | Line 1,198: | ||
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| Line 1,307: | Line 1,286: | ||
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| Line 1,424: | Line 1,402: | ||
1, u | 1, u | ||
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| Line 1,467: | Line 1,444: | ||
51 I-, | 51 I-, | ||
. - - ~ - - - - . - - - . . - - * . * - - - ~ ~ - .... '* .-- : ~ ,* ,_*,.:**** *....,. .:r, ~ , . .- .... -:*.~'.*, *;,*.,-... *::. ~ .. ,~~::0.. -**:;:, *.,, -,-., . - -.- - -* **. : # --::----:::--=-~-.-;'- . -..---::--* .~ | . - - ~ - - - - . - - - . . - - * . * - - - ~ ~ - .... '* .-- : ~ ,* ,_*,.:**** *....,. .:r, ~ , . .- .... -:*.~'.*, *;,*.,-... *::. ~ .. ,~~::0.. -**:;:, *.,, -,-., . - -.- - -* **. : # --::----:::--=-~-.-;'- . -..---::--* .~ | ||
* F; | * F; Table 23 Strontium-89 and Strontium-90 in Vegetation VEPCO REMP 1983 (Results in Units of pCi/kg (wet)+ 2s) u r:'"! | ||
Table 23 Strontium-89 and Strontium-90 in Vegetation VEPCO REMP 1983 (Results in Units of pCi/kg (wet)+ 2s) u r:'"! | |||
Sample Sampling Location Type Date Strontium-89 Strontium-90 Carter's Cabbage 07/12/83 (1) (1) r | Sample Sampling Location Type Date Strontium-89 Strontium-90 Carter's Cabbage 07/12/83 (1) (1) r | ||
,,i __: | ,,i __: | ||
| Line 1,619: | Line 1,594: | ||
r **~-. | r **~-. | ||
I;., | I;., | ||
*~--- | *~--- | ||
56 | 56 | ||
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Name of Facility: SURRY Nuclear Power Station Docket Nos. 5-280; 50-281 Location of Facility: SURRY County, Virginia Reporting Period: 10 January - 31 December 1983 Medium or | Name of Facility: SURRY Nuclear Power Station Docket Nos. 5-280; 50-281 Location of Facility: SURRY County, Virginia Reporting Period: 10 January - 31 December 1983 Medium or | ||
/ Pa tllway Type and Location with Highest Annual Mean I Sampled Total Number Lower All Indicator Control LocaH?ns Mean (f) ( 2 ) | / Pa tllway Type and Location with Highest Annual Mean I Sampled Total Number Lower All Indicator Control LocaH?ns Mean (f) ( 2 ) | ||
*l (Units of of Analyses Limit of (1 l Locations Name, Di stance Mean (fl | *l (Units of of Analyses Limit of (1 l Locations Name, Di stance Mean (fl | ||
} | } | ||
| Line 1,768: | Line 1,741: | ||
J K-40 14000 (10/10) POS 17000 ( 2 /2) 17000 (1/1) | J K-40 14000 (10/10) POS 17000 ( 2 /2) 17000 (1/1) | ||
-'j (3000-17000) (17000-17000) (,17000-17000) | -'j (3000-17000) (17000-17000) (,17000-17000) | ||
.J J i | .J J i 11 | ||
11 | |||
.,:i NOTE: See footnote at end of table * | .,:i NOTE: See footnote at end of table * | ||
.J | .J | ||
Revision as of 04:03, 23 February 2020
| ML18142A335 | |
| Person / Time | |
|---|---|
| Site: | Surry |
| Issue date: | 01/31/1984 |
| From: | Grover J, Robison M NUS CORP. |
| To: | |
| Shared Package | |
| ML18142A334 | List: |
| References | |
| NUS-4503, NUDOCS 8504100625 | |
| Download: ML18142A335 (71) | |
Text
NUS - 4503 SURRY POWER STATION OPERATIONAL RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Annua 1 Re port 1983 Prepared for Virginia Electric Power Company by Mary S. Robison January 1984 Environmental Services Division NUS Corpora ti on 5350 Campbells Run Raad Pittsburgh, Pennsylvania 15~05 Approved: On:M. /1, ~&+:,,1,,/'
7 .
Joan M. Grover, Manager Radiological Laboratory 8504100625 ~iggg~80
~DR ADOCK PDR
OPERATIONAL RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Annua 1 Re !=)Ort 1983 Prepared for Virginia Electric Power Company
1--*-* -=* **----**>>*--*--*--* -----~*-*--**~.~-**,-*' .,._,,./-.. :.,i,* -- **---**. *0c-,--*-~* ... *. -*** ,*' ,,..'*.,.*s .........."'***-*, ........ ****-* *.' - - - - - * * - * - - - - * - - * * * **-*-**-**
- ~ -- Ii<*
f'.'
rl .:!
TABLE OF CONTENTS i
i l .: Section Title r*--
1 '
I I.*
I. INTRODUCTION 1 f] I I. SAMP~ING PROGRAM 3 I I I. ANALYTICAL PROGRAM 11 IV.
SUMMARY
AND DISCUSSION OF 1983 ANALYTICAL RESULTS 15 A. Air Iodine/Air Particulates 15 I:
I.-*
B. Milk 25 1~-.
I ' C. Pree i pita ti on 35 U* .
D. Water 35
[ E. Aquatic Biota 39 F. Sediment 45
[--~
G. \-Ja ter Fowl 45
(
\
H. Food Products 50 I*
I. Soi 1 50 J. Direct Radiation 54 V. CONCLUSIONS 64
,*-*,j l, A~PENDIX A REPORTING OF ANALYTICAL RESULTS i
l~
APPENDIX B ANALYTICAL PROCEDURES APPENDIX C LABORATORY QUALITY ASSURANCE I' i
.:-;**----~- --~-.--
<* *: *; "* *.:,*. ~h':, :.:.~:,'* '
-~.
.:,,-.,24_ .. ~ .... ~-~-* 0"*4*---"~-.: *.*'--*.. --***-*-- . _ _ _ * *"" * * .* "", * ***
- -- --*-*---*-*~ .. --.-**-... 4*0 -*-.. ',...,,,_ * ~0,....s::z** ..: _ * - M - ~ "* .*.. *_* -~* *; C*-" __ . * " - - ~ - * * *-* ',
- __ ,_;. : .:*..*
lJ
( :
l ..J LIST OF TABLES Table Ti _tl e 1 Sampling Program 4 2 Analytical Program 12 3 Iodine-131 in Charcoal Cartridges 16 n
i_.__i 4 Gross Alpha on Air Particulate Filters 18 5 Gross Beta on Air Particulate Filters 21 l;
' ! 6 Gamma Spectrometry of Composited
~ *..J Air Particulate Filters 24
\ __\ 7 Iodine-131 in Milk 26
,---, 8 ~amma Spectrometry of Milk 28 l
i i
'i I '
9 Calcium in Milk 30 10 Strontium-89 and Strontium-90 in Milk 33 11 Gross Beta and Tritium in Precipitation Monthly and Quarterly Composites 36 11 \
12 Determination of Gross Alpha, Gross Beta, and Tritium in I-later, Semi-Annual Samples 37 l '
\ .:....... 13 Gamma Spectrometry of River Water 38 14 Determination of Tritium in Water I : Semi-Annual Composites 40 r*, 15 Gamma Spectrometry of River Water I
I
- , Monthly Composites 41
\ . ...I 16 Strontium-89 and Strontium-90 in Water 42
[*1 i :
I
-~ 17 Gamma Spectrometry of Clams and Oysters 43 i i 18 Gamma Spectrometry of Crabs 46 u 19 Gamma Spectrometry of Fish 47 ii
. ~I
. . . . .. - .. . . - .. :*... * . ---. .... ., .. ,.. - *. *: . . . . . -* ..... --~~_:__.:~:~ .'~* :_.* - , .. - . *. .** .. **- . . . *.-. .
r1
- L:<
-*~ 1 I :
LIST OF TABLES (continued)
\* .
Table Title i*
20 Gamma Spectrometry of Sediment 48 21 Gamma Spectrometry of Fowl 49 22 Gamma Spe_ctrometry of Vegetation 51 23 Strontium-89 and Strontium-90 in Vegetation 52 24 Gamma Spectrometry of Soil 53
',.--. 25 Direct Radiation-Thermoluminescent Dosimetry 55
!L..;i 26 Summary of Data for the Surry NPS r**1 Radiological Environmental Monitoring I -:i' Program.- 1983 57 l ,.J u
r*, (
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u
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iii
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r-: LIST OF FIGURES i '
i .'
Figure Title 1 Land Based Sampling Locations 2 River Based Sampling Locations 9 3 Site Boundary TLD Locations 10 C
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I. INTRODUCTION This document reports on the operational radiological environmental monitoring program conducted during 1983 for the Surry Power Station.
r*- The analytical portion of this program was conducted by NUS Corporation
'. (NUS) under contract to the Virginia Electric Power Company. This
- __ ,'. annual report of the radiological environmental monitoring program s*ummari zes
- the results of measurements and analyses of data obtained from samples collected during the reporting period.
A. Site and Station Description
,i.........; The Surry Power Station of Virginia Electric Power Company consists of two Westinghouse pressurized water reactors, each with a generating capacity of 788 MHe. Unit 1 has been in operation since July 1, 1972*,
Unit 2 since March 7,1973. The station is located on a peninsula in the James River, approximately 25 miles upstream of Chesapeake Bay. Cooling water is taken in downstream of the site and discharged 5.7 miles i ; upstream of the intake.
l *'
B. Objectives and Overview of the Surry Power Station Monitoring Program United States Nuclear Regulatory Commission (NRC) regulations (10 CFR r**-*
50.34) require thai nuclear power plants be de~igned, constructed, and I
i operated to keep levels of radioactive material in effluents to unrestricted areas as low as reasonably achievable (ALARA). To ensure that these criteria are met, the operating license for Surry Power Station includes Technical* Specifications ~hich govern the release of I. '
radi cacti ve effluents
- I .., In-plant monitoring is used to ensure that these predetermined release limits are not exceeded. However, as a precaution against unexpected and undefined processes which might allow undue accumulation of radioactivity in any sector of the human environment, a program for monitoring the plant environs is also included.
Various environmenta.l samples are collected at indicator and *control or background 1oca tions and analyzed to determine if changes *in radioactivity levels may be attributable to the operation of the station. Measured values are compared with background l~vels. The background levels at ~ny one location are not const~nt, but vary with.
time due to external events such as cosmic ray bombardment, weapons test fallout, an~ seasonal variations. These levels also vary spatially within relatively short distances as a reflection of geological
- .-
- * composition. Data collected prior to plant operation are used to
\
indicate the degree of natural variation to be expected. These preoperational data are compared with data collected during the
,,,. operational phase to assist in evaluating the radiological impact of plant operation.
1
. . .'., . . ..., .. -. *- .. ,- .' ...... ,. . . . . . *. . .. : ; "'*.* - . ~-. ~ . .* ~ .-, . . . _,.,__ . . ..
.* *,: __:~
d The objectives of an operational radiological environmental monitoring program are:
l .*
o To fulfill the obligations of the Surry Power Station Technical Specifications;
/ .
t *-*
o To determine whether any* statistically significant increase occurs in the concentration of radionuclides in any critical pa th; o To detect any buildup of long-lived radionuclides in the en vi ronmen t; o To verify that radioactive releases are within allowable limits and that plant operations have no detrimental effects on the health and safety of the public or on the environment;
, .... o And, to establish measurement and assessment methods capable of l
l
- rapid mobilization during unplanned releases and emergencies.
I __ l In 1983 the radiological monitoring program included the mea~urement of ambient gamma radiation by thermoluminescent dosimetry; the determination of gross alpha, gross beta, and gamma emitters in air particulates; the measurement of airborne I-131 in charcoal cartridges; the determination of gamma emitters in river bottom sediment, fish, crabs, clams, and oysters; the measurement of gamma emitters, tritium, and strontium-89 and -90 in river water; the determination of gross a 1pha and beta . and tritium in we 11 water, surface water; the determination of gross beta and tritium in precipitation; the determination of gamma emitters, iodine-131, calcium and strontium-89 and -90 in milk; the measurement of gamma emitters and strontium-89 and
-90 in food crops; and the determination of gamma emitters in soil and waterfowl.
2 r *.,
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~
- --:-*--~,- ____:c.a*::,..c~,...,,,...L,,c_..:.,,,,:-_,;,c"*'.:.,.a'.:,,c::,:,:;*;,~.:i,:;<;,:;;:.\,>;c f-,,
I( __j;
- II. SAMPLING PROGRAM L:'. Table 1 summarizes the sampling program for Surry Power Station during 1983. The symbols on this table refer to the sample locations shown on Figures 1 to 3. Figure 1 shows the locations of land based sampling in the environs of the station, while Figure 2 shows the locations of river based sampling stations. The small triangles in Figure 3 indicate the positions of environmental thermoluminescent dosimeters (TLDs) at the site boundary.
Samples are collected by VEPCO personnel except for those 1i sted as state splits, which are collected by the Commonwealth_of Virginia. All samples are shipped to the NUS Radiological Laboratory in Pittsburgh, Pennsylvania.
A. Program Exceptions No air*samples were collected from station FE for the week of 09/06/83-09/14/83 due to pump failure. No air particulate filter was collected from station SS for the week of 07/26/83-08/02/83.
T~e I-131 analysis on the milk sample from station LEE HALL for the
. month of December was lost due to a broken container. The milk sample from station WMS for the month of June was lost during ashing in r~- preparation for gamma spectrometry, due to a furnace malfunction. The stronti.um-89, -90 analysis on this sample was also lost, as well as the L..; strontium-89, -90 analysis on the sample from this station for the month r-**~
of May. The milk sample from station JDKs for the month of September i : was depleted in other analyses and no gamma spectrometry could be I ,
-performed.
Values for five quarterly TLD measurements are not reported. Three were missing at the time of pickup. These were the second quarter TLDs for location 04 and the fourth quarter TLDs for locations 07 and 08. Two additional fourth quarter TLD locations, 14 and 15, were not recorded as I
missin~ at the time of pickup, but were not received for analysis by the I _c laboratory.
3
TABLE 1 (Page 1 of 4)
SAMPLING PROGRAM l ; Media Sampling Location Collection Frequency L ,.
Air Particulates Surry Station (SS) weekly and Hog Island Reserve (HIR)
Charcoal Cartridges Bacon's Castle (BC)
A11 i ance (ALL)
D Colonial Parkway (CP)
Dow Chemi ca 1 (DOW)
Fort Eustis (FE)
Newport News (NN)
Milk Lee Hall (Ross) Dairy (LEE HALL)(l) ~onthly Epps Dairy (EPPS ) (1 )
Colonial. Parkway (Smith) Dairy (CP)
Judkins Dairy (JDKs)
William's Dairy (WMS)
Precipitation Surry Station (SS) monthly and
('" quarterly composites i Newport News (NN)
L__j CV Well Water Surry Sta ti on (SS) semi-annually Hog Island Reserve (HIR)
Bacon's Castle (BC)
Jamestown (JMTN)
L Surface Water Chippokes Creek (CC) semi-annually Williamsburg, Waller Mill Reservoir (WMR) r*1 Newport News Reservoir (NNR)
Smithfield Reservoir (SR)
River Water Surry Station Intake (SI) bi-monthly Hog Island Point (HIP)
Newport News (NN)
Chicahominy River (CHIC)
Surry Station Discharge (SD)
Surry Station Discharge (SD)(l) monthly composites Scotland Wharf (S. WHARF)(l)
Note: See footnote at end of table.
4
...__J
..... * .. * .*. . - . ._... ,' .* ~~----~~- .... ~ .
. ~ . '_ : *::__* ..
{,* -.L i *]
l.i TABLE 1 (Page 2 of 4)
SAMPLING PROGRAM Media Sampling Location Collection Frequency Sediment (Si.l t) Chicahominy River (CHIC) semi-annually Surry Sta ti on Intake (SI) r**, @ Surry Station Discharge (SD)
I :
I*-,
Hog Island Point (HIP)
\.._...:
Point of Shoals (POS)
Newport News (NN)
'- r-~
I .'
u Clams Chicahominy River (CHIC) bi-monthly Surry Station Discharge (SD)
© Hog Island Point (HIP)
Jamestown (JMTN)
Lawnes Creek (LC).
I; Oysters Deep Water Shoals (DWS) bi-monthly Point of S-hoa 1s (POS)
- Newport News (NN)
Crabs Surry Station Discharge (SD) July-August-September Fish (catfish, eel) Surry Sta ti on Discharge (SD) semi--annua l ly I
i '
0Fowl Hog Island Reserve (HIR) semi-annually I '
- ~*-*,;
Crops Slade's Farm (Slade's) annually (corn, peanuts, Brock's Farm (Brock's) soybeans, cabbage) Carter's Grove Garden (Carter's)
Poole Home Garden (Poole)
Soil Surry Station (SS) annually
- Bacon's Castle (BC)
A11 i ance (ALL)
- Colonial Parkway (CP)
Dow Chemi ca 1 (DOH)
Fort Eustis (FE)
Note: See footnote at end of tab.le.
5
- * . * . . ' . *-.. .** .... ~- '< .* *-,.-~. - .. - .* * .* . --.:. :, .*.*:,,**' .*
.~
u I *.
n*
I:
l_
- TABLE 1 (Page 3 of 4) r.
I . SAMPLING PROGRAM Media Sampling Location Collection Frequency Thermoluminescent Control (CONTROL) (00) quarterly Dosimetry Surry Station (SS) (01)
West North West (WNW) (02) 6 Station Discharge (SD) (03)
North North West (NNW) (04)
Nor th (N) (0 5 )
r**~
I
- I . North North East (NNE) (06)
LJ North Ea st (NE) (07)
East North East (ENE) (08)
I
- East (exclusion) (EE) (09)
I I. -
West (W) (10)
West South West (WSW) (11) r, South West (SW) (12)
I' .I South South West (SSW) (13)
Sou th (S ) (14)
South South East (15)
South East (16)
East (E) (17)
Sta ti on Intake (SI) (18)
Hog Island Reserve (HIR) (19)
Bacon's Castle (BC) (20)
Route 633 (RT 633) (21)
Alliance (ALL) (22)
L_; Surry (SURRY) (23)
Route 636 & 637 (636/637) (24)
Scotland Wharf (S.~HARF) (25)
[J Jamestown (JMTN)
- Colonial Parkway (CP)
(26)
(27)
Route 617 & 618 (617/618) (28)
Kingsmill (KM) (29)
Williamsburg (WMBG) (30)
Kingsmill North (KMN) (31)
Budweiser (BUD) (32)
Water Plant (WP) (33) r-.
I.
i Note: See footnote at end of table.
6
. ; ,, - **. :* *.* :* .. :- . - - - .. .. . . . . . -*' :_*_.:: :_:* ___._:...:~_ . >:-". ':,~-~- ~ ~-* .. -:..,.;*::_.... *-* ..**--.*
- a:,
- j i;
I ,
. TABLE 1 (Page 4 of 4) l SAMPLING PROGRAM L__ J Media Sampling Location Collection Frequency
[__J Thermoluminescent Dow (DOW) (34) quarterly Dosimetry Lee Ha 11 (LEE HALL) ( 35 )° (continued) Goose Island (GI) (36)
Fort Eustis (FE) (37)
Newport News (NN) (38)
James River Bridge (JRB) (39) Control Benn's Church (BENN'S) (40) Control Smithfield (SMFD) (41)
Rushmere (RUSHMERE) (42)
Route 628 (RT 628) (43)
[ ;
,.~
i\_;;
(1 ) Sta te s pl i t 7
' ' .*'. ~ .<.:_~. . -
r-:-:
f :
l_. __ :
r-;
'I I.*
I ___ ;
r:":"i I '
I II ** :
- .:in..,
l r::
I -1:
L ..)
[J f:
L.:
I ,
L:~
I' LAND BASED SAMPLES 8
--..'\
. ,I
\ J L.
r**
l.1 r**
l~
r ---~
1; L__.
l __ ...,
1*
SAMPLES
~- . *-* --;-**....., . . *_,-::-;-----:-*~.-=.: .. -* - .. _.--, .* *.:-:~:-~,-~.;-*_--:::-......----:----,----~-----:--*- ----=~*--,,-;~;-~-:::---r---:-:*-:---::---:*:..__~_-;-:--::-.....-.--.--,..--:---- - . -. ----*-***
[' :* + + . *!*
r~
i*:+
1.... ,
r-*-
i L__ ;
[
+
[J
+
i i i
t .
,_j r*,
I:
i L
Figure 3
- - SITE BOTJNDRY TLD
/ +.
10
- .**------ -~---~.
- ** ---.-**- :' *--~--- -~* ------ *-----*----~-"'--%
~ . -~. **'*°'*-***-->-*-- * . __ .* *' * -* ~-~-*-~~-- *** *....,.* * * ,.- ....... *~:s:d:*=~-~~- ~~;, ,*~*-,.-'< ,* .....~ ... 4*<**" *. ' * ~ . *'-' : -~' *-* * * . *"_:,,~.-.:,__:_,A_...,_.:___.__..~----*-~~-*
III. ANALYTICAL PROGRAM Table 2 summarizes the analytical program for Surry Power Station during 1983. Sample c*lass, frequency, an<;! type of analysis performed are
~- 1i sted. The analytical methods used are described in detafl in Appendix I' , C.
L *"
Air iodine and air *~articulate samples were collected from seven indicator and one control location on a weekly basis. Air iodine was lJ collected by drawing air through TEDA impregnated charcoal cartridges.
Air particulates were collected by drawing air though a 47-millimeter 1; diameter glass-fiber filter. In the laboratory, air par~iculate filters were analyzed for gross alpha and gross beta activity, and were L: composited quarterly for analysis by gamma spectrometry. Charcoal cartridges were analyzed for iodine-131.
[ Milk was collected from one control and four indicator locations on a monthly basis. Samples from the LEE HALL and EPPS locations were collected by and split with the Commonwealth of Virginia. All milk samples were analyzed for iodine-131, gamma emitters, stable calcium, and strontium-89 and -90.
r*:
I '
Precipitation samples were collected as monthly and quarterly composites L..: from one control and one indicator location. Gross beta and tritium analyses were performed on both types of composites.
water samples in.eluded well water, surface water and river water.
Well water was sampled from four locations on a semi-annual basis ..
Gross alpha, gross beta, and tritium analyses were performed on these samples.
Surface water was sampled from four locations on a semi-annual basis.
Gross alpha, gross beta, and tritium analyses were performed on these samples.
Two types of river water samples were collected. Monthly composites were taken from one control location upstream of the plant and an indicator station at the plant discharge location. These composite samples were collected by and split with the Commonwealth of Virginia; they were analyzed for gamma emitters and strontium-89 and -90.
Bi-monthly river water samples were also collected from one control and four indicator locations. These were analyzed by gamma spectrometry on a bi-monthly basis and composited for semi-annual analysis of tritium.
The James River is an estuary near Surry Power Station, and tidal exchange of water with Chesapeake Bay occurs. River based samples include silt, crabs, fish, clams and oysters.
Crabs were taken from the plant discharge location during July, August and September only.* These samples were analyzed by gamma spectrometry.
11
- - -* -- . --- ' *--. *-* *-~ ' *. -* ..,,~ *.. *,* ..__ ._ ..._;; *. *--* ; **:.._: :, . *">*~:.;.':,._,:: :> ,* ~.:. ;--~-.~~.".: .'.- ****.!,... *** **:*.,*.,- ..**,,:* .-. : ..... * ... *-- :. ~ *.:. --v*. __ .,:..*;;,~*: __ ,.'* **..____ ,. ***-*---'"*-* -~-* *-~--:. - _*. ;* __ ' *. ,* -~- - ' . _,..___ ' .' :__
I.. ii,_
n u
,~
I*' TABLE 2 I~
(Page 1 of 2) r I__ ANALYTICAL PROGRAM
[ Sample Class Frequency Type of Analysis
[-: _j Air Particulate weekly Gross alpha and beta quarterly composite Gamma spectrometry
[J Air.borne Iodine weekly Iodine-131
[J Thermoluminescent quarterly Radiation dose Dosimetry* (TLD) 1*:
Milk monthly Iodine-131 Gamma spectrometry
[J Strontium-89, -90 Stable calcium r-:
l__ J Precipitation monthly Gross beta Tritium
- quarterly composite Gross beta C Tritium r**
i L..J Well water semi-annually Gross alpha and beta Tritium
[J Surface water semi-annually Gross alpha and beta r*--: Tritium I '
I
! i I :
River water bi-monthly Gamma spectrometry semi-annual composite Tritium D monthly composite Gamma spectrometry Strontium-89, -90 r*-1 L-1 r**:
I
~
i L-iLJ; 12
- - - * - - - - - . * - - . , * - : - ~ - - - - -.. - .._-------.-----..* ... *-..-...--*-'"<*--,--.--,.., __ .-_ . * ~. -- -~- ...... _ - - - . * - . - -..---..- .--:c*****-- .* .;--... ~- *~:c---r-......- ~ - . - - - - * -.* - .----;--......,-~*7'"".
r~.,
[J f'
I i I',__ _;i TABLE 2 r~ (Page 2 of 2)
II .'
i._ __
- ANALYTICAL PROGRAM Sample Class Frequency Type of Analysis
[J Silt semi-annually Gamma spectrometry Clams and Oysters bi-monthly Gamma spectrometry I)
LJ
~-
Crabs three summer months Gamma spectrometry Fish semi-annually Gamma spectrometry D Fowl annually Gamma spectrometry r-1 Crops annually Gamma spectrometry LJ Strontium-89, -90 Soil annually Gamma spectrometry i .;
I '
L..J r --~
r .
r *l
__J
'r
I 13
Two kinds of fish, eel and catfish, were collected semi-annually from the*plant discharge location for analysis by gamma spectrometry.
t.)
Clams were collected bi-monthly from one control and four indicator locations for analysis by gamma spectrometry. Oysters were also collected bi-monthly from three indicator locations for analysis by gamma spectrometry.
r-;.
!-.; .1 River bottom silt (sediment) was collected semi-annually from one l _:J control and four indicator locations for analysis by gamma spectrometry.
One waterfowl sample was analyzed by gamma spectrometry.
Seven samples of food crops were collected during 1983 for analysis of gamma emitters and strontium-89 and -90. These included cabbage, kale, corn, peanuts, and soybeans from four indicator locations.
Annual samples of soil were taken from six indicator locations near air samplers and analyzed by gamma spectrometry.
Thermoluminescent dosimeters (TLDs) were used to determine the direct r,
1*,; (ambient) radiation levels at monitoring points. For routine TLD
( .. ~.; measurements, a dosimeter of CaS04:oy*in a Teflon card wai deployed at each selected location. Dosimeters were exchanged on a quarterly basis.
Additional sets of dosimeters were shipped with each exchange cycle to serve as in-transit controls. For routine exchanges, TLDs were shipped by Federal Express. Individual dosimeters were calibrated by exposure to an accurately known radiation field from a calibrated Cs-137 source.
~'*.*.
l '
LJ ll U*
[1 lJ 14
- .. -, *-**,-. ----- - ... - * - - - .. --*--- -.*-*-....,---* *.. ' *. *._::-;--.... .,"" .... *.*.. -~. * . . :. c-.-. -. .*.. -** ,-. .-*-*--:-- ** . --..:--...... _.*--. .. , ... *.- . . ~-.- - .* '72 ...... -- .* -_ .......... ~ . - - : : - . . _ , _ .
...**. * - .* - * .* , '
- S c ~ ... ** '* . *-~- * *.*.*.* , __ ,.:.__ __ ,._:._ ___ ,.o.i"'---**~---~*..:,.-=.C.O.o,c:-'--'*"**.,_;__,,,"",*'*"-'-*~COC"'-"'--"--'-"':*,*~--*':
nI i r1*:J :
IV.
SUMMARY
AND DISCUSSION OF 1983 ANALYTICAL RESULTS Data from the radiological analyses of environmental media collected during the report period are tabulated a~d discussed below. The procedures and specifications followed in the laboratory for these analyses are as required in Section 5.0 of the NUS Environmental Services Division Quality Assurance Manual, and are detailed in the NUS
,-, Radiological Laboratory Work Instructions.
[-l Radiological analyses of environmental media characteristically approach and frequently fall below the detection limits of state-of-the-art measurement methods. (1) The use of 11 LT 11 in the data tab-les is the equivalent of the less than symbol (<) and is consistent with the NUS Radiological Laboratory practice of data reporting. The number following the 11 LT 11 is a result of the lower limit of detection (LLD) 11 calculation as defined in Appendix B. ND 11 (Not Detected) is used periodically in the tables presenting gamma analysis results for various media. It primarily appears under the "Others" column, where it I'°'. indicates that no other detectable gamma emitting nuclides were I
I identified. NUS analytical methods meet the LLD requirements addressed ,
in Table 2 of the USNRC. Branch Technical Position of Radiological Monitoring (November 1979, Revision 1). (2)
Tables 3 through 25 give the radioanalytical results for individual samples. A statistical summary of the results appears in Table 26. The reported averages are based only on concentrations above the limit of detection. In Table 26, the fraction (f) of the total number of analyses which were detectable follows in parentheses. Also given in n parentheses are the minimum and maximum values of detectable activity Ii during the report period.
A. Air Iodine/Air Particulates i
L.~ Results of airborne iodine-131 analyses on charcoal* cartridges are presented in Table 3. I-131 was not detected in any of the samples.
Results of gross alpha and gross beta analyses on air particulate filters are given in Tables 4 and 5. The mean gross alpha activity for all stations was 3.8 + 2.6 E-03 pCi/~3 and the range of gross alpha activity was 1.2 to 20 E-03 pCi/m T~e mean gross beta activity for a 11 stations was 16 + 19 E-03 p~i /m3 and the* range of gross beta r*~,
I i activity was 3.2 to 78 E-03 pCi/m.
I i L Air filters were composited quarterly and then analyzed by gamma spectrometry. The gamma spectrometry data is presented in Table 6.
1*: Cosmogenic beryllium-7 was detected in 2~ of 32 samples. The range of
[J Be-7 activity *was 32 to 110 E-03 pCi/m. Three samples for v1hich LLDs were measured also fell within this range. Cesium-134 and cesium-137
'r*-,. were found in the first and second quarterly composites from Surry i Station (SS). Both isotopes may be the result of plant effluents.* This station is located within the plant boundary and is not an environmental location. Cesium-137 was also detected at one environmental location in th~ third quarter. This isotope is occasionally found in air particulate composites and is considered to be a result of atmospheric r*r-,
weapons testing and global fallout.
'I .*
i . 15 LJ
----.-- -~------------.------~- ,,-- -- *,7-- --~-,--- --- - ----.----,""----~ ..-----" ...-.*,--------...-,--
r r--*
L. ,.L.... '
- ._J r.. ------,
L - ..
I
._j
.~.--1 L~.a.J -1
- I
.j I
,]
,*1
.. ,.. i-L*
.1*
i TABLE 3 !*'
- 1
.*I j (Page 1 of 2)
.l Iodine-131 in VEPCO Charcoal Cartridges REMP - 1983 ,.
l 1.*
i 3 I j (Results in pCi/m +/-_ *2s)
'-j 1-.*
i'!) Honth Collection Period ss IIIR BC ALL CP DOW FE NN
.I I
January 12/28/82 to 01/04/83 LT 0.02(1) LT 0.03 LT 0.03 LT 0.04 LT 0.019 LT 0.018 LT 0.02 LT 0,02
,:1 01/04/83 to 01/12/83 LT 0.03 LT 0.04 LT 0.03 LT 0.05 LT 0.03 LT 0.03 'LT 0.03 LT 0,04
- 1 01/12/83 to 01/18/83 LT 0.04 LT 0.04 LT 0.04 LT 0.07 LT 0.02 LT 0.02 LT 0.02 LT 0.02
)
- /
01/18/83 01/25/83 to to 01/25/83 02/02/63 LT LT 0.02 0.02 LT LT 0.015 0.02 LT
- LT 0.015 0.02 LT LT 0.02 0.03 LT LT 0.017 0.02 LT LT 0.017 0.02 LT LT 0.018 0,02 LT LT 0.019 0.03 i
.*! February 02/02/83 to 02/08/83 LT 0.016 LT 0.018 LT 0.018 LT 0.03 LT 0.02 LT 0.02 LT 0,02 LT 0.02
'.*,) 02/08/63 to 02/15/83 LT 0.06 LT 0.05 LT 0.04 LT 0.07 LT 0.019 LT 0.018 LT 0.018 LT 0.02 I 02/15/63 to 02/22/83 LT 0.04 LT 0.05 LT 0.05 LT 0.06 LT 0.02 LT 0.019 LT 0.02 LT 0.02 "i 02/22/63 to 03/02/63 LT 0.03 LT 0.04 LT 0.04 LT 0.05 LT 0.04 LT 0,03 LT 0.03 LT 0,04
) March 03/02/83 to 03/10/83 LT 0.03 LT 0.03 LT 0.03 LT 0.05 LT 0.03 LT 0.03 .LT 0.03 LT 0,03
. I, 03/10/63 03/16/llJ to to 03/16/83 03/23/83 LT LT 0.04 0.03 LT LT 0.04 0.03 LT LT 0.05 0.03 LT 0.07 LT 0.05 LT 0.04 LT 0.05 LT 0.04 LT 0.05 LT 0.03 LT 0,03 LT 0.03 LT 0.03 j 03/2 3/03 to 03/30/63 LT 0.018 LT 0.02 LT 0.02 LT 0.03 LT 0.02 LT 0.019 LT 0.02
- I LT 0.02
- i
.'i April 03/30/83 to 04/06/83 LT 0.03 LT 0.03 LT 0.03 LT 0.03 LT
- 0.05 LT 0.03 LT 0.03 LT 0,03 I 01, /06 /83 to 04/12/83 LT 0.03 LT 0.03 LT 0.03 LT 0.05 LT 0.03 LT 0.03 LT 0.03 LT 0.03
- 04/12/83 to 04/19/83 LT 0.03 LT 0.03 LT 0.03 LT 0.05 LT 0.018 LT 0.017 LT 0,018 LT 0.02 i 04/19/83 to 04/26/83
- LT 0.03 LT 0.03 LT 0.03 LT 0.05
.*! LT 0.04 LT 0.03 LT 0.03 LT 0,04 04 /26/83
.*1 to 05/03/83 LT 0.02 LT 0.02 LT 0.02 LT 0.04 LT 0.03 LT 0.02 I.T 0,02 LT 0.02
~
':i
,.I May 05/0.1/IJ) to 05/10/83 LT 0.03 LT 0.03 LT 0.03 LT 0.05. LT 0.04 LT 0.03 LT 0.03 LT 0.03 l 05/10/63 05/17/63 to 05/17/83 LT LT 0.04 LT 0.04 LT 0.04 LT 0.06 LT 0.04 LT 0.04 LT 0.04 LT 0.04
'.i to 05/24/83 0.018 LT 0.02 LT 0.02 LT 0.04 LT 0.02 LT 0.02 LT 0.02 LT 0.02
- J 05/24/83 to 06/01/83 LT 0.04 LT 0.04 LT 0.04 LT 0.07 LT 0.03 LT 0.03 LT 0.03 LT 0.03 i
,'j June 06/01/63 to 06/08/83 LT 0.03 LT 0.03 LT 0.03 LT 0.04 LT 0.03 LT 0.03 LT 0.03 LT 0.03
- l 06/06/63 to 06/14/63 LT 0.03 LT 0.03 LT 0.03 LT 0.06 LT 0.03 LT 0.03 LT 0.03 LT 0.03 I
- .i 06/14/83 to 06/22/83 LT 0.03 LT 0.03 LT 0.03 LT 0.04 LT 0.03 LT 0.03 LT 0.03 J,T 0.03
- i 06/22/13) to 06/28/83 LT 0.05 I.T 0.05 LT 0.05 LT 0.07 LT 0.07 LT 0.07 LT 0.06 LT 0.07 j July 06/26/83 to 07 /06/83 LT 0.03 LT 0.05 LT 0.04 LT 0.07 LT 0.06 LT 0.05 LT 0.05 LT 0.05
.J 07/06/83 to 07 /13/83 LT 0.04 LT 0.05 LT* 0.04 LT 0.06 LT 0.03 LT 0.05 LT 0.03 LT 0.03 J 07 /1 )/63 to 07/19/83 LT 0.03 LT 0.03 LT 0.03 LT 0.03 LT 0.03 LT 0.03 LT 0.02 LT 0,03 I .07/19/83 07 /26/83 to to 07 /26/83 08/02/83 LT LT 0.03 0.06 LT LT 0.04 0.07 LT LT 0.03 0.07 LT LT p.07 0.05 LT LT 0.04 0.05 LT LT 0.05 0.07 LT LT 0.06 0.05 LT LT 0,06 0,05 1
J Note: See footnote at end of ta~le.
1 I
I 1
l
1 *.,.., r-*.1 r-:--.
- t. ....... I 1-*-.~
- 1. __ * .,:.. .*.* J r..,.--,J 1..- ~--..... _* **
1::--1
.... ~.~-. -
- I t
TAHU: .'3 (Page 2 of 2) lod!ne-131 in Charcoal Cartridges VEPCO REMP - 1983 pCl/ra)
(Results in
-+ 2e)
Month Collect Lon PP.rlod ss IIIR nc ALL CP DOW FE NN August Ofl/02/111 to 06/09/63 LT 0.04 LT 0.05 LT 0.05 LT 0.04 LT 0.04 LT 0.05 LT 0.04 LT 0.04 06/09/83 to 08/17 /fl1 LT 0.017 LT 0.02 LT 0.02 LT 0.02 LT 0.03 LT 0.03 LT 0.03 LT 0.04 08/17 /83 to 08/23/83 LT 0.03 LT 0.03 LT 0.03 LT 0.03 l,T 0.05 LT 0.04 LT 0.04 LT 0.05 08/23/83 to 08/30/83 LT 0.03 LT 0.03 LT 0.03 'LT 0.03 LT 0.03 LT 0,03 LT 0.03 LT 0.03 September 08/30/83 to 09/06/83 LT 0.03 LT 0.03 LT 0.03 LT 0.04 LT 0.06 LT 0.04 LT 0.06 LT 0.06 09/06/83 to 09/14/83 LT 0.04 LT 0.04 LT 0.04 LT 0.04 LT 0.04 LT 0.05 (2) LT 0.05 09/14/83 to 09/20/83 LT 0.06 LT 0.05 LT 0.05 1,T 0.04 LT 0.06 LT 0.07 LT 0.06 LT 0.07 09/20/83 to 09/27 /83 LT 0.05 LT 0.05 LT 0.05 LT 0.04 LT 0.05 LT 0.05 LT 0.04 1,T 0.05 09/2 7 /83 to 09/27 /83(3) I.T 0.04 October 09 /2 7 /8 3 to 10/04/83 LT 0.05 LT 0.05 LT 0.05 LT 0.04 LT 0.05 LT 0.06 LT 0.05 LT 0.06 10/01, /8 3 to 10/11/83 LT 0.04 LT 0.04 LT 0.04 LT 0.04 LT 0.04 LT 0.04 LT 0.03 LT o.04 10/11/83 to 10/18/ll.1 LT 0.03 LT 0.04 LT 0.03 LT 0.04 LT 0.04 LT 0.04 LT 0.04 LT 0.04 10/18/83 to 10/26/83 LT 0.04 LT 0.04 LT 0.04 LT 0.04 LT 0.04 LT 0.04 LT 0.03 LT 0.04
- ,.:.]
- .: November 10/26/83 to 11/01/83 LT 0.06 LT 0.06 LT 0.06 LT 0.06 LT 0.05 LT 0.05 LT 0.04 LT 0.05 11/01/83 to 11/08/83 LT 0.03 LT O.OJ LT 0.03 LT 0.03 LT 0.04 LT 0.05 LT 0.04 LT 0.05 ll/08/83 to 11/15/83 LT 0.03 0.02 LT O.OJ l,T 0.03 LT 0.04 LT 0.04 LT 0.07. LT 0.03
.J.,
- .I l l/15/83 11/22/83 to to 11 /22/83 11/29/83 LT 0.03 0.02 LT l,T LT 0.03 0.03 LT LT 0.03 0.03 LT 0.03 0.03 LT LT 0.03 0.04 LT LT 0.03 0.04 LT LT 0.03 0.03 LT 0.04 0.04 LT LT LT j.
j December 11/29/83 to 12/07 /83 LT 0.03 LT 0.04 LT 0.04 LT 0.03 LT 0.05 LT 0.06 LT 0.04 LT 0.05
.,.*l 12/07 /83 to l 2/L 3/83 LT 0.05 LT o.os LT 0.05 LT 0.05 LT 0.03 LT 0.04 LT 0.03 LT 0.04 12/l3/83 to 12/20/83 LT 0.05 LT 0.05 LT 0.06 LT 0.06 LT 0.06 1.T 0.07 LT 0.04 LT 0.05 i 12/20/83
- I to 12/28/83 LT 0.06 I.T 0.06 LT 0.06 LT 0.06 LT 0.05 LT 0.05 LT 0.04 LT 0.05 i l2/28/83 to Ol/03/84 LT 0.04 LT 0.05 LT 0.05 LT 0.05 LT 0.05 LT 0.06 LT 0.05 LT 0.06 l., --------
- l (1) LT ~
Lese Than
- I i (2)
(3)
Sample missing due to failed sample pump
- One-day sample collected as part of effluent release monltorlng program.
i i
l l j
- I
- 1 I*
- j:
I l*i le ...:; [". -*.
( . ' ~1 c----, ,-*-:--*1 I II L~* ...,_:I I **- ~- .J \.. ....*... I I
I 1
j I
'-..._ Table 4 Ii .1 (Pagel of 3)
J*1 Gross Alpha on Air Particulate Filters VEPCO REHP - 1983 i 3
- 1 '(Results in E-03 pCi/m + 2s)
.,**/
'i' AVERAGE
'J Month Collection Period ss IIIR BC ALL CP DOW FE NN + 2s
- i*; -----
- .1 January 12/28/82 to 01/04/83 LT 1.50) LT 1.8 LT 1.8 LT 3 LT 1.9 LT 1.7 LT 2 LT 2 2.0 + 0.9.
j
- ., 01/04/83 to Ol/12/83 LT 1.8 LT 2 LT 2 LT 3 LT 2 l,T 2 J.T 2 LT 2 2,1 + 0.7
'.j 01/12/83 to 01/18/83 LT 3 LT 3 LT 3 LT 4 LT 3 3.1 + 2.6 LT 3 LT 3 3.1 + 0.7
- ! 01/18/83 to 01/25/83 3.1 + 2.1 2.3 + 2.1 LT 2 LT 4 LT 3 J.T 3 J.T 2 3.0 + 2.5 2.8 + 1.3
.I ii 01/25/83 to 02/02/83 2,4 + 1.6 LT 1.5 LT 1.5 LT 2 2.1 + 1.8 LT 1.7 LT 1,7 2.0 + 1,9 1,9 + 0.6 1i February 02/02/8) to 02/08/83 LT 1.3 2,1 + 1.8 q 1.4 3.5 + 2.6 LT 1.6 LT 1.6 LT 1,6 LT 1. 7 1.9 + 1,4 1! 02/08/83 to 02/15/83 1.4 + 1.3 2.9 + 2.0 1.5 + 1.5 LT 2 LT 1.4 LT 1.3 1.7+1.6 LT 1.4. 1.7 + 1.1 2.2 + 0.7 t,i' 02/15/83 to 02/22/83 LT 1.9 LT 2 LT 2 LT 3 LT 2 LT 2 LT 2 2,3 + 2.2
~
OJ 02/22/83 to 03/02/83 1.5 + 1.5 2.3 + 2.0 I.T 2 LT 2 LT 3 LT 2 LT 2 LT 3 2.2 + 1.1 l'.l
'I j March 0)/02/83 to 03/10/83 3.0 +*1.0 2.1 + 1.7 I.T 1.5 LT 2 2.7 + 2.0 LT 1.6 3.9 + 2.3 3.1 + 2.2 2.5 + 1.7
.J;
.i
! 03/10/8) to 03/16/83 15 + 5 9.5 + 4.1 19 + 5 l2 + 6 1.8 + 1.4 17 + 5 12 + 5 11 + 5 12 + 11 0)/16/63 to 03/23/63 LT 1.5 LT l. 7 1.T l. 7 LT 3 LT 2 LT 1.8 LT 2 LT 2 2.0 + 0.9 I 03/2)/83 to 03/30/83 1.9 + 1.6 LT l.7 LT 1.7 LT 3 LT 2 LT 1.9 LT 2 LT 2 2.0 + 0.8
- I li April 03/30/83 to 04/06/63 5.6 + 2.5 3.2 + 2.1 4.1 + 2.3 l.T 3 l.T 2 4.3+2.5- 3.1 + 2.3 LT 2 3.4 + 2.4 I 04/06/83 to 04/12/83 l.T 2 l.T 3 LT 3 3.0 + 2.2 LT 3 LT 3 r.T 3 4.9 + 3.1 3.1 + 1.6 I
j 04/12/63 to 04/19/83 4.1 + 2.2 J.T 1. 7 2.7..+ 1..8 l.T 3 LT 1.4 LT 1.9 LT 2 LT 2 2.3 + 1.7 J
04 /19/83 to 04/26/83 LT 2 LT 3 LT 3 2.0 + 2.0 LT 1.9 LT 3 LT 3 LT 3 2.6 + 1.1
- ,1 04/26/83 to 05/0)/83 2.4 + 1.7 3.7 + 2.1 1.8 + 1;6 2,6 + 2.0 2.1 + 1.5 2.8 + 2.1 3.4 + 2.2 LT 1,5 2.5 + 1.5 1;
l j
l Note: See footnote at end of table.
J I
I l
t I.
"i'.
r-*-*-**
j I :.., 1,: .. l Table 4 (Page 2 of 3)
Grose Alpha on Air Pert!culate Filters VEPCO REMP - 1983 3 .
(Results In E-03 pCi/m :!:. 2e)
AVERAGE Month Collection Period ss l!IR BC ALL CP DOW. FE NN + 2e May 05/03/83 to 05/10/83 I.T 3 LT 3 LT 3 LT 2 I.T 1.8 LT 3 ,LT. 3 "* LT 3 2.7 + 1.0 05/10/83 to 05/17/83 3.7 + 2.2 J.T l .3 LT l.3 LT 3 LT l.~ 3.8 + 2.3 LT 1.4 LT 1.5 2.2 + 2.2 05/17/81 to 05/24/83 1.8 + 1.6 2.2 + 1.9 LT 1.8 LT 4 LT 2 LT 2 LT 2 LT 2 2.2 :!:_ 1.* 5 05/24 /83 to 06/01/83 2.3 + 1.6 LT 1.6 t.T 1.6 LT 2 LT 1.9 LT 1.9 2.2 + 1.9 LT 1.8 1.9 + 0.5 June 06/01/83 to 06/08/83 2.4 + 2.2 LT 3 LT 3 LT 4 LT 3 LT 3 4.0 + 2.9 LT 3 3.2 + 1.1 06/08/83 to 06/14/83 2.4 + 1.9 LT 2 3.1 + 2.2 4.1 + 3.2 LT 2 LT 2 LT 2 LT 2 2.5 + 1.5 06/14/83 to 06/22/83 5.4 + 2.3 2.8 + 1.8 3.7 + 2.0 5.4 + 3.1 4.9 + 2.5 6.3 + 2.7 4.3 + 2.3 4.4 + 2.3 4.7 + 2.2 I-' 06/22/83 to 06/28/83 1.7 + 1.6 2.6 + 2.1 2.0 + 1.8 LT 3 LT 3 20 + 4 3.3 + 2.4 3.0 + 2.3 5 + 12 I.O 06/28/83 to 07/06/83 LT 2 LT 2* LT 2 LT 3 LT 3 LT 2 LT 3 LT 3 2.5 + 1.1 July 07 /06/83 to 07/13/83 2.2 + 1.6 2.0 + 1.7 2.2 + 1.8 5.2 + 3.4 LT 2 2.8 + 2.0 LT 2 3.5 + 2.3 2.7 + 2.3 07/13/83 to 07/19/83 2.6 + 2.4 3.0 + 2.6 3.1 + 2.5 4.8 + 3.9 LT 3 4.8 + 3.2 3.5 + 3.0 4.2 + 3.1 3.6 + 1.7 07 /19/83 to 07 /26/83 2.2 + 1.7 2.7 + 2.1 4.6 + 2.5 5.9 + 3.4 3.0 + 2.4 5.3 + 2.8 4.5 + 2.7 6.5 + 3.2 4.3 + 3.1 07 /26/83 to 08/02/83 NS(4) 5.5 + 3.0 6.8 + 3.1 LT 3 3.3 + 2.6 LT 2 LT 3 3.6 + 2.7 3.9 + 3.3 August 08/02/83 to 08/09/83 2.6 + 1.9 7.3 + 3.3 2.7 + 2.2 3.2 + 2.6 3.6 + 2.7 2.2 + 2.2 5.2 + 3.1 4.1, + 3.0 3.9 + 3.4 08/09/83 to 08/17 /83 3.3 + 1.9 3.3 + 2.3 3.2 + 2.2 2.8 + 2.2 6.2 + 3.0 3.7 + 2.3 3.3 + 2.3 7.2 + 3.3 4.1 + 3.3 08/17/83 to 08/23/83 7.1 + 3.4 7.8 + 3.7 10 + 4 5.8 + 3.4 9.4 + 4.4 LT 3 6.0 + 3.5 9.9+4.5 7.* 4 + 4.8 08/23/83 to 08/30/83 6.1 + 3.0 2.9 + 2.3 5.7 + 2.9 3.9 + 2.6 3.6 + 2.7 2.7 + 2.7 4.1 + 2.8 3.3 + 2.6 4.0 + 2.5 Note: See footnote at end of table.
I . -*.*- i. *. -*--- r-,-.--. r.----... .---~
I., . I. ...*.* I L,. * * * * *
,) '
- l. . ....J' ~:.J Table 4 (Page 3 of 3)
Gross Alpha on Air Particulate Filters VEPCO kEHr - 1933 3
(ilesulte in E-03 pCi/m :!:_ 2s)
AVERAGE Month Collection Period ss IIIR IIC ALI, CP DOW FE NN + 2e September 08/30/83 to 09/06/83 3.3 + 2.3 3.2 + 2.4 5.4 + 2.8 2.7 + 2.3 5.1 + 3.1 5.2 + 2.9 LT 3 4.2 + 2.8 4.0 + 2;2 09/06/83 to 09/14/83 3.4 + 2.1 5.2 + 2.6 4.2 + 2.3 LT 2 1.9 + 1.8 LT 2 (2} 4.7 + 2.7 3.3 + 2.8 09/14/83 to 09/20/i3 2.1 + 2.1 LT 3 5.0 + 3.0 2.9 + 2.3 2.9 + 2.5 3.7 + 2.9 LT 3 LT 3 3.2 + 1.7 09/20/63 to 09/27/83 LT 3 LT 2 4.1 + 2.5 2.8 + 2.1 6.1 + 2.9 1.6 + 1.5 2.5 + 1.4 1.11 + 1.5 3.0 + 3.0 09/27/83 to 09/27/83(3) 1.7 + 1.2
- October 09/27/83 to 10/04/83 LT 3 2.6 + 2.5 J.l + 2.6 2.8 + 2.3 3.1 + 2.6 2.8 + 2.8 LT 3 LT 3 2.9 + 0.4 10/01,/83 to 10/11/83 1.5 + 1.4 LT 2 1.7+1.5 1.7+1.4 LT 2 LT 3 LT 2 LT 2 2.0 + 0.9 10/11/83 to 10/18/83 2.3+1.7 1.7+1.6 1.5 + 1.4 1.9 + 1.6 LT 1.2 1.5 + 1.5 1.9 + 1.7 2.8 + 2.1 1.9 + 1.0 l'v 10/18/83 to 10/26/83 LT 1.3 LT 1.5 LT 1.4 LT 1.4 LT 1.4 LT 1.5 LT l,3 LT 1.6 1.4 + 0.2 0
10/26/83 to 11/04/63 2.4 + 1.4 LT 1.2 2.2 + 1.3 2.4 + 1.4 1.6 + 1.3 2.1 + 1.5 LT 1,1 2.8 + 1.6 2.0 + 1.2 November 11/01/83 to 11/08/83 1.7 + 1.2 2.1 + 1..3 2.3 + 1.3 1.9 + 1.2 2.4 :!:_ 1.4. 2.4 + 1.5 2.0 + 1.2 3.2 + 1.7 2.3 + 0.9 11/08/83 to 11/15/83 2.8 + 1.6 1.7 + 1.4 LT 2 2.5 + 1.5 LT 2 1.8 + 1.6 4.3 +. 1.7 3.8 + 1.9 2.6 + 1.9 11/15/83 to 11/22/83 2.0 + 1.2. LT 1.2 1.9 + l.2 1.2 + 1.1 1.6 + 1.2 1.4 + 1.1 1.2 + 1.0 2.8 + 1.6 1.7 + 1.1 11/22/83 to 11/29/83 3.3 + 1.4 3.3 + 1.6 4.2 + 1.7 ,,.6 + 1.8 4.2 + 1.7 3.5.+ 1.7 2.3 + 1.3 4.3 + 1.9 3.7 + 1.5 i December 11/29/83 to 12/07/83 12/07/83 to 12/13/83 3.1 + 1.5 5.6 + 2.4 2.8 + l.6 4.3 + 2.1
].l + 1.6 1.9 + 1.8 5.3 + 1.8 4.5 + 2.1 4.0 + 1.8
~.o + 2.5 3.-9 + 2.0 5.4 + 2.2 2.3 + 1.4 4.8 + 2.5 LT 1.9 4.1 + 2.2 3.3 + 2,.2 4.5 + 2.3 1 12/13/83 to 12/20/83 3.1 + 1.3 4.2 + 1.5 2.7 + 1.3 3.2 + 1.4 4.1 + 1.6 4.7 + 1.8 2.5 + 1.2 4.5 + 1.7 3.6 + 1.7 i 12/20/83 to 12/28/83 2.7 + 1.3 2.8 + 1.3 1.5 + 1.2 2.6 + 1.3 3.6 + 1.5 2.9 + 1.5 3.3 + 1.4 3.8 + 1.6 2.9 + 1.4 i
l 4.9 + 2.1 3.0 + 1.9 2.7 + 1.8 5.1 + 2.2 4.2 + 2.2 4.3 + 2.0 3.6 + 2.2 4.1 + 1.9 r 12/28/fll to 01/03/84 5.1 :I- 2.5 lI AVERAGE + 2s 3.0 + 4.3 2.9 + 3.2 3.1 + 5.5 3.3 + 3.3 2.9 + 3.0 3.4 + 6.5 3.0 + 3.4 3.3 + 3.7 I. (1) J.T - Less Thnn. The nctual I.LO values are included in the averages and standard deviations shown on this tahle.
I (2)
(3)
Sample missing due to failed sample pump.
One-day sample collecte~ oe part of effluent release monitoring program.
I. (4) NS - No sample received.
I rj;
[ ~- *--: r--1 :-----i
'*., ___ j ' _____ .....JI i.
Table 5 (Page 1 of 3)
Gross Beta on Air Particulate Filters VEl'CO REHP - 1983 (Results in E-03 pC1/m3 .:!: Zs)
AVERAGE Month Collection Period ss llIR BC Al.I, CP DOW FE NN + 2s January 12/28/62 to Ol/04/83 16 + 5 14 + 5 17 + 5 9.8 + 6.9 10 +5 LT 7(1) 13 + 6 17 + 6 13 + 7 01/04/83 to 01/12/83 21 + 4 11 + 4 14 + 5 7.4 + 5.8 12 + 5 15 + 5 12 + 5 13 + 5 13 + 8 01/12/83 to oi/18/8'3 7.6 + 4.7 6.5 + 5,1 l,T fl l,T 7 l,T 9 9.1 + 5.4 LT 9 9.1 + 5.9 8.2 + 2.1 01/18/ll.l to fl l /2 5/83 19 + 5 4.8 + 4.1 ll + 5 LT 10 LT 7 8.3 + 4.7 5.2 :!:. 4 .8 LT 7 9.0 + 9.1 Ol /2 5/8) to 02/02/fl J 19 + 5 14 + 5 13 + 5 7.5 + 6.2 13 + 5 12 + 5 13 + 5 13 + 6 13 + 6 February 02/02/83 to 02/08/83 LT 7 6.9 + 5.2 . LT 8 LT 10 LT 9 LT 9 LT 9 LT 9 8.5 + 2.2
\,)
02/08/83 to 02/15/83 25 + 4 28 + 5 19 + 4 26 + 6 21 + 4 24 + 5 25 + 5 21 + 5 24 + 6 02/15/83 to 02/22/83 19 + 5 16 + 5 14 + 5 LT 8 11 + 5 11 + 5 16 + 6 10 + 6 13 + 7 02/22/83 to 03/02/83 15 + 4 5.0 + 4.2 8.1 + 4.2 5.6 + 4.6 7.3 + 6.4 8.6 + 4.8 LT 7 8.0 + 5.4 8.1 + 6.1 Harch 03/02/83 to 03/10/83 11 + 4 6.9 + 4.3 7.5 + 4.2 LT 9 LT 7 LT 7 8.3 + 4.9 7.8 + 5.2 8.1 + 2.8 03/10/83 to 03/16/83 28 + 7 15 + 6 22 + 7 23 + 10 LT 8 29 + 8 16 + 7 19 + 7 20 + 14 03/16/83 to 0)/23/83 26 + 6 LT 8 LT 7 LT 8 LT 9 LT 8 LT 9 LT 9 11 + 13 03/2 3/63 to 03/30/83 11 + 5 LT 8 8.1 + 5*.2 LT 8 Iii + 7 LT 8 LT 9 6.7 + 5.7 9.4 + 5.9 April 03/30/83 to 04/06/83 78 + 8 9.7 + 5.1 7.7 + 4.8 LT 8 LT 8 LT 8 7.0 + 5.6 12 + 6 17 + 1,9 Olo/06/83 to 04/12/83 LT 7 LT 8 LT 8 LT 10 LT 10 LT 9 LT 9 23 + 7 11 + 10 04/12/8) to 04/19/83 29 + 6 4.8 + 4.5 4.6 + 4.4 J.T 10 l,T 6 LT 8 LT 8 LT 9 *9.9 + 16 04/19/83 to 04/26/83 11 + 5 8.3 + 5.1 9.9 + 5.0 7.8 + 5.2 LT 6 14 + 6 LT 8 11 + 6 9.5 + 5.0 04/26/83 to 05/03/83 22 + 5 23 + 6 16 + 5 13 + 5 18 + 5 13 + 6 19 + 6 20 + 6 18 + 8 NOTE: See footnotes on last page of table
c* - r--
1 r:-=:i r*-_.1
- --~-**'"-*'
- r. . --~-.. . . . r
...r-~
- .....~_) l Table 5 j (Page 2 of 3) j Gross Beta on Air Particulate Filtera l
1 VEPCO KliMP - 1983 (Results in E-03 pCi/m3 :!: 2s)
I j AVERAGE i Month Collection Period ss urn BC ALL CP 1)0\,/ l'g NN + 2s j
,\
,! May 05/03/83 to 05/10/83 34 + 6 10 + 5 13 + 5 LT 9 LT 7 8.1 + 5.6 5.8 + 5.5 9.3 + 5.7 12 + 18.
I 05/10/83 to 05/17 /83 25 :!: 5 8.4 + 5.1 7.4 + 4.9 LT 10 LT 8 33 + 7 11 + 6 LT 8 14 + 19 Ij 05/17/83 to 05/24/83 53 + 6 9.2 + 5.0 11 + 5 5.3 + 5.2 6.8 + 5.7 14 + 6 7.4 + 5.3 9.3 :!: 5.5 15 + 32 i
i 05/24/83 to 06/01/83 42 + 6 LT 7 6.5 + 4.6 LT 8 LT 9 LT 9 LT 8 7.1 + 5.4 12 + 24 I
I June 06/01/83 to 06/08/83 9.4 + 4.8 8.9 + 5.6 6.9 + 5.2 I.T 8 LT 9 LT 9 LT 9 8.5 + 6.0 8.6 + 1.6 j
'* 06/08/83 to 06/14/83 45 + 7 16 + 6 15 + 6 7.6 + 6.5 18 + 7 LT 10 14 + 7 17 + 7 18 + 23 06/14/83 to 06/22/83 39 + 6 16 + 5 22 + 5 12 + 7 18 + 6 23 + 6 25 + 6 17 + 5 22 + 16 06/22/83 to 06/28/83 14 + 6 LT 10 9.9 + 6.3 LT 9 9.9 + 5.1 63 + 7 72 + 10 12 + 5 25 + 53 9.5 + 5.3 9.3 + 3.9 r i
~
06/28/83 to 07/06/83 12 + 4 11 + 5 11 + 5 LT 8 6.2 + 5.4 8.4 + 4.9 LT 8 l*
I July 07 /06/83 to 0?/13/83 18 + 5 10 + 5 12 + 5 14 + 7 13 + 6 18 +*6 14 + 6 17 + 6 15 + 5.9 07/13/83 to 07/19/83 '43 + 8 27 + 7 23 + 7 14 + 9 27 + 9 21 + 8 37 + 9 30 + 8 28 + 18 I 07/19/83 to 07 /26/83 35 + 6 24 + 6 18 + 6 12 + 7 17 + 7 16 + 6 20 + 7 13 + 6 19 + 15 II 07 /26/83 to 08/02/83 NS(4) LT 8 11 + 5 9.1 + 6.0 11 + 6 LT 8 LT 9 11 + 6 9.6 + 2.8 I
i August 08/02/83 to 08/09/83 11 + 5 19 + 6 9.3 + 5.1 LT 9 14 + 6 9.8 + 5.8 13 + 6 6.3 + 6.1 l1 + 8
} 08/09/83 to 08/17/83 30 + 5 9.3 + 5.2 21 + 5 14 + 6 15 + 6 15 + 5 15 + 5 12 + 6 16 + 13 .
l ~
08/17 /83 to 08/23/83 08/23/83 to 08/30/83 39 + 8 22 + 6 40 + 8 16 + 6 33 + 7 19 + 6 22 + 7 7 .6 + 5."5 42 + 9 15 + 6 LT 9 13 + 6 39 + 9 18 + 6 40 + 9 17 + 6 33 + 23 16 + 9 ll*J 1
i NOTE: See footnotes on last page of table l
l 1I l
l 1
l lI I,
j
/1
i r--- [.. -*--.. r----:-1 ,.... .......,.
I **-' ... __ .. ~-* .. , t..
i i
r j
t Table 5 (Page J of. 3)
I
(Results in E-03 pCi/mJ :!:. 2s)
I
- j. --- ... --------------------------------------------------------------------
I
,{ AVERAGE.
r Month Collection Period SS lllR IIC ALL CP DOW FE NN + 2s l j September 08/30/83 to 09/06/83 22 + 6 19 + 6 17 + 6 11 + 6 15 + 7 14 + 6 19 + 6 10 + 6 16 + 8
.J' 09/06/83 to 09/14/83 17 + 5 23 + 5 30 + 6 LT 6 17 + 5 LT 7 (2) 38 + 7 20 + 23 09/14/83 to 09/20/83 22 + 6 19 + 7 18 + 7 15 + 6 16 + 6 15 + 7 19 + 6 23 + 8 18 + 6 11:
1 09/20/83 to 09/27 /83 LT 8 15 + 6 14 + 5 14 + 5 20 + 6 12 + 4 13 +4 15 + 4 14 + 7
.1. 09/27/83 to 09/27/03(3) 12 + 3 l
1,.
If 1
October 09/27/83 to 10/04/83 10/04/83 to 10/11/83 19 + 6 19 + 5 21 + 6 9,7 + 4.1 19 + 6 12 + 4 18 + 5 11 + 4 19 + 6 15 + 4 19 + 7 12 + 5 17 + 5 13 +4 20 + 6 16 + 5 19 + 2 13 + 6
!j. 10/11/83 to 10/18/83 27 + 5 12 + 4 8.6 + 3.4 16 + 4 16 + 4 15 + 4 23 + 5 21 + 5 1.7 :!:. 12
! 10/18/83 to 10/26/83 11 + 3 3.2 + 3.0 3.8 + 2.8 LT 4 LT 5 LT 5 LT 4 LT 5 5.1 + 4.9 A 10/26/83 to 11/04/83 7.5 + 3.8 5.1 + 3.8 LT 6 6.4 + 3.9 J.T 6 J.T 7 J.T 6 r.T 6 6.3 + 1.5 j.
J j November 11/01/83 to 11/08/83 10 + 3 7.6 + 3.4 3.7 + 3.1 9.9 + 3.4 5.9 + 3.4 7.5 + 3.8 9.3 + 3.2 11 +4 8.l + 4.9
.j I 11/08/83 to 11/15/83 15 + 4 11 + 4 LT 5 8.8 + 3.3 LT 6 10 + 4 9.0 +-3.3 9.5 + 4.1 9.3 + 6.1
!J .i 11/15/83 to 11/22/83 14 + ,, 3.5 + 3.1 LT 5 5.2 + 3.3 5.4 + 3.5 7.8 + 3.4 3.8 + 3.1 12 + 4 7.1 + 7.8 j ' 11/22/83 to 11/29/83 24 + 4 19 + 4 11 + 4 19 + 4 20 + 4 19 + 4 16 + 3 19 + 4 18 + 7 JI '
1 Jj December 11/29/8*3 to 12/07 /83 14 + 3 8.6 + 2.9 LT 4 11 + 3 8.7 + 3.0 12 + 4 7.2 + 2,6 LT 4 8.7 + 7.2 q
- I 12/07/83 to 12/i1/IIJ 15 + 4 8.1 + 3.7 4.0 + 3.6 8.5 + 3.7 9.1 + 4.4 13 + 4 16 +5 7.4 + 4.0 10 + 8
!; 12/13/83 to 12/20/83 22 + 3 19 + 3 11 + 3 19 + 3 20 + 4 43 + 5 16 + J 22 + 4 *22 + 19
\' 12/20/83 to 12/28/1!3 17 + 3 14 + 3 3.4 + 2.7 12 + 3 14 + 3 15 + 4 16 + 3 14 +4 13 + 8
). 12/23/83 to 01/03/84 19 + 4 17 + 4 4.7 + J.7 13 + 4 19 + 5 13 + 5 18 + 4 16 + 5 15 + 10 I .
.I.
I.
i AVERAGE + Zs 22 + 27 13 + 1/, 12 + 13 11 + 9 13 + 13 14 + 20 14 + 22 14 + 15 I
j f
' (l) LT - Lees Than. The nc1.w1l I.Lil vulues are included in the averages and standard deviations shown on this table, l
l (2) Sample mfsslng due to failed sample pump.
(3) One-day sample collected as part of effluent release monitoring program.
(I,) No sample received i
- I II, I ij :*
tr, . .*
):l' f,'.
' -~-::S-~. . -~ :* -~~-~-
n I {
r Table 6 I
I .
L:_; Gamma Spectrometry of Composited Air Particulate Filters VEPCO RE.MP - 1983 (Results in Units of E-03 pCi/m( 3 ) + 2s) rl*.-
Composite Location Quarter Period Be-7 Ce-144 Cs-134 Cs-137 Nb-95 Zr-95 ss 1 12/28/82 48 :t_ 13 LT 4Cl) 2.2 + 1.1 6.6 + l.6 LT l. 7 LT 3 HIR to 58 + 13 LT 4 LT 1.2 LT l.O LT l.2 LT 2 BC 03/30/83 50 :t_ 13 LT 3 LT l.6 LT 1.7 LT* 1,7 LT 4 ALL 78 + 23 LT 8 LT 1.9 LT 2 LT 2 LT 3 CP 32 :t_ 13 LT 7 LT 2 LT 1,4 LT 1.7 LT 3 DOW 53 ::t_ 13 LT 4 LT l.5 LT l.3 LT l. 7 LT 2 FE 48 :t_ 14 LT 4 LT 1.7 LT l.7 LT 1.,9 LT 3 NN 38 + 16 LT 7 LT 2 LT l.6 LT l.5 LT 3 ss 2 03/30/83 79 :t_ 28 LT ll 5.4 + 2.2 14 + 3 LT 4 LI 6 liIR to 58 :t_ 24 LT 11 LT 3 LT 3 LT 3 LT .5 BC 07 /06/83 55 :t_ 19 LT 6 LT 1.9 LT 2 LT 2 LT 5 ALL 66 :t_ 20 LT 10 LT 3 LT 3 LT 3 LT 6 CP LT 70 LT 17 LT 4 LT 6 LT 6 LT 10 DOW 100 + 40 LT 15 LT 3 LT 3 LT 5 LT 14 FE 56 + 29 LT 13 LT 5 LT 7 LT 6 LT 7 NN LT 70 LT 13 LT 4 LT 5 LT 4 LT 11 11 I i ss 3 07 /06/83 88 :t_ -23 LT 9 LT 3 4.3 :t_ l.9 LT 3 LT 5 L.'j HlR to 94 :t_ 26 LT 8 LT 2 LT 3 LT 4 LT 8 BC 10/04/83 88 + 24 LT 9 LT 2 2.0 + LO LT 3 LT 5 r *. ALL 97 + 28 LT 10 LT 3 LT 3 LT 4 LT 7
!' CP 82 :t_ 25 LT 9 LT 2 LT 2 LT 2 LT 4
~
DOW 73 :t_ 22 LT 9 LT 2 LT 3 LT 4 LT 6 FE 75 ::t_ 23 LT 10 LT 2 LT 2 LT 3 LT 4 110 :t_ 30 LT 9 LT 2 LT 3 LT 4 LT 7 ss 4 10/04/83 60 + 20 LT 8 LT 3 LT 3 LT 3 LT 5 r, HlR to 43 :t_ 13 LT 5 LT l.3 LT l.3 LT l.9 LT 3 L.; LT l.8 LT LT LT 4 LT 6 BC Ot/03/P,4 LT 50 3 3 ALL 46 :t_ 16 LT 8 LI l. 7 LT l.9 LT 3 LT 4 CP 33 :t_ 20 LT 12 LT 4 LT 4 LT 4 LT. 8 DOW 62 :t_ . 25. LT 11 LI 3 LT 3 LT 4 LT 8 FE 33 :t_ 26 LT l. 7 LT 3 LT 4 LT 5 LT 9 r**-~ NN 71 :t_ 20 LT 8 LT 2 T,T 2 LT 2 LT 5 i .
i '
Cl) LT* Less Than 24
-=---***** -- ----.-*-*---*---.-----------.-- ---.-------- -
.,. :r
~
- i. j
- .. }
B.- Mi 1k The results of iodine-131 analyses of milk samples are presented in Table 7. No I-131 was detected in any of the samples. A total of 59 analyses were performed, 47 from indicator locations and 12 from the Williams (WMS) control location. The required sensitivity limit of 1 pCi/1 for I-131 in milk could not be met for the December milk sample from station EPPS due to delay between sample collection and arrival at f -~ the 1abora tory.
L.J Milk samples were also analyzed by gamma spectrometry and the results are shown in _Table 8. A total of.58 samples were analyzed, 47 from indicator locations and 11 from the WMS control location. The required sensitivity limits of 60 pCi/1 for Ba-140 and 15 pCi/1 for La-140 were not met in 10 of the analyses, due to delay in analysis. The La-140 sensitivity limit was also exceeded in two additional analyses due to delay between sample collection and arrival at the laboratory.
As expected, naturally occurring*K-40 was the major detectable activity
! : in the milk samples. Detectable levels of cesium-137 were found in 15 i :
of 58 samples, ranging from 1.4 to 43 pCi/1. Since Cs-137 is present in global
- fallout, the occasional detection of this isotope in environmental media is not unusual. With two exceptions,* the results fell well within the expected range of activities due to long term fallout. On~ value, 43 pCi/1, was higher than expected, although 1**, occasional results in this range have been reported for other programs.
LJ In a second sample, Cs-137 was accompanied by Cs-134 at a level of 10 pCi/1. The presence of Cs-134 is indicative of the release of radioactivity from the plant. This possibility has been previously noted in the discussion of air particulate analytical results. NRC non-routine reporting levels for these isotopes are 60 pCi/1 for Cs-134 and 70 pCi/1 for Cs-137, and the levels found are well below these action levels.
Stable. (non-radioactive) calcium in milk was also determined in 60 r*****
\ . samples at an average level of 1400 + 340. These analyses were performed by the NUS Laboratory Services Division rather than by the NUS Radiological Laboratory.
- r .
I.
I l \ Strontium-89 and strontium-90 were determined in 58 samples, 48 from indicator locat~ons .and 10 from the WMS control location. Results for these analyses are listed in Table 10. Stro~tium-89 was not detected in any of the samples analyzed.
Strontium-90 was found in 5 of 58 samples, ranging from 1.6 to 3.5 I pCi/1. Two of the four samples were from indicator locations; the i
- l. remaining two were from the WMS control location. Strontium-90 is likely to be due to global fallout. During the preoperational radiological monitoring program for Surry Power Station, stronti~m-90 was detected in milk samples at a range of 5.2 to 13 pCi/1.
25
-- *----- ----..........-c-..,_____ ,__,.. -.-7'"-* _... .,~ -,,.- - ** ... - ,..... * -_. *-. *- - - - . - - ---*--' - **,.._ ......,_ --.-,- - * ........-.. .--. --- - ----------*------..... - - - - - - - - * - - - - ~ - - - - -
---*f **-***-- .
- *-~--;,*:*-* *** ~._ ....:_,._ ... * **** * ** * ** * * ** ** __ .*. -, ___ ** ~-~: *** -* .*', ** * --~*.: * .. ~z' - ::=::** -.:. ---~--~...-:-- -0_~ .,-~-- -~-..;: .: ..,.* :_;,._
n u
Table 7 (Page 1 of 2) i"
! .-~
r -. Iodine-131 *in Milk VEPCO REMP - 1983 (Results in pCi/1 + 2s) l n-L_J Month Location Sampling Date Iodine-131 n! l l'.....:.J January LEE HALL 01/05/83 LT 0.4(l)
EPPS 01/06/83 LT 0.3
,-i CP 01/18/83 LT 0.6 ll .\
.c..l WMS JDKs 01/18/83 01/18/83 LT LT 0.5 0.5 r-, February LEE HALL 02/02/83 LT *0.5 1..~ EPPS 02/03/83 LT 0.4 CP 02/08/83 LT 0.3 WMS. 02/15/83 LT 0.5 1".. JDKs 02/08/83 LT 0.4 L.-~!
March LEE HALL 03/29/83( 2 ) LT 0.3 f':
._J EPPS 03/03/83 LT 0.3 CP 03/16/83. LT 0.2 WMS 03/23/83 LT 0.2 n JDKs 03/16/83 LT 0.3 f .'.
- April LEE HALL 04/13/83 LT 0.3 I -
I EPPS 04/14/83 LT 0.3 l .
L.J CP 04/12/83 LT 0.3 WMS 04/19/83 LT 0.4 r*-1 JDKs 04/12/83 LT 0.4 l.J May LEE HALL 05/11/83 LT 0.7 EPPS 05/12/83 LT . 0 .3
- 05/10/83 05/24/83 LT 0.3 LT 0.2
- JDKs 05/10/83 LT 0.2 1*,.,
u June LEE HALL 06/01/83 LT 0.2 EPPS 06/01/83 LT 0.3 n CP 06/14/83 LT 0.3 LJ WMS JDKs 06/23/83 06/14/83 LT LT 0.6 0.,2.
~: **;
'L__
Note: See footnotes at end of table.
26
- ..... -:;:-***----~-.. -- t -----------*--*-- .- .:.. *-----"-~~--- ... * .. --~- .. * ,.* .. *-*c:-*.<:c*0*>.'*.:<.:*,.,2c******h,-.-*.*.c,.*.. -<***--=-',.- .-.*:...;.,., ,,. . :. :_.-~ .: * * "* . ___*. * *-----* *-~-
~ .,*
\
u rn ,
u Table 7 (Pa:ge 2 of 2)
Iodine-131 in Milk VEPCO REMP - 1983 (Results in pCi/1 + 2s)
[J Month Location Sampling Date Iodine-131 n
Lj July LEE.HALL 07 /13/83 LT 0.13 EPPS 07 /14/83 LT 0.3 u
CP 07 /19/83 LT 0.14 WMS 07/27/83 LT 0.2 JDKs 07/19/83 LT 0 .11
,- August LEE HALL 08/10/83 LT 0.4
) '
/_; EPPS 08/10/83 LT 0.9 CP 08/10/83 LT 0.4 r; WMS 08/17/83 LT 0.2 u JDKs 08/10/83 LT 0.4 September LEE HALL 09/01/83 LT o.s r-:LJ EPPS 09/01/83 LT 0.3 CP 09/14/83 LT 1.0 WMS 09/27 /83 LT 0.3 n
i :!
JDKs 09/14/83 LT 1.0 L.:J October LEE HALL 10/06/83 LT 0.2 r= -*
! ; EPPS 10/06/83 LT 0.2 u CP WMS 10/11/83 10/18/83 LT 0.2 0.2 LT f Tl
- 1
- JDKs 10/11/83 LT 0.2 LJ November LEE HALL 11/10/83 LT 0.2
- --~ EPPS 11/10/83 LT 0.2
/_j CP 11/08/83 LT 0.14 WMS 11/29/83 LT 0.17 JDKs 11/08/83 LT 0.15 r*~ ..
(~~!
t~ December LEE HALL 12/08/83 <3 )
EPPS 12/08/83 LT 1.2(4) r--:*:i r : CF 12/13/83" LT 0.3 i*-,,
I,:
~ ... WMS 12/20/83 LT o. 7 JDKs 12/16/83 LT 0.3 c: ~
- 4 LT = Less Than L,
(1)
(2) Original sample, dated 03/03/83, was received spoiled and could not be analyzed for I-131. The station was re sampled on 03/29/83.
!_:_: (3) Sample lost during *analysis due to broken container.
(4) Lower sensitivity due to delay in shipping.
r - -*
I 27
. - . . .** _ .. - *y~_....... _, *_* ""'. - . . . . . ..- .,--~_ ~~~ ~- * * - ,...,.._.,. __ -._ ,,--,.,,~-, :- .....,~-----~-----*-- - ~ _.,..,. _______ * - - - - - - - - -... -~-~~ *. ,.-. -**-------.~ ...---.--. - - - * - - - __________ _, ___ _
. **--;----- .*... _,. *i*** *. . . . . . . . . *.. **-*.**** .*:. .~. :*** .._*_:.~ ::.** .:.,-*.J,.\ ,*".):<:<:*.:~:.-"-~:.-* .,,: :* -'_-_.**:;- ".,.: .._.. *.~--->-~:- -~-: .*. . *:*.-;;*. -. ~-~----. --~:.:L..-.:<< .* --~:-. -... **>* __ :* .- __ .. __ *... 0.,.* *.... : .:- ~:-* :_. -~* *._* ::<_.<:.::-~---:*=..
r, .
iL._~i r1 i Table 8 1 .. i (Page 1 of 2)
Gamma Spectrometry of Milk r--c.
[I ____: (Results in pCi/1 !_ 2s)
Month Location Sampling Date Ba-140 Cs-134 Cs-137 K-40 La-140 I
\ ..
January LEE RALL 01/05/83 LT 30(l) LT 9 LT 10 1400 200 LT 10 01/06/83 LT 30 LT 11 1100 + 200
=- LT 13 EPPS LT 9
[l CP 01/18./83 LI' 30 LT 10 LT 12 1400 + 200 LT 13 IIMS 01/18/83 LT 30 LT 9 LT 8 1300 + 200 LI' 15 JDKs *01/18/83 LT 30 LT 9 LT 8 1300 200 LT 12
['__j =-
February LEE RALL 02/02/83 LT 13 *LT 4 LT 4 1300 200 LT 8 EPPS 02/03/83 LI' 20 LT 7 LT 6 1500 + 200
=- LT 8
[1 CP 02/08/83 LT 30 LT 10 LT 10 1300
=-
200 LT 15
--' IIMS 02/15/83 LT 20 LT 7 LT 8 1400 + 200 LT 9 r~ JDKs 02/08/83 LT 15 LT 6 LT 7 1100 200 LT 7
=-
i __;
March LEE HALL(2) 03/29/83 LT 30 LT 7 LT 7 1400 + 200 LT 13 EPPS 03/03/83 LT 19 10 4 21 5 1300 200 LT 13 Tl 03/16/83 LT 20 LT 9
=- =-
LT 8 1300 + 200
=- LT 11 CP l..J IIMS 03/23/83 LT 13 LT 4 LT 5 1500* 200 LT 6 03/16/83 LT 30 LT 11 LT 10 1200
=- 200 LT 14 JDKs
=-
[ April LEE HALL 04/13/83 LT 16 LT 5 3.1 2.8 1300 + 200 LT 9
=-
n EPPS 04/14/83 LT 20 LT 5 LT 6 1400 200 LT 9 LT 9 . 1400
=- 200 CP 04/12/83 LT 20 LT 11 LT 12
=-
WMS 04/19/83 LT 17 LT 5 LT 6 1400 +
- 200 LT 9
-- JDKs 04/12/83 LT 20 LT 8 LT 8 1200 200 LT 12
(
I ,
=-
u May LEE HALL 05/11/83 LT 20 LT 6 LT 8 1400
=-
200 LT 10 EPP"S 05/12/83 LT 20 LT 7 LT 8 1400 200 LT 9
=-
r-i I CP 05/10/83 LT 19 LT 6 LT 7 1200
=--
200 LT 10 L_J IIMS 05/24/83 LT 20 LT 6 LT 7 1500 200 LT 13 43 1100
=-+* 200 JDKs 05/10/83 LT 20 LT 8 8 LT 9 r*-:c =-
L June LEE HALL 06/01/83 LT 17 LT 4 8.6 + 3.0 1800
-+ 200 LT 7 EPPS 06/01/83 LT 20 LT 7 LT 8 1400 +- 200 LT 11 r*1i CP 06/14/83 LT 30 LT 9 LT 12 1000
=-
100 LT 17
' I L IIMS (3) 06/23/83 JDKs 06/14/83 LT 15 LT 5 5.6 3.4 1300 200 LT 6 r-*1 =- =-
I I -----
LJ Note: See: footnote at end of table.
r-:
\
I l
'-J 28
\...--1
/
- - -*. ' * ' -**. . * "I: ~ ** ** * * -:----.-.-::,-......- . - ~ - - - - ..- - - * - - ~ . --------* * * * ~*-* . - - - - - - ~ ** *--* .-.,-,--,.-------------~----........--~. - ~ - - . . - - - *
. ~-,' ~-. _: ... ;
""'"_ . . . .___ :..-:__:...~--..;::.:.._:.~~~~;.-~~-~-~*-:-.-- *-- .. : .. :-_.>* . ---.~::<> . . *::_***>::~.:!:.-** .:'-.; *., ... .,. *!* * -*** .. ,_ _ _ *- ** -:<..- .. *... ,* ..,.. a.:....::-'-* .*. :_** .....,...~:**- .... *.. *,.-;-:.-:-.<:.-.:*::;-*..: .'*-,_~-~::* .. *. - .. _..: >, *.:.....
.. f L.J Table 8 (Page 2 of 2) c~ Gamma Spectrometry-of Milk l ..
I ' VEPCO REMP ~ 1983 (Results in pCi/1 +/-. 2p)
Month Location Sampling Date Ba-140 Cs-134 Cs-137 K-40 La-140 l
July LEE HALL 07 /13/83 LT 30 LT 10 LT 12 1300 +/-_ 200 LT 14 f: EPPS 07 /14/83 LT.30 LT 11 LT 13 1400' +/-_ 200 LT 11 1._J LT 400( 4 ) LT 180( 4 )
CP 07/19/8':. LT 1.9 2.5 +/-_ 1.2 1200 + 200 WMS 07 /27 /83 LT 30 LT 7 LT 8 1500 + 200 LT 14 n
I i JDKs 07 /19/83 LT 200( 4 ) LT 1.3 2.9 +/-_ 0.8 1300 +/-_ 200 LT 130( 4 )
L3 August LEE HALL 08/10/83 LT 30 LT 10 LT 11 1500 +/-_ 200 LT 15 EPPS 08/10/83 LT 30 LT 7 LT 9 1500 +/-_ 200 LT 15 CP 08/09 /83 LT 40 LT 11 LT 13 1300 +/-_ 200 LT 14 WMS 08/17 /83 LT 40 LT 12 LT 14 1700 + 200 LT 14 f-C-'
' . JDKs 08/09/83 LT 30 LT 9 LT 12 1300 +/-_ 200 LT 13 i i l....'
September LEE HALL 09/01/83 LT 150( 4 ) LT 2 2.0 +/-_ 1.3 1400 +/-_ 200 LT 70( 4 )
r, I i EPPS 09/01/83 LT 120( 4 ) LT l.9. 3.6 +/-_ l.l 1200 +/-_ 200 LT 50( 4 )
u CP 09/14/83 LT 50 LT l.3 l.4 +/-_ 0.8 1300 +/-_ 200 LT 20 WMS 09/27 /83 LT 4000( 4 ) LT 3 LT 4 1300 + 200 LT 1300( 4 )
JDKs(6) 09/14/83 October LEE HALL 10/06/83 LT 800( 4 ) LT l.4 ~.3 +/-, 0.8 1300 +/-_ 200 LT 300( 4 )
n EPPS CP WMS 10/06/83 10/11/83 10/18/83 LT 1000 ( 4 )
LT 1300( 4 )
LT 800( 4 )
LT 2 LT 3 LT 3 2.5 LT 4 LT 3
+ Ll 1300 1500 rsoo +
+/-_ 200
+ 200 200 LT 400( 4 )
LT 600( 4 )
LT 400( 4 )
JDKs 10/11/83 LT 600( 4 ) LT 1.8 2.1 +/-_ l.0 1400 + 200 LT 300( 4 )
l i .:
__ J November LEE HALL 11/10/83 . LT 20 LT 4 LT 5 1400 +/-_ 200 LT 9 EPPS 11/10/83 LT 18 LT 4 4.0 + 2.3 1600 +/-_ 200 LT 9 CP 11/08/83 LT 30 LT 5 LT 6 1400 + 200 LT 15 WMS 11/29/83 LT 30 LT 5 LT* s 1500 +/-_ 200 LT 20 JDKs 11/08/83 LT 18 LT 3 LT 4 1300 + 200 LT 9 December Lee Hall 12/08/83 LT 30 LT 2 LT 3 1200 .!. 200 LT 18( 5 )
EPPS 12/08/83 LT 60 LT 4 LT 4 1400 +/-_ 200 LT 30 (S)
CP 12/13/83 LT 50 LT 6 LT 6 1300 +/-_ 200 LT 20 WMS 12/20/83 LT 20 LT 3 LT 4 1300 .!. 200 LT 13 n
L____;
JDKs 12/16/83 LT 18 LT 2 2.5 + 1/2 1300 + 200 LT 10 (l) LT= Less Than (2) This was the record sample collected. An earlier sample arrived spoiled and was resampled.
(3) Sample destroyed during ashing, due to furna*ce malfunction.
(4) Lower sensitivity due to delay in counting, (5) Lower sensitivity due to delay in shipping, (6) Sample depleted in other analysei.
29
. - *- -**---* *------* -------~----~---~,--------:-- ------.*-*-:-*:----::: . -,.. .* .. - ',.- . -. *... - :.-
-~ ,...,;::,.,. .* ~-' .... .* .---- .. *.* . .~:--~- _. , , ~ ..... \.{..-....... _... -~--- . -,--.-~- . ~--~. ~,---_.....:::_ __ _
(1 i* i t.:.*.J Table 9 (Page 1 of 3) f':
I '
Calcium in Milk VEPCO REMP - 1983 i ; (Results in mg/1) l..
Sampling Calcium Month Location Date Concentration January LEE HALL 01/05/83 1380(1)
EPPS 01/06/83 1380 n
u CP WMS 01/18/83 01/18/83 1540 1570 JDKs . 01/18/83 1550 Average.+/- 2s 1480 + 190 February LEE RALL 02/02/83 1200 EPPS 02/03/83 1160 CP 02/08/83 1430 WMS 02/15/83 1570 JDKs 02/08/83 1550 Average + 2s 1380 + 380 March LEE HALL 03/29/83 1450 EPPS 03/03/83 1250 CP 03/16/83 1320 I ,
u WMS 03/23/83 1610 JDKs 03/16/83 1360 Average.+/- 2s 1400 + 280 April LEE HALL 04/13/83 1390 EPPS 04./14/83 1400
.CP 04/12/83 1560 WMS 04/.19/83 1890 JDKs 04/12/83 1590 Average.+/- 2s 1570 + 410 r**,.
I i 1060 u May LEE HALL EPPS 05/11/83 05/12/83 1110 CP 05/10/83 1360 WMS 05/24/83 1400 JDKs 05/10/83 1340 Average+ 2s 1250 + 310 Note: See footnote at end of table .
l_.'
30
- .* .----~---****-~---. **.*-.-. r * - ..*. *z.~" -,-_.,-. ** - -*.*~--~--"',""7.* * ~ .* *... ~-:*... *.* ,._.-.*--* --~-*,-.-**.~ ..~ * ! . - *...- .. ~-_, ____ .,.,_ .,* *~ .. * ~--~-- --**---.---.~----.-.--.,--.---.-,.
- ---*-- -...._~- ~- <.~., *,_ '* ..-.* __ ._.___,__ ___.__ -_* -*~-~-**-*-* . *. **-..-__ ' _.* - . '*~-- .. *- -*-*-** *. *~:.":,. -~;".*:;. . . :.*.:.-:~.,:*., :_~;~.-..;:: :_. **_ :.~*-.. *.. *:_. *.
('
~-
1... J 1*, ! / Table 9
\ ..
L_.*.a (Page 2 of 3)
Sampling Calcium Month Location Date Concentration June LEE HALL 06/01/83 1200 r---
1 *.] EPPS 06/01/83 1300 I j L.J CP .06/14/83 1500 WMS 06/23/83 1400 JDKs 06/14/83 1400 Average+/- 2s 1360 + 230 July LEE HALL 07/13/83 1300 EPPS 07/14/83 1200 CP 07/19/83 1400
- WMS 07/27/83 1400 fJ JDKs Average+/- 2s 07/19/83 1600 1380 + 300
[
August LEE HALL 08/10/83 1400 EPPS 08/10/83 1300
[ CP WMS 08/09/83 08/17/83 1300 1300 JDKs 08/09/83 1400 Average+ 2s 1340 + 110 September LEE HALL 09/01/83 1300
- EPPS 09/01/83 1400 L.
- ..i CP 09/14/83 890 c-*,
. r *: WMS 09/27/83 1500 u JDKs Average + 2s 09/14/83 1000 1220 + 260 Note: See footnote at end of table.
0 31
. _____ ~- -~. *. --~"'.".---..-... _. .... * ~- ~--* .... .._
- -* *-**~**.**-.-* **. '* --.-* .. :-.-.~ ....
l(
Table 9 (Page 3 of 3)
Calcium in Milk VEPCO REMP - 1983 (Results in mg/1)
Sampling Calcium Month Location Date Concentration C __ ;
October LEE HALL 10/06/83 1400 i"':i EPPS 10/06/83 1400 l :.-.:; CP 10/11/83 1500 WMS 10/18/83 1400 r,- . JDKs 10/11/83 1500
!I l_,.
- Average.+/- 2s 1440 + 110 November LEE HALL 11/10/83 1100 EPPS 11/10/83 1000 CP 11/08/83 1500
.. WMS 11/29/83 1500 JDKs 11/08/83 1200 Average.+/- 2s 1260 + 460 1":
i :
[_~
December LEE HALL 12/08/83 2000 r*'* EPPS 12/08/83 1200 I ' CP 12/13/83 1420 L WMS 12/20/83 1500 JDKs 12/16/83 1350 Average.+/- 2s 1490 + 610
- l. i..2 JDKs 1400 + 350 (1) Estimated error is less than 5%.
I i'--'-
32
.,. ...-47. ., * *-. - ~ * "* ."'J"-- * .-. *, ~~.~ <., ,-.s;;:v~ ** ~ , .-~,*. * * ,-.* .. - - * - ~ _ _ _ _ _ -* _ _,_ ., ~ _ *--=---- '---=---*- -="' _ _,_. _ *-*
I D
I .,
~ ..
- n. __ j .
Table 10 (Page 1 of 2)
Strontium-89 and Strontium-90 in Milk VEPCO REMP-1983 (Results in pCi/1 + 2s)
Month Location Sampling Date Strontium-89 Strontium-90 January* LEE HALL 01/05/83 LT 0.7(l) LT 0.8 r
II *. EPPS 01/06/83 LT 1.5 2.2 + 1.3 L ..
CP 01/18/83 LT 0.6 LT 0.6 WMS 01/18/83 LT 1.0 LT 1.0 JDKs 01/18/83 LT 0.7 LT O. 7 February LEE HALL 02/02/83 LT 0.6 LT 0. 6 EPPS 02/03/83 LT 0.6 LT 0.6 CP 02/08/83 LT 1.2 LT O. 6 WMS 02/15/83 LT 0.7 LT 0. 7 JDKs
- 02/08/83 LT 0.6 LT 0~6 March LEE HALL 03/29/83 LT 1 LT 1 EPPS 03/03/83 LT 1 LT 1 CP '03/16/83 LT 2 LT 2 WMS 03/23/83 LT 1 LT 2 JDKs 03/16/83 LT 2 LT 2 April LEE HALL 04/14/83 LT 1.3 LT 2 EPPS 04/14/83 LT 0.8 LT 1.1 r*-- CP 04/12/83 LT 1.0 LT 1.2 i
L.: WMS 04/19 /83 LT 1 LT 1 JDKs 04/12/83 LT 1.1 LT 1.5
~'.
[ i May LEE HALL 05/11/83 LT 1 LT 1
-s EPPS 05/12/83 LT 1 LT 2 CP 05/10/83 LT 1 LT 1 WMS (2) 05/24/83 JDKs 05/10_/83 LT 1 LT 2 June LEE HALL 06/01/83 LT 1 EPPS 06/01/83 LT 1 CP 06/14/83 LT 1.8 WMS (2) 06/23/83 JDKs 06/14/83 LT 5 3.5 + 2.7 r .
Note: See footnote at end of table.
i .
,_ 33 i .
- -**---. __ ,**.*:/*,~*~--------- - ~--*-
-r:-:a r .
f ..
Table 10 (Page 2 *of 2)
Strontium-89 and Strontium-90.in Milk VEPCO REMP-1983 (Results in pCi/1 +/- 2s )
Month Lo.cation Sampling Date Strontium-89 Strontium-.90 i ~ r-i July LEE RALL 07/13/83 LT 0.6 LT 0.5 EPPS 07/14/83 LT 0.7 LT 0.6
!__ ; CP 0.9 LT 1.0
[ ;
07/19/83 LT WMS 07/27/83 LT 1.1 LT 1.5 JDKs 07/19/83 LT 1.2 LT 1.5 August LEE RALL. 08/10/83 LT 0.8 LT 0.7
,---. EPPS 08/10/83 LT 1.3 LT 2 il . CP 08/09/83 LT 0.9 LT 1.8 WMS 08/17/83 LT 1.0 1.6 + 1.1 JDKs 08/09/83 LT 0.8 LT 0.8 September LEE HALL 09/01/83 LT 0.8 LT 1. 2 EPPS 09/01/83 LT 0.8 LT 1.3 CP 09/14/83 LT 0.7 LT 2 WMS 09/27/83 JDKs 09/14/83 LT 0.8 LT 2 October LEE RALL 10/06/83 EPPS 10/06/83
,: -- CP 10/11/83 WMS 10/18/83 LT 0.5 L J.DKs 10/11/83 November LEE RALL 11/10/83 EPPS 11/10/83 CP 11/08/83 WMS 11/29/83 JDKs 11/08/83 December LEE RALL 12/08/83 EPPS 12/08/83 CP 12/13/83 WMS 12/20/83 r-~ JDKs 12/16/83 i
L......:
(1) LT= Less Than (2) Sample destroyed in analysis L.
r ,
34 I
- -~-*,--a*-...._~** ... * - . ~ * ~ * * . * * . , - : ' * . * " ' ... *. * **.~ .*, .~.- -,* '* .*.. ~ .. *'r,.-"./,, ...... ~ , .*.--*.;.-, ..,~,, .......- ._*-f N'S:.-...~--
C. Precipitation I
I ' Precipitation samples were collected as monthly composites and analyzed 1*--,
for gross beta and tritium. Quarterly samples from the same locations (one indicator and one control) were composited from monthly aliquots retained at the site. This compositing was performed by station personnel and the composites were submitted for the san~ analyses as monthly samples. The results of these analyses are shown in Table 11.
In some cases, the. gross beta results on the quarterly samples appear to be at variance with the results from monthly samples. In all these cases the reported value was confirmed by reanalysis. Sampling, storage n l--:.J and compostting methods were reviewed with VEPCO and the reason for the discrepancies remain unresolved. Tritium was detected in 6 of 32 analyses. The values were typical for environmental samples.
r, l) D* Water l **..J
,-- Well water was collected from four indicator locations during May and 1 ; October. The results of gross alpha, gross beta, and tritium analyses
!....! on these 8 samples are sho\'m on Table 12. No alpha activity was found in any of the samples (stations SS, HIR, BC, and JMTN). Gross beta activities ranged from 1.8 to 11 pCi/1, well within the preoperational range of O to 25 pCi/1. Tritium was.detected in 2 of 8 analyses at typical environmental levels.
Table 12 also includes gross alpha, gross beta, and tritium results on 8 surface water samples which were also collected during May and October.
Surface water stations are Chippokes Creek '(CC) and three reservoirs
- n. (WMR, NNR, and SR). All are indicator locations.
activities of 4 and 9.6 pCi/1 were found in 2 of the 8 samples.
range of gross beta activity was 1.4 to 23 pCi/1. The maximum value in Gross alpha The this range was confirmed by reanalysis; this sample contained high suspended solids. No tritium was detected in any of these samples.
In addition to the water samples discussed above, samples of James River lJ water are collected as both. monthly composites and bi-monthly grab samples. The James River is an estuary near Surry Power Station and undergoes tidal exchange with Chesapeake Bay. River water samples thus represent saline bay water in contrast to the fresh water samples discussed above.
Ga~ma spectrometr~ was performed on bi-monthly grab samples of James River water and the results are presented on Table 13.
- With four exceptions, all nuclides were below the detectiorr limit. The May sample from Surry Discharge (SD) contained 5.5 pCi/1 Co-58, 9.8 pCi/1 Cs-134, I: and 11 pCi/1 Cs-i37. These nuclides may be due to plant operations. In addition, the November sample from Hog Island Point (HIP) contained 3.7 pCi/1 Cs-137. When unaccompanied by Cs-134, Cs-137 is likely to be due to atmospheric fallout.
'L....' 35
...____-._.,.~-----..................... --- ....... _ ... *. *--. ---~---*****-* . .-,-*--*-*-- ------ --. ----- *- " - ------
,__.- --:* *---~-~-~-**---------~*----------...-*-* ..- . - . . ---" -*-. :- ~~- ---- *---- _. - .. ,. ---**
Table 11 Gross Beta and Tritium in Precipitation (Monthly and Quarterly Composites)
VEPCO REMP-1983 (Results in pCi/1 +/- 2s)
Collection Location Month Period Gross Beta Tritium ss January 01/01/83 to 02/01/83 2.7 + 1.4 LT 300(1)
February 02/01/83 to 02/28/83 1.9 + 1.3 LT 400 March 03/01/83 to 03/30/83 1.6 + 1.2 LT 300 Quarter 1 01/01/83 to 03/30/83 75 + 8 LT 300 NN January 01/01/83 to 02/01/83 1.4 + 1.3 LT 300 February 02/01/83 to 02/28/83 4.6 + 1.4 LT 400 March 03/01/83 to 03/30/83 LT 1.8 190 + 180 Quarter 1 01/01/83 to 03/30/83 49 + 5 LT 300 ss April 04/01/83 to 04/26/83 1.5 + 1.3 LT 300 May 04/27/83 to 05/31/83 5.0 + 4.9 750 + 200 June 06/01/83 to 06/30/83 37 + 4 570 + 200 Quarter 2 04/01/83 to 06/30/83 45 + 5 380 + 200 I
NN April 04/01/83 to 04/26/83 1.8 + 1.3 LT 300 L~* May 04/27/83 to 05/31/83 LT 2 630 + 200 June 06/01/83 to 06/30/83 6.6 + 1.5 410* + 200 Quarter 2 04/01/83 to 06/30/83 46 + 5 LT 300 ss July 07/01/83 to 07/31/83 2.9 + 1.3 LT 500
).
August 08/01/83 to 08/30/83 14 +
- 1.4 2 LT 300
\_ September 09/14/83 to 09/27/83 4.4 +
-+ 2 LT 300 Quarter 3 07/01/83 to 09/27/83 12 LT 300 r:*,
i NN July 07/01/83 to 07/31/83 LT 1. 8 LT 500 August 08/01/83 to 08/30/83 14 + 2 LT 300 r .,
September 09/14/83 to 09/27/83 1.3 + 1.0 LT 300 I . Quarter 3 07/01/83 to 09/27/83 10 + 2 LT 300
\
L~
ss October 09/28/83 to 10/26/83- 3.7 + 1.2 LT 300 November 10/27/83 to 11/29/83 4.3 + 1.2 LT 300 December 12/01/83 to 12/28/83 2.7 + 1.3 LT 300 Quarter 4 10/01/83 to 12/28/83 1.4 + 1.1 LT 300 NN October 09/28/83 to 10/26/83 1.4 + 1.2
- LT 300 November 10/27/83 to 11/29/83 1.6 + 1.1 LT 300 December 12/01/83 to 12/28/83 LT 1. 9 LT 300*
Quarter 4 10/01/83 to 12/28/83 LT 1. 8 LT .300 ss Annual Average+/- 2s 6.8 + 20 (2)
NN Annual Average+/- 2s 3.4 + 7.4 (2)
(1) L.T = Less Than (2) No average computed due to large number of LLDs.
36
1--. L.... [. _* .. (**-*-**1 .* . r-~ /*----,
l .. l. . *( C* *: : .*. : i l. ..... --.... ~.:i i,C: .. ./
Table 12 Determination of Gross Alpha, Gross Beta, and Tritium in Surface and He 11 ,Water, Semi-Annual Samples VEPCO REMP 1983 (Results in pCi/1 .:!:. 2s) 1.
I I
Sampling Analysis Surface Water ~Jell Water Gross. Be ta 1:
/.'. *\.
[.-* ' ..
Date Type cc ~/MR NNR SR ss HIR BC JMTN Average + 2s f
04/12/83 Gross Alpha LT 1.5(1) LT 1. 5 LT 3 9.6 + 2.9 LT 1. 9 LT 2 LT 3 LT 3 (2) rl Gross Beta 2.0 .! 1.2 1.4 .! 1.2 2.9 .! 2.3 6.4 + 2.5 2.8 .! 1.3 4.1 .! 1.4 6.4 + 1.!i 11 + 2 4.6 + 6 1*
- Tritium LT 300 LT 300 LT .300 LT 300 LT 300 LT 300 230 + 180 LT 300* (2) w
-..J 10/11/83 Gross Alpha 4.0 .! 2.7 LT 4 LT 2 LT 3 LT 2 LT 2 LT 3 LT 3 (2) i I
Gross Beta 23 + 6 7.5 + 4.6 4.0 + 2.7 4.5 .! 2.8 4.8 + 1.4 1.8 .:!:. 1.5 9.3 + 3.0 6.1 + 1.6 7.6 + 13
[>
Tritium LT 300 LT 300 LT 300 LT 300 560 + 170 LT 300 LT 300 LT 300 (2) 1.
Gross Beta Average.:!:. 2s 13 + 30 4.5 + 8.6 3.8 + 3.8 5.5 + 2.6 3.8 + 2.8 3.0 + 3.0 7.9 + 4.2 8.6 .:!:. 7.0 (2) !*
1*
i-*
1:.-
I:
,.i" I
[-..
(1) LT = Less than I.
I (2) No average computed due to large number of LLDs. 1*
t.
1*.*
I*.**--~-- 7 --,
l ... *__-.;
I l.
I r*-:--*-~
\,.-- ..... ;, L
- r-
.. ~- *****. ,J r--
~ ...... -
I
.... I r---*1
'***-'- -*-J i i.....
Month Location Date Ba-140 Co-58 Co-60 Cs-134 Cs-137 Fe-59 La-140 Mn-54 Nb-')5 Zn-65 Zr-95 K-40 (3) LT 5 ND( 2 )
January SI 01/19/83 LT 50(1) l.T 3 LT 3 LT 2 LT 2 LT 8 LT 40(3) LT 2 LT 3 LT 5 1983 IIIP 01/20/83 LT 50 LT 3 LT 3 LT 2 l,T 2 LT 10 LT 40( 3 ) LT 2 LT 3 LT 7 LT 6 ND NN 01/21/83 LT 60( 3 ) LT 3 LT 2 LT 2 LT 2 LT 8 LT 30( 3 ) LT 3 LT] LT 6 LT 6 ND CIIIC 01/211/83 LT 70 l.T 5 LT 5 LT 3 LT 3 LT 16 LT 50 LT 4 LT 6 LT 11 LT 9 ND Sll 01/26/8) LT 90(3) LT 5 LT 3 LT 4 LT 4 LT 11 LT 30 LT 4 LT 6 LT 8 LT 11 ND March SI 03/29/83 LT 16 LT 3 LT 6 LT 5 LT 4 LT 11 LT 14 LT 5 LT 4 LT 9 LT 7 ND HIP 03/2 3/83 LT 30 LT 6 LT 4 LT 5 LT 8 LT 10 T:r 14 l,T 5 LT 5 LT 11 LT 9 ND NN 03/23/83 LT 14 l.'f 6 LT 4 LT 4 LT 4 Lt 12 LT 8 LT 3 LT 4 LT 9 LT 7 ND CHIC 03/~8/8) LT 11 LT 3 LT 3 LT 3 LT 3 LT 6 l,T 6 LT] LT] LT 6 l,T 5 ND SD 03/28/83 LT )0 LT 7 LT 6 LT*6 LT 5 LT 12 LT 14 LT 5 LT 5 LT 14 LT 12 ND May SI 05/25/8) LT 13 LT 2 LT 2 I.T 2 LT 2 LT 6 LT 10 LT 2 LT 2 LT 4 LT 4 ND HIP 05/19/8) LT 30 LT 7 LT 6 LT 5 LT 5 LT 13 LT 15 LT 5 LT 6 LT 10 J.T 10 ND w NN 05/2 5/8) LT 15
- LT 3 LT 3 l,T 2 LT 2 I.T 5 LT 9 LT 2 LT 2 LT 5 LT 4 100 + 20 ro CHIC 05/25/8) LT 20 LT 4 LT 4 l.T 3 LT 4 LT 9 LT 12 LT 3 LT 4 LT 8 LT 7 ND Sll 05/2 7 /BJ LT 30 5.5 + 4.6 LT 6 9.8 + 3.5 11 + 4 LT 10 LT 14 LT 5 LT 6 LT 11 LT 10 ND (4)
July SI 07/19/8) LT 8 LT 13 LT 8 LT 7 LT 7 LT 40( 4 ) l,T 8 LT 9 LT 13 LT 18 LT 20 ND lllP 07 /13/83 LT 12 LT 15 LT 9 LT 8 LT 8 LT 40( 4 ) LT 12 LT 9 LT 15 LT 20 LT 30 ND NN 07 /13/83 LT 10 LT 14 l.T 8 LT 7 LT 7 LT 40 LT 10 LT 9 LT 14 LT 18 LT 20 Nll CIIIC 07/25/83 LT 8 LT 6 LT 4 LT 4 LT 4 LT 18 LT 8 l,T 4 LT 6 LT 9 LT 11 ND SD 07/19/83 LT 9 LT 6 LT 4 LT 4 LT 4 LT 20 LT 9 LT 4 LT 6 LT 9 LT 12 ND LT 200( 4 ) (4)
September SI 09/27 /83 LT 5 LT 3 LT 3 LT 3 LT 14 LT 110( 4 ) LT] LT 5 LT 6 LT 9 ND IIIP 09/27/83 LT 200( 4 ) LT 5 LT 3 LT J f,T 3 LT 14 LT 110( 4 ) LT J LT 5 LT 6 LT 9 ND NN 09/27/83 LT 400( 4 ) LT 5
- LT 3 LT 3 r:r 2 I.T 16 LT 200( 4 ) LT J LT 5 LT 7 LT 9 ND CIIIC 09/27 /83 LT 200( 4 ) LT 5 LT 3 l.T 3 LT 3 LT 14 LT 110( 4 ) LT] LT 5 LT 6 LT 9 ND SD 09/27/83 LT 400( 4 ) LT 6 LT] LT 3 LT 3 LT 18 LT 200 LT J LT 6 LT 8 LT 11 ND (4) LT 180( 4 )
Noven1ber SI 11/14/83 LT 300( 4 ) LT 4 LT 3 LT 2 LT 2 LT 15 LT 3 LT 4 LT 7 LT 8 ND lllP 11/14/83 LT 170 LT 3 LT l. 7 LT 1.4 3.7 + 0.8 LT 8 LT 100( 4 ) LT 1.5 LT J- LT 4 LT 5 ND NN 11 /ll, /83 LT 300( 4 ) LT 4 LT 3 LT 2 LT-2 LT 13 LT 130( 4 ) LT 3 LT 4 LT 6 LT 7 ND CIIIC l l/llo/83 LT 170( 4 ) LT 5 LT 4 LT 3 LT 3 LT 16 LT 100( 4 ) LT 3 LT 5 LT 9 LT 9 ND Sll 11/14/83 LT 400( 4 ) LT 6 LT 4 LT 3 LT 3 LT 19 LT 200( 4 ) LT 4 LT 7 LT 9 LT 12 ND
--(ff--I.T-= Less Than I
I I
(2) ND = Not Detected. I.I.Os fo K-40 not normally calculated for individual water sample.
(3) Lower sensitivity due to delay ln shipping.
(4) Lower sensitivity due to delay in counting.
I i
1:
J l
l
- - - ------~-----------~-----:___.* _._ - ----~~-._,_:_*_,_, __ **:*____ -_.,,._- - ........_,~,,.--~- --.~,. - "'--.. -~~-- __._ ._ '..J.'--~'-*,..*-
- l. ., __ , __ __,i_~..,-~._........, __ _:_..,_:.~.i..~----"'--'--*-
I' I'- J..,
i i
/ __ :
i ';
The bi~month1y samples of river water were composited on a semi-annual basis and analyzed for tritium. Low positive values of 200 and 290 pCi/1 were found in samples from the Chicahominy River (CKIC) control location. Values for .the indicator lotations ranged from 220 to 1500 pCi/1. These results are given on Table 14. During the preoperational i
J radiological environmental monitoring program, higher values of 4500 to 1' .*' 15000 pCi/1 were reported.
Monthly composites of river water are col"lected by the Commonwealth of Virginia. Results of gamma spectrometry on these samples are shown in Table 15. With four exceptions, all nuclides were below the detection limit. The February sample from the indicator location~ Surry
\i I
1._:
Discharge, contained 12 pCi/1 of Co-58 and 27 pCi/1 of Co-60. Co-60 was again detected in th~ November sample from the same location, at a level r-~.
- of 3.8 pCi/1, and was accompanied by 2.6 pCi/1 of Cs-137. These I ; nuclides may be due to plant operations.
u The monthly composites of river water are also analyzed for strontium-89 r~
l !
and -90. Results are shown on Table 16. (Ten of these analyses were
( : incomplete at the time of submission of the draft annual report. Low levels of Sr-90 (0.68 to 0.98 pCi/1) were found in samples from both the
- I indicator and control (Scotland Wharf) locations. During the
\ ~
preoperational. radiological environmental mbnitoring program for Surry Power Station, Sr-90 was occasionally found in James River water in the range 0.1 to 3.1 pCi/1.
In addition, strontium-89 was detected in the two samples collected in April. The levels observed were 1.0 + 0.6 and 1.6 + 1.1 pCi/1. These va 1ues for stronti um-89 may be art'ifacts of the calculation method.
Because this analysis is a function of the difference between two counts, normal statistical variations will occasionally lead to the r-** reporting of a false positive result for this isotope at values near its I detection limit. The analysis could not be confirmed because sufficient L* volume of sample no longer remained to match the original sensitivity 1imH.
r1 E. Aquatic Biota Marine biota can be sensitive indicators of radionuclide accumulation in the environment because of their ability to concentrate certain chemical elements wh.ich have radioactive isotopes. Gamma spectrometry was performed on bi-monthly samples of clams and oysters from the James River. The results are shown on Table 17. As expected, naturally occurring K-40 was the nuclide most frequently detected. In one sample from station LC, Co-60 was found at a low level of 18 pCi/kg (wet weight). All other nuclides were below the detection limit.
39
____._c - - **- *- ** --*..--**- ....._.-,.,.. --**, .... _.,--,.--..-..-...,.,.-*,*, . , . . . - . - ~ . . , , - - - ~ - - - .......* - * - - - - - - - - -
TABLE 14 Determination of Tritium in River Water - Semi-Annua 1 Composite VEPCO REMP 1983 r*- (Results om pCi /1 ~ 2s) j I
rr I:
(j l
Location Collection Period Tritium CHIC 1/24/83 to 5/28/83 290 + 200 HIP 1/20/83 to 5/19/83 240 + 200 NN 1/21/83 to 5/25/83 220 + 200 r*--* SD 1/26/83 to .5/27/83 380 + 20?
l !
it ____.
SI 1/19/83 to 5/25/83 LT- 300 l) r **- CHIC 7/25/83 to 11/14/83 200 + 190 HIP 7/13/83 to 11/14/83 380 190 iL ... NN 7/13/83 to 11/14/83 570 -++ 190 SD 7/19/83 t*o 11/14/83 1300 + 200
- SI 7/19/83 to 11/14/83 1500 + 200 I '
I l._.:
I '
r.;
l.J (1) LT= Less Than I \
i___:
40
i*
('
l..
- r:* c.,..~:i [~:J
- ~--:---*,
L~-,-~c! [__ . . ~:.J c*;:_J :--,-}
- ---*.......)
r-1 L.:_,j c=:-J r-1 ;-*** .. ****-,,
lc.":*.:.... :J r~,...--.-**.1 t I
- -*-*-* *.. 1
- ;,; .i ~.;:: .:J r:':~.-..:,1
~.: * **** ..! * .:.J [) ..'}] ~ Ti
- I.
,.l I.
l
,.1**
Table 15 t.*
rI"*...
Gamma Spectrometry of River Water {monthly composl tee) . f:*
i*
(Results in pCl/1 :!: 2s)
I 1.-..
I-.
Month Location Date Ba-140 Co-58 Co-60 Cs-134 Cs-137 Fe-59 La-140 Mn-54 Nb-95 Zn-65 Zr-95 K-40 r'.
---*--- ('
December Scotland Wh. 12/31 /83 LT 30(1) LT 1.9 LT 2 LT 1.5 LT 1.5 LT 6 LT 20< >
2 LT 1.8 LT 2 LT S LT 4 ND( 4 )' L 1982 Surry Dis. 12/31/83 LT 80( 2 ) LT 5 LT 4 LT 3 LT 4 LT 11 LT 40< 2>
LT 3 LT 5 LT 10 LT 9 ND 1.'t/*. .
January 1983 Scotland Wh.
Surry Dis.
Ol/3 l /83 01/31/.83 LT l 4 LT 40 LT 3 LT 7 LT 4 LT 7 LT 3 LT 7 LT 3 LT 7 LT 8 LT 16 LT 12 (2)
LT 16 LT 3 LT 6 LT 3 LT 7 LT 7 LT 15 LT S LT 13 ND ND ir February Scotland Wh.
Surry Dis.
02/28/83 02/28/83 LT 30 LT 30 LT 2 12 + 3 LT 2 27 + 3 LT 1. 7 LT 1. 9 LT 1.* 6 LT 2.
LT 7 I.T 9 LT 19 < )
LT 20< )
2 2
LT 1.8 LT 3 LT 3 LT 3 LT 4 LT 6 LT 4 LT S 53 + 15 ND r:
March Scotland Wh. 03/31/83 LT 30 LT 4 l.T 5 LT 4 LT 4 LT 9 LT 20< )
2 2
LT 4 LT 5 LT 10 LT 7 ND i
i Surry Dis. 03/31/83 LT 30 LT 5 LT 4 LT 4 LT 4 LT 10 LT 20< ) LT 4 LT 4 LT 9 LT 8 ND h I
April Scotland Wh. 04/30/83 LT 30 LT 3 LT 3 LT 3 LT 3 LT 7 LT 14 LT 3 LT 3 LT 6 LT 6 ND /*
1:.
Surry Dis. 04/30/83 I.T 19 LT 3 LT 3 LT 2 LT 2 I.T 7 LT 10 LT 2 LT 3 LT 5 LT 5 ND !:**
f.: ..
- 3 f.
May Scotland Wh. 06/21 /83 LT 20 LT 1.3 LT 2 LT 3 I.T 0.8 LT 5 LT 30< ) LT 1.0 LT 1.3 LT 3 LT 2 ND I-'
Surry Dis. 06/21/83 LT 30 LT 4 LT 3 LT 3 LT 3 LT 8 LT 15 LT 3 LT 3 l.T 7 LT 6 ND i June Scotland Wh. 07 /08/83 LT 11 LT 6 LT 4 LT 3 LT 4 LT 19 LT 11 LT 4 LT 6 LT 9 LT 11 ND I*
Surry Dis. 07 /08/83 LT 30 LT 7 LT 4 LT 4 LT .4 LT 20 LT 30 LT 4 LT 7 LT 10 LT 14 LT 60 lI
/.
t July Scotland Wh. 07/31/83 LT 150 < )
3 LT 3 LT 1.6 i,T 1.4 LT 1.5 LT 8 LT 10< 3 ) LT 1.5 LT 3 LT 3 LT 5 LT 20 r.:
Surry Dis. 07/31/83 LT 150 (3) LT 3 LT 1.6 LT 1.4 LT 1.5 LT 8 LT 70( 3 ) LT 1.5 LT 3 LT 3 LT 5 LT 20 [.
3 I'>
August Scotland Wh. 09/27 /83 LT 4 00 < ) LT 5 LT 3 I.T 2 LT 2 LT 13 LT 180(3) LT 3 LT 5 LT 6 LT 7 ND I .
!I:.
Surry Dis. 09/27/8) LT 190 (3) LT 5 LT 3 LT 3 LT 3 LT 15 LT llO())
3 LT 3 LT 5 LT 7 LT 8 ND c.
September Seo t land Wh. 10/18/83 LT 2'00 (3 ) LT 8 LT 4 LT 4 LT 3 LT 30 LT 120< > LT 4 LT 9 LT 11 LT 17 ND j?i Surry Dis. 10/18/83 LT 1200(3) 'LT 11 100< 3>
LT 6 LT 5 LT 5 LT 40 LT LT 6 LT 12 LT 14 LT 20 ND October Scotland Wh. 11/22/83 3
LT 100< > LT 4 LT 3 LT 3 LT 3 LT ll LT 60< )
3 f,-
LT 3 LT 4 LT 7 LT 7 ND Surry Dis. ll /2 2/83 3 LT 100< > LT 4 LT 3 LT 3 LT 3 LT 11 LT 60< )
3 I.T 3 LT 4 LT 7 LT 7 ND k:'
1***
1*,:* ..
[..i'*:
November Scotland Wh. 11 /30/83 LT 60(3) LT 3 LT 2 LT *2 LT 2 LT 8 LT 30( 3 ) LT 2 LT 3 LT 6 I.T 6 ND i Surry Dis. l l /30/83 LT 10< 3 ) LT 3 3.8 + 1.3 LT 1. 9 2.6 + 0.9 LT 7 LT 40(3) 1:r 1. 7 LT 3 LT 4 LT 5 ND v*
t*.
December Scotland Wh. 12/31 /83 LT 30 LT 3 LT 2 J.T 2 LT 2 I.T 7. LT 15 LT 2 LT 3 LT 5 LT S ND f'*.*:1*;
Surry Dis. 12/31/83 LT 30 LT 3 LT 2 LT 2 LT 2 J.T 7 LT 15 LT 2 LT 3 J.T 5 LT S ND r.:i.:
(I ) I.T
- Lens Thon (2)
(3)
Lower sensitivity due to delay in shipping. lv*,-
Lower sensitivity due to delay in counting (I,) NO ~ Not Detected. LLDs for K-~0 not nor11111l l.y calculated for indiv!duol water sample.
liJ, i.,* ,:..:,
l i:'
i** ,:t ,
n i*__ i i
Table 16 Strontium-89 and Strontium-90 in River Water VEPCO REMP -1983 (Results in pti/l + 2s Ij '**;
i
( __ .i r**
! **I Month Location Sampling Date St ront i um-89 St ront i um-90 I {
u December Surry Dis 12/31/82 LT 0.8(l) LT 0.8 1~82 Scotland Wh. 12/31/82 LT 0.9 LT 0.7 Fl I
L--' '
January Surry Dis 01/31/83 LT 0.7 LT 0.7
--"j 1983 Scotland Wh. 01/31/83 LT 0.7 LT 0.7
- r. .J February Surry Dis . 02/28/83 LT 1.0 LT 1.0 Scotland Wh. 02/28/83 LT 2.0 0.86 + 0.86 March Surry Dis 03/31/83 LT 3 LT 3 Scotland Wh. 03/31/83 LT 1.5 0.98 + 0.94 April Surry Dis 04/30/83 1.0 + 0.6 0.68 + 0.56 Scotland vJh. 04/30/83 1.6+1.l LT-1. 7 May Surry Dis Scotland Wh.
June Surry Dis Scotland Wh.
I
- July Surry Dis 07/31/83 LT 1.4 LT 1.2 L.J Scotland Wh. 07/31/83 LT 1.2 LT 0.8 August Surry Dis Scotland Wh.
September Surry Dis 10/18/83 LT 1.0 LT 1.5 r*;: Scotland Hh. 10/18/83 LT O. 7 LT 0.5 I,._......,
October Surry Dis
,-. Sc ot l an d Wh*
- ,l l-"
November Surry Dis.
Scotland Hh.
December Surry Dis.
( ~
Sc ot l an d Wh .
(1) LT = Less than f i r *~
~- 42
- * -~--,...-._.,.._ --.---- .. _...,.......-~-,.~~--,..---*, * * ,........,.........,._ ______ ---..---*---*****-.....,.--..------...---.-..-....----...-.-. ......- - - *
,-- .. - - ~ - - * - - - ~ - - -.-. - - . . - - - - . - - - - - * * - - - - - - - - - - - - - ~ .
- -*-:*1 [ ...
'i ' L , L. . . c_-...*, :*--*,
l :: . -* __ .j
'-*******; ~
,-':J L ..*..
... *- ~*-' ' ... J r-*--.--,
L:. * .... ; [::_-:-:J c=--=-J ::] *... **1 ... ....*1
) :-.** :J . ,,t L
I.,.
I (Page l Table t7 of 2)
~-
Gamma Spectrometry of Clams and Oysters ~*
VEPCO RllMP 1983 r-l (Results in pCl/kg (wet) :!:. 2e) f*
1:_
I*
I..'
Sampling Sample r* ::.:
c-** .
Month Location Date Type Co-58 Co-60 Cs-134 Cs-137 Fe-59 K-40 Mn-54 Zn-65 L:..
L;>:* .
January SD 01/20/83 Clam LT 50 (l) LT 30 LT 30 LT 30 LT 140 LT 200 LT 30 LT 70 if::*:-
))}' . *>
HIP 01/20/83 Clam LT 50 LT 30 LT 30 LT 30 LT 140 1200 + 200 LT 40 LT *00 LC 01/20/83 Clam LT 30 LT 20 LT 20 LT 18 LT 100 4600 + 1500 LT 20 LT 50 (i'>"*
CIIIC JMTN 01 /20/83 01/20/83 Clam Clam LT LT 20 30 LT LT 19 18 LT LT 15 20 LT LT 14 19 L'l' LT 90 90 4200 2300
+
+
1200 1100 LT LT 15 20 LT 40 LT 40 p:**
POS DWS 01/21/8) 01/21/83 Oyster Oyster LT LT 70 60 LT LT 50 40 LT LT 50 40 LT LT 50 40 LT LT 200 200 1300 + 300 850 + 270 LT LT 50 40 LT 130 LT 100 r1-*r.*
~\-
NN 01/23/83 Oyster LT 40 LT 40 LT 30 LT 30 LT 190 630 + 280 LT 30 LT 90 t'* .
r Harch SD 03/08/83 Cl.am LT 30 LT 20 LT 40 LT 40 LT 60 250 + 200 LT 40 LT 70 f 1111' 03/2 )/8) Clam LT 20 LT JO LT 20 LT )0 LT 60 440 + 180 LT 20 LT 50 f:~
of::>
LC CIIIC 0)/2)/8) 03/23/83 Clam Clam LT LT 1.\
30 18 LT
+ 11 30 LT LT l) 30 LT LT 13 30 LT LT 40 80 250. + 80 LT 300 LT LT 13 30 LT LT
)0 60 bi<
w JMTN 03/23/83 Clam LT 19 LT 20 LT 20 LT 19 LT 60 390 + 160 LT 20 LT 40 POS 03/23/83 Oyster LT 20 LT JO LT 20 LT 20 LT 60 670 + 220 LT 20 LT 50
[§J:;i DWS 03/23/83 Oyster LT 40 LT 30 LT 40 LT qQ LT 100 480 + 230 LT 30 LT 80 NN 03/07 /83 Oyster LT 30 LT 20 LT 19 LT 19 LT 80 570 + 190 LT 20 LT 5_0 May SD 05/03/83 Clam LT 20 LT 30 LT 20 LT 30 LT 60 li30 + 170 LT 20 LT 50 HIP 05/19/83 Clam LT 50 LT 60 LT 50 LT 50 LT 130 4200 + 500 LT 50 LT 90 LC 05/19/83 05/2 5/8)
Clam LT 50 LT 50 LT 50 LT 50 LT 120 1200 + 300 LT 40 LT 100 CIIIC Clam LT 50 LT 50 LT 40 LT 50 LT 130 LT 200 LT 40 LT 100 JMTN 05/25/83 Clam LT 50 LT 40 LT 40 LT 40 LT 120 LT 300 LT 40 LT 100 POS 05/25/83 Oyster LT 30 LT 40 LT 30 LT 40 LT 100 730 + 300 LT 30 LT 70 D\IS 05/25/83 Oyster LT 70 LT 70 LT 60 LT 70 LT 160 1700 + 600 LT 60 LT 130 NN 05/02/83 Oyster LT 18 LT 20 LT 19 LT 20 LT 50 570 + 150 LT 20 LT 40 July so 07/12/83 Clam LT 70 LT 90 LT 60 LT BO LT 180 LT 900 LT 60 LT 150 l!lP 07 /13/83 Cl.am LT 70 LT BO LT 60 LT 70 LT 200 LT 1200 LT 50 LT 150 LC 07 /13/83 Clam LT 80 LT 90 LT 60 LT 60 LT 200 LT llOO LT 50 LT 150 CHIC 07/25/83 Clam LT 90 l.T 110 I.T 70 LT 80 LT 250 LT 1400 LT 80 LT 160 V'/':
JMTN 07/13/8) Clam LT 70 LT 60 LT 70 LT 70 LT 200 LT 1000 LT 50 I.T 140 POS 07/13/8) Oyster LT 110 LT 100 LT 80 LT 100 LT 250 LT 1300 LT 90 LT 200 ll\lS 07/13/8) Oyster LT BO LT BO LT 70 LT 70 LT 260 1400 + 400 LT 70 LT 170 NN 07/11/83 Oyster J.T llO 1.T 100 LT 70 LT 70 LT 200 LT 1600 LT 90 LT 170 Note: See footnotes at end of table.
1----- - ,~~, i c;;.7:l F~~~.~J
(--*""7'-...
i
.j
\*.
I
- l. ... \,--*****-'*' t*-::.~__J :_._,__ j ~]
1.........,_._....:..:.J . .. *i . r- /*
~- [:'-
l
.I
.l l ~)-u l'
t; '
f: ..
J1 Jt: _-
Table 17 (.;:.
I (Page 2 of 2) i J Gamma Spectrometry of Clams and Oysters
-I VEPCO REHP 1983 i
(Results in pct/kg (wet) ~ 2s)
Sampling Sample Month Location Date Type Co-58 Co-60 Cs-134 Cs-137 Fe-59 K-40 Hn-54 Zn-65 Septembe'r SD 09/01/83 Clam LT 70 LT 70 LT 50 LT 60 LT 260 LT 700 LT 40 LT no HIP 09/27/83 Clam LT 70 LT 80 LT 50 LT 60 LT 200 LT 1000 LT 60 LT 120 LC 09/27/fl) Clnm LT 80 LT 60 LT 70 LT 90 LT 200 1100 + 500 LT 60 LT 180 CIIIC 09/2 7 /83 Clnm LT 60 LT 60 LT 60 LT 60 I.T 260 LT- 900 LT 60 LT 120 JMTN 09/27/83 Clam LT 60 LT 50 LT 40 LT 50 LT 180 1100 + 300 LT 40 LT 110 POS 09/27 /83 Oyster LT 50 LT 40 LT 40 LT 40 LT 140 LT- 700 LT 40 LT 90 D\./S 09/27/83 Oyster LT 80 LT 80 LT 80 LT 80 LT 260 LT 1200 LT 80 LT 150 NN 09/06/83 *oyster LT 70 LT 90 LT 70 LT 70 LT 200 LT 1200 LT 70 LT 140 November SD ll /02/83 clam LT 150( 2 ) LT 80 LT 70 LT 80 LT 400( 2 ) 2400 + 500 LT 80 LT 170 IIIP l l/14/fl3 Clam LT 60 LT 60 LT 50 LT 50 LT 150 790 + 240 LT 50 LT 100 LC 11/14/83 Clam LT 70 LT 60 LT 50 I.T 50 LT 150 1100 + 400 LT 50 LT 110 CIIIC 11/14/83 Clam LT 50 LT 40 LT JO LT 40 LT 120 LT 600 LT JO LT 80 JMTN
- 11/14/83 Clam LT 80 LT 70 LT 60 LT 70 LT 200 1100 + 500 LT 60 LT 160 POS 11/14/83* Oyster LT 70 LT 60 LT 40 LT 50 LT 140 760 + 350 LT 40 LT 100 Df!S ll/14/83 Oyster LT 90 LT 70 LT 70 LT 70 LT 200 LT 1000 LT 70 LT 170 NN 11/02/83 Oyster LT 90 LT* 90 LT 70 LT 70 LT 200 970 + 520 LT 70 LT 170 (1) LT
- Less Than (2) Lower sensltlvity due to delay in analysis.
I j
I I
.j.
I
't- ; ...
,_ {
f{
LJ n
~ ___ ;
Crabs were also collected during July, August, and September from the i--; Surry Discharge (SD) location and analyzed by gamma spectrometry.
I:
\._.'
Naturally occurring K-40 was found in all three samples, as shown on Table 18. The August sample contained 13 pCi/kg Cs-134 and 18 pCi/kg Cs-137 on a wet weight basis. These nuclides could be due to plant operations.
Eel and catfish were collected during February and August from the same SD location. The results of gamma spectrometry on these samples are shown on Table 19. K-40 was found in all four samples. The eel sample from February contained 100 pCi/kg Co-58 and 50 pCi/kg Co-~0. The r, catfish sample from February contained 6.7 pCi/kg Cs-134 and 12 pCi/kg L.J Cs-137. (All results are given on a wet weight basis.) Only the eel sample from August showed positive activity for any nuclide other than K-40; it contained 37 pCi/kg Cs-137. These nuclides could be due to
- .J plant operations, although the Cs-137 may also be attributable to global f' .__ .l fallout.
F. Sediment Sediment samples were collected twice during this program year. All samples were analyzed by gamma spectrometry: five locations were submitted in March and six 1oca ti ons in September. A number of man-made and naturally occurring radioisotopes were detected in these samples.
The isotope cesium-137 was detected in all samples, ranging from 56 to 2900 pCi/kg (dry). Cesium-134 was detected in 8 of 10 indicator samples ranging from 180 to 1300 pCi/kg (dry). Cobalt-60 was detected in 7 of 10 indicator samples. Its range was from 310 to 2400 pCi/kg (dry).
/ . Cobalt-58 was detected in one indicator sample at 1900 pCi/kg (dry).
/
l __.. The only man-made isotope in the single control sample collected was Cs-137. In addition to the man-made isotopes discussed above, a number of naturally occurring isotopes were observed in all samples.
iL-..J Potassium-40 was detected in all samples, ranging from 3000 to 17000 pCi/kg (dry)~ An assortment of daughters from the uranium and thorium chains were also detected in all of the samples. These generally ranged from 97 to 1100 pCi/kg (dry) between the different samples. The observed results were internally consistent for any .given sample.
r",'
I I G. Waterfowl i
A single waterfowl sample was collected for 198j from Hag Island Reserve (HIR) . . This sample was analyzed by gamma spectrometry, the results or which are shown in Table 21. The man-made isotope cesium-137 was detected at a value of 4.7 pci/kg (wet). The naturally occurring isotopes K-40 and Be-7 were also detected at 420 and 42 pci/kg (wet),
respectively. The values for the K-40 was not unexpected nor unusual.
The Be-7 value is attributable to the probable ingestion of leafy vegetation or sediment which may contain this particular isotope due *to-its production in the upper atmosphere and subsequent deposition_ on vegetation and soi 1.
45
**----*-------------*~---- -- " .. ~
[ --- *'
, ... 1*-0*~.--, :* --:-*-~-1 ~
I. L.*.<*---j L ...,*.. :! l..:_:., ..... J i
ll Table 18 Gamma-Spectrometry of Crabs VEPCO REMP 1983 I
(Results in Units of pCi/kg (wet) + 2s) l I
I i Sampling I
Month Location *nate Co-58 Co-60 Cs-134 Cs-137 Fe-59 K-40 Mn-54 Zn-65 I!
II I
! July SD 07 /19/83 LT LT 40 LT. 30 LT 120 3100 + 400 LT 40 LT 80 i
I
- - August SD 08/25/83 LT 19 LT 11 13 + 5( 2 ) 18 + 5 LT 60 1700 + 200. LT 11 LT 30 I
I September SD 09/24/83 LT 70 LT 60 LT 60 LT 60 LT 200 25(?0 + 600 LT 60 LT 110 i
,i,.
en (1) LT= Less Than (2) Positive activity confirmed by recount.
\~~--.:*. . :. ~ ~:.~-~-.l ."'-~~J L~~ ~, ~ t<-
~-*. _,' .. I _l L:: : ....... J l. ...: ... J i:.. _** ... J (._"~--J Table 19 Gamma Spectrometry of Fish VEPCO REMP-1983 (Results in pCi/kg (wet)+/-. 2s)
Sampling Sample Month, Location Date Type Co-58 co~6o Cs-134 Cs-137 Fe-59 K-40 Mn-54 Zn-65 February SD 02/02/83 Eel 100 + 30 50 + 17 LT 30(l) LT 30 LT 130 690 + 150 LT 30 LT 60 SD 02/02/83 Catfish LT 3 LT 2 6.7 + 1.0 12 + 2 LT 15 1300 + 200 LT 2 LT 7 I
I I
I J August SD 08/26/83 Catfish LT 60 LT 50 LT 40. LT 40 LT 200 1300 -+ 300 LT 40 LT 90 l
.t> SD 08/17/83 Eel LT 40 LT 20 LT 20 37 + 13 LT 150 940 + 270 LT 20 LT 60
! -...J j
l I
l l
I 1*
I (1) LT - Less Than
r*--1 c-_ - ---.
,,I* -~
L .. _ - ....'J L** _.,* *. *.,.'
i J * ~ L ..
l r/
TABLE 20 * .Jr.
l Gamma Spectrometry of Sediment f.:-,
I*'.
VEl'CO REHP - 1983 i' j (Results in pCi/kg (dry)+/- 2s) f,*.
r ..
- J
[' ':
i Loca- Sampling L I
.) tion Date Bi-214 Cs-134 Cs-137 K:-40 Pb-212 Pb-214 Ra-226 Tl-208 Co-60 Others f .:/*.
-I
.j
- 1 SI 03/2 3/83 1200 + 400 470 + 150 1500 + 300 16000 + 3000 990 + 310 990 + 390 1100 + 400 ND(l) ND ND
[:}?
j SD 03/23/83 1100 + 40'0 1300 + 300 2300 + 300 15000 + 3000 820 + 280 630 + 360 860 + 400 880 + 480 930 + 260 ND fjg r :~ ,: --
j
'j Ill p . 03/23/83 1000 + 200 510 + 90 1100 + 200 17000 + 2000 850 + 190 970 + 220 1000 + 200 1200 + 300 420 + 120 Ac-228@ [*; ~(
llOO + 300
- l
..I, POS 03/23/83 850 + 200 180 + so 720 + 140 17000 + 2000 1000 + 200 890 + 190 870 + 200 990 + 2'10 370 + llO Ac-228@
780 + 310
-.,'l NN 03/23/83 ND LT 50( 2 ) 56 + 34 3000 + 700 ND ND ND 97 + 83 ND ND I
- l i CIIIC 09/27 /83 1200 + 200 LT 140 860 + 110 17000 + 2000 1200 + 200 1300 + 200 1300 + 200 1300 + 200 ND n1-212 @
- I ,i's 1100 + 800
- 1 OJ i Ac-228@
j 1400 + 300 J [:*,::
1 I SI 09/27/83 940 + 220 420 +.100 1300 + 200 16000 + 2000 950 + 240 1100 + 200 1000 + 200 1000 + 300 450 + 160 Ac-228@
750 + 400 r:..
I **
I SD 09/27 /83 1100 + 200 1200 + 200 2900 + 300 17000 + 2000 970 + 240 1000 + 200 1100 + 200 llOO + 400 2400 + 300 co~58@
i,-*
r*.
1I 1900 + 200 i*'\
i Ac-228@
! 790 + 480 1
I IIIP 09/27/83 1200 + 300 190 + 70 690 + 150 11000 + 2000 810 + 200 1400 + 300 1300 + 300 1300 + 300 450 + 120 ND I.
i POS 09/27/83 1000 + 300 200 + 80 980 + 160 17000 + 3000 940 + 220 1000 + 200 1000 + 300 1200 + 300 310 + 130 Ac-228@
[/
- l}\\
,J 610 + 400
- J NN 09/27/83 HlO + 130 LT 140 260 + 80 14000 + 2000 500 + 120 690 + 150 750 + 170 720 + 200 ND Ac-228 @
690 + 260 ii
- 1 (I ) N>> d Not-detected
.I (2) LT= Less than J
'.j
.I j
'l 1.J i ____!]
. L-
'1.. ........ *** ~--J, c,----i --*-**.. .-. '1*
. -,..-.-.! -.- .. I]
l
- i._ __ .... * . .,I _
Table 21 Gamma Spectrometry of Fowl VEPCO REMP-1983 (Results in pCi/kg (wet) + 2s)
Sampling Month Location Date Be-7 Co-58 Co-60 Cs-134 Cs-137 Fe-59 K-40 Mn-54 I
j l February HIR 02/15/83 42 + 21 LT 4(l) LT 4 LT 3 4.7 + i.9 LT 18 420 + 50 LT 3 LT 8 I
I i
j J
,i,.
I \!)
I l
I*
I 1
l
\
J j
1 (1) LT= Less Than I
1 I
i 1*
I.
i r
I i
H. Food Products n
! A total of seven food products were collected for analysis during this program year. Two samples each of corn and peanuts were submitted for analysis as ,,.,ell as individual samples of cabbage, kale .and soybeans.
All samples were analyzed by gamma spectrometry as well as for strontium-89 and -90.
No man-made .radioisotopes were detected in any of the sample$. The naturally occurring isotope potassium-40 was observed in all the samples. The observed values (2300 to 5600 pCi/Kg (wet)) were within nLJ the expected range of normal distribution.
I. Soil Soil samples were collected from six locations during this program year.
All samples were analyzed by gamma spectrometry *. The only man-made radioisotope detected was cesium-137. This isotope was detected in all r.
but one sample, ranging from 270 to 830 pCi/Kg(dry). In addition, a number of naturally occurring isotopes were observed in all samples
- Potassium-40 was detected in all samples, ranging from 2100 to 15000 pCi/Kg(dry). An assortment of daughters from the uranium and thorium chains were also detected in all of the samples. These generally ranged from 100 to 1700 pCi/Kg(dry) between the different samples.* The f ',, observed results were internally consistent for any given sample.
t . Finally, one sample contained detectable activity of beryllium-? at a Li level of 520 pCi/Kg(dry). This is a naturally occurring radioisotope which is produced in the upper atmosphere. It is often detected in air particulate samples, and quite commonly seen on leafy vegetation and in soil samples.
L.
1, u
,-~
\, :
\-,*,
50 f.'.,
n.
I ,
r ir __ *'
Table 22 r---,
Gamma Spectrometry of Vegetation
\___ :
(Results in Units of pCi/kg (wet)*+/- 2s)
.. (71 j.- i
~.J Sample Sampling nj -;
Location Type Date Cs-134 Cs-137 I-131 K-40 t .
r-**
I!
I -
- Carter's Cabbage 07/12/83 LT 30(1) LT 30 LT 40
- 3100 + 400 Grove
- 1**...,
I I.
( ___ ., Poole Kale 10/18/83 LT 11 LT 13 LT 30 3000 + 300 Gardens r*~..
\ 1 Brock Farm Peanuts 11/23/83 LT 11 LT. 15 LT 30 4400 + 500
'-" Brock Farm Corn 11/23/83 LT 13 LT 15 LT 40 2300 + 300 r*-., Slade Farm Peanuts 11/23/83 LT 14 LT 16 LT 40 4900 + 500
!1 i Slade Farm Corn 11/23/83 LT 7 LT 8 LT 19 2100 + 300 L)
Brock Farm Soybeans 11/29/83 LT 12 LT 14 LT 20 5600 + 600 Ct
(_.,t iI ,
~.)
'1 I
L_
r*;
r' __'.
(1) LT = Less Than r-:
I Lt
( ~ .,.
\
(
i
'*--~
51 I-,
. - - ~ - - - - . - - - . . - - * . * - - - ~ ~ - .... '* .-- : ~ ,* ,_*,.:**** *....,. .:r, ~ , . .- .... -:*.~'.*, *;,*.,-... *::. ~ .. ,~~::0.. -**:;:, *.,, -,-., . - -.- - -* **. : # --::----:::--=-~-.-;'- . -..---::--* .~
- F; Table 23 Strontium-89 and Strontium-90 in Vegetation VEPCO REMP 1983 (Results in Units of pCi/kg (wet)+ 2s) u r:'"!
Sample Sampling Location Type Date Strontium-89 Strontium-90 Carter's Cabbage 07/12/83 (1) (1) r
,,i __:
Grove Poole Kale 10/18/83 Gardens Brook Farm Peanuts 11/23/83 Brock Farm Corn 11/23/83 r~
I . Slade Farm Peanuts 11/23/83 I ;
t__; Slade Farm Corn 11/23/83 I~'
I l... J
- Brock Farm Soybeans 11/28/83 I ,
L.:
(1) Sample destroyed in analysis.
r-;
LJ p
- .)
52
~ --*--~ ~i I._ .. - _;
l..
c*-~7 l.. -~---,.*J
- --:-- '\
...... . , )
t ' . -....,___ !
.r..,...._..._..
'\..~.c.:...1
---~~
L. ... .,.. ,
TABLE 24 Gamma Spectrometry of Soil VEPCO REMP 1983 (Results in pCi/kg (dry}:!:_ 2s}
Location( 3 } Ac-228 81-214 Cs-134 Cs-137 J<-40 Pb-212 Pb-214 Ra-226 Tl-208 Others ss 1100 + ioo 1300 + 200 LT 140(l} 470 + 70 15000 + 2000 1100 + 200 1700 + 200 1500 + 200 1600 + 200 Be-7@
540 + 120 Di-212 @
1700 + 700 BC ND( 2 } 580 + 110 LT 80 720 + 80 5200 + 900 310 + 50 560 + 100 570 + 100 450 + 120 ND ALL ND 270 + 190 LT 150 270 + 90 2100 + 800 100 + 90 620 + 190 450 + 190 410 + 210 ND CP 470 + 210 540 + 140 LT 110 830 + 100 7500 + 1500 550 + 70 790 + 140 670 + 140 550 + 180 ND DOW 1',00 + 300 llOO + 200 LT 140 320 + 80 9000 + 1600 720 + 90 1100 + 200 llOO + 200 910 + 230 ND FE 820 + 250 910 + 160 LT 120 LT 120 11000 + 2000 670 + 80 890 + 150 900 + 160 680 + 190 ND tn w
(1) LT= Less Than (2) ND= Not Detected
(]) All samples collected on 17 August 1983
I .i u
n
\.J J. Direct Radiation
- . \
I ,
l . ..J Environmental radiation dose rates determined by thermoluminescent dosimeters (TLDs) are given in Table 25. TLD badges of four readout r:: areas each were deployed quarterly at each location. The mean values of I ' four readings (corrected individually for response to a known dose and i* j for in-transit exposure) are reported in this table, unless indicated otherwise. A description of the TLD system used is contained in r--,'
Appendix C.
I:
- ~.-1 ..
A statistical summary of the 1983 data is included in Table 26.
Individual measurements of external radiation levels in the environs of the Surry site ranged from 0.11 to 0.82 mR/day. Annual: levels ranged from 47 to 130 mR/year. The values obtained for location 00 (an onsite lead pig controll and location 01 (an onsite station near a waste holding area) are not included in the statistical summaries. Exposures at the onsite location 01 were elevated throughout the year.
TLD results from the first and second quarter indicated an anomalous exposure to a low energy radiation source. Each TLD placed in the field has four separate readout areas, each of which has a different degree of r1' L--'
shielding. This permits a *rudimentary assessment of the energy of exposure *within certain limits. On initial review, the data exhibited wider variations among the four readout areas-of individual badges than
," was usual. Closer inspection revealed a trend wherein the least
( \
shielded areas showed the highest exposures, although this was by no u means universal. Using a method supplied by the TLD and badge manufacturer, the readings were corrected for the overresponse to low energy radiation. Not all the values could be corrected in this way.
There were many instances of inversions (higher response from the more heavily shielded area), tight initial variations, and outliers. Each of these conditions can result in sets of readings which diverge on application of the correction curves. Fpr Table 25, the corrected readings were reported if the application *of the correction curves to any individual station resulted in a new data set which uniformly converged with respect to the internal variation of the four readings.
Sets for which no low energy corrections were applied are indicated in the data table. Despite the corrections which were applied, the data for the first and second quarters still shows a high variability. The results seem to indicate an non-uniform exposure to a source of low energy radiation. This anomalous pattern of results has been observed previously in other programs and has been attributed to accidental shipping or storage in proximity to a source or intentional x-raying enroute for shipping inspection. In any case, plant releases are not implicated because of the absence of any rational pattern, in particular, the high exposure exhibited by the control locations.
r ...
54
\
....i,
n Table 25 (Page l of 2)
Direct Radiation--Thermoluminescent Dosimetry VEPCO REMP 1983 (Results in mR/day :!:_ 2s)
STATION NO. FIRST QUARTER SECOND QUARTER THIRD QUARTER FOU,RTH QUARTER AVERAGE + 2s r*~
I j I, l
- .. .J Start: 011383 Start: 040783 'Start: 071383 Start: 101183 Stop: 040783 Stop: 071383 Stop: 101183 Stop: 010684 1/
' I 00(12) .09 :!:_ .01 (l) .07 + .01 .09 + .01< 8 ) .as .:_ ,01 (ll) 0.08 + 0.01 L,
01(12) 2,4 + .3(l)(*) 6.3 +/-. .7(S)(*) 4.1 + ,3 2.9 + ,1 3.9 + 1.7 02 .24 + .03 ,23 +/-_ .03 .29 .:_ .02 <3 ) .26 + .a/11) 0.26 + 0.03 03 .19 + .03(l) .11 + .02(S) .12 +
- 01 (S) .11 + .01 (11) 0.13 + 0.04 04 .23 + .08< 1 ) (6) .17 + .02-< 8 ) .20 + .01< 11 ) 0.20 +/-_ 0.03 05 .29 + .03 .17 + .02 ,19 + .02 ( 3 ) .19 .:_ .01< 11 ) 0.21 + a.as
.04< 5 ) .o/8) .01< 11 >
L, 06 07
.28
.26
+
.02(1)
.03(l)
,25
.21
+/-_
+/-. .04 (S)
.23 +
.22 +
- 01 (S)
.22 .:_
(6) 0,25 0.23
.:_ 0.03
+/-_ 0.03 08 .36 :!:_ .04 (l) .22 + ,03< 5 ) .20 + .01< 3 ) (6) Q.26 + 0.09 09 .36 :t .as <1 ) .23 +/-. .03 (S) .22 .:_ .01 (S) .19 +/-. .01< 11 ) 0.2s .:. a.as 10 .27 +/-_ .* 04< 2 > .77 + .09< 5 )(*) .21 .:_ .02 <3 ) .20 +/-. .01 (ll) 0.36 + 0.27
- 11 ,32 +/-_ .04< 2 ) .31 +/-_ .04 (S) .21 + .02< 8 ) .22 .:_ .01 (ll) 0,27 + 0.06 12 .26 +/-_ ,04< 3 ) .14 +/-_ ,02 .20 +/-_ .01< 8 ) .21 :t_ .02< 11 ) 0.20 + a.as 13 .26 + ,04< 3 ) .14 + .02 .23 .:_ , 02 ( 9 ) .27 +/-. .04(ll) 0.23 + 0.06 14 .38 .:_ ,04< 3 ) ,16 .:!: ,02 * .28 .:. .o/9) (10) 0.27 .:_ 0.11 15 * .30 .:_ .03< 2 > .11 + .02< 5 ) .26 .:_ .02 <9 ) (10) 0.24 .:_ 0.07 16 .21 :!:_ ,03< 2 > .26 .:!: ,03< 5 ) .26 .:_ ,02 <9 ) ,21 :t_ .01< 11 ) 0.24 .:_ Q,03 17 ,16 :!: ,05< 4 ) .62 + ,32< 7 ) .2*4 :!:_ .01 ( 9 ) .25 + .02(1l) 0.32 + 0.21 18 .19 :!:_ .02< 4 ) .27 .:!: .03< 5 ) .18 + .01< 9 ) .15 +/-. .01 (ll) 0.20 +/-. a.as l.. 19 .17 .:_ .02 .13 + .02 .18 :!:_ .02 .19 .:!:
+
.01 0.17 .:_
+
0.03 20 .20 .:_ .03 .12 + ,02 .17 :!:_ .01 .15 .01 0,16 0.03 21 .19 .:_ .02 .15 .:!: .02 .19 + .03 .17 .:!: .01 0.18 + 0.02 22 .47 + .as .13 + .02 .18 :!:_ .02 .16 .:!: .01 0.23 + 0.16 23 .26 .:_ ,03<*) .16 + .02 .19 :!:_ .03 , 15 :t_ .01 0.19 + a.as
(
( ;
' 24 .17 :!: .02 .23 + ,04<*) .20 + .03 .18 .:!: .01 0.20 +/-. 0.03
- __: 25 .17 +/-_ .02 .13 + ,02 .20 :!:_ .02 .17 + .01 0.17 + C.03 26 .16 + .03 .29 + ,03<*) .20 + .02 .16 + .01 0.20 +/-. 0.06 27 .47 +/-. .2s<*) ,14 + .02 .18 +/-_ .02 .16 +/-. .01 0.24 +/-. 0.16 Li 28 .22 +/-. .03 .14 +/-_ .02 .20 +/-. .02 ,17 .:!: .01 0.18 +/-. 0.03 29 .22 + .03 (*) .12 .:!: .02 .18 +/-_ .02 .15- +/-_ .01 0.17 + 0.04
["") 30 .15 +/-. .02 .12 .:!: .02 .20 + .01 .17 !. .01 0.16 .:!: Q,03 I ;
I '
Note: See footnotes at end of table, 55
r
. .:,t'""
n ji(
l.'.C:!
'r:I.
I r.
Table 25 (Page 2 of 2) r
/ ; Direct Radiation-Thermoluminescent Dosimetry 1, **** :
VEPCO REMP 1983 1*. (Results in mR/day .!. 2s)
L.
STATION NO. FIRST QUARTER SECOND QUARTER THIRD QUARTER FOURTH QUARTER AVERAGE + 2s Start: 011383 Start: 040783 Start: 071383 . Start: 101183 Stop: 040783 Stop: 071300 Stop: 101183 Stop: 010684 f:1 31 + .02 .15 .02 + + 0.01 II_ __;i .15 .!. .18 .02 .17
-+ .01 0.16 32 .28 .!. .03 .16 .!. .02 .18
-+ .02 .19 + .01 0.20 + o.os 33 .21 .!.
- 03 <3 ) .17 .!. .02 .21 .!. .02 .24 + .02 0.21 + 0.03 34 .22 +
- 03 <3 ) .17 .!. .02 .21 + .02 .21 0.20 + 0.02
.!. .01
- 02 <3 ) + .01 35 .21
-+ .19 .!. .02 .24 .46 + .17 0.28 + 0.13
- 05 <3 )
r' 36 .46 + .20
-+ .02 .24 + .01 .26
-+ .01 0.29 + o."t2 37 .82 + .22< 3 )(*) .18 .02 .20 .03 .20 + .01 0.35 0.31
'i : - .!. .!. .!.
I . .!
38 .26 .!.
- 09 <3 ) .26 .!. .08 .27 .!. .03 .28 .01 0.27 + 0.01
. (3)(*)
39 .43 .!. .05 .19 .!. .03 .20 .!. .02 .20 .!. .01 0.25 + 0.12 40 .74 .!. .23< 3 ) .12 .!. .02 .16 + .02 .15 .!. .01 0.29 + 0.30 41 .31 .04 <3 ) .16 .02 .22 + 0.06
.!. .!. .!. .03 .24 .!. .02 0.23 42 .52 .!. . 06 <3 ) .18 + .02 .19 + .01 .24 + .02 0.28 + 0.16 43 .55 .44( 3 )(*) .14 .02 .16 .02 .22 + .02 0.27 0.19
.!. .!. .!. -+
INDICATOR
+
AVERAGE
-+ 2s 0.29 0.14 0.21 .!. 0.13 0.21 + 0.03 0.20
-+ 0.06 CONTROL r--"
+ 2s f '
i I AVERAGE 0.58
-+ 0.22 0.15
-+ .OS 0.18 .!. 0.03 0.18
-+ 0.04
....-1
[,__j',
- COMMENTS: (l) Exposure period was 1-14-83 to 4-11-83.
(2) ~xposure period was 1-13-83 to 4-11-83.
(3) Exposure period was 1-14-83 to 4-07-83.
(4) Exposure period was 1-13-83 to 4-12-83.
(5) Exposure perioa was 4-11-83 to 7-13-83.
(6) Missing at time of pickup in field.
(7) Exposure period was 4-12-83 to 7-14-83.
(8) Exposure period was 07-13-83 to 10-10-83.
(9) Exposure period was 07-13-82 to 09-28-83.
(10) Lost in transit.
(11) Exposure period was 10-10-83 to 01-06-84 (12) Not included in vertical averages.
(*) No low energy correction applied.
r **~-.
I;.,
- ~---
56
r-**--i l, ..*,*-** _J Pl t'_:__~,_J c:-J TABLE 26
SUMMARY
OF DATA FOR THE SURRY NPS RADJOLOGICAL ENVIRONMENTAL MONITORING PROGRAM - 1983 (Sheet 1 OF 7)
N11r.ie of Facility: SURRY Nuclear Power Station Docket Nos. 5-200; 50-281 Location of Facility: SURRY County, Virginia Reporting Period: 10 January - 31 December 1983 Medium or Pathway Type and Location with Highest Annua 1 Mean Sampled Total Number Lo~ier A11 Indicator Control LocaH~ns (Uni ts of of Analyses Limit of Locations Name, Di stance Mean ( f) ( 2 l Mean (fl Measurement) Performed Detection (1) Mean (f) (Range) and Direction (Range) (Range)
Air 1o9ine - 1-131 - 423 0.07 LLD L,LD (pCi/m)
Ai rl.Jorne Gross Beta - 422 10 15.0 (285/369) FE 17 (38/52) 19 (45/53)
Pa rti cul ates {3.2-78) (3.8-72) (6.3-40)
(lE-03 pCi/rn3J Gross Alpha - 422 3.7 (212/369) DOH 4.5 (28/53) 4.2 (29/53) 1.2-20 (l.4-20) (2.0-11)
Gamma Spec - 32 Be-7 64 (26/28) DOH/FE 72 (4/4)/72 (4/4) 73 (3/4)
(32-100) . (53-100/46-97) (38-110)
Ce-141 LLD LLD Cs-134 0.05 3.8 (2/28) ss 3.8 (2/4) LLD (2.2-5.4) (2.2-5.4)
Cs-137 0.06 6. 7 (4/28) BC 2.0 (1/4) (3) LLD (2.0-14) (2.0-2.0)
IJb-95 LLD LLD Zr-95 LLD LLD Milk Gamma Spec - 58 (pCi /l) K-40
- 1300 (47/47) LEE HALL 1400 (12/12) 1400 (11/11)
(l 000-1800) (1200-1800) (1300-1700)
Cs-137 18 8.4 (12/58) JDKS 14 (4/11) LLD (l.4-43) (2.5-43)
Cs-134 15 10 (l/50) EPPS 10 (1/12) LLD (10-10) (10-10)
- Ba-140 60 LLD LLD La-140 15 LLD LLD I-131 - 59 l LLD LLU Sr 58 *5 2.9 (1/58) CP 2.9 (1/12) LLD (2.9-2.9) (2.9-2.9)
Sr-90 -58 l 2.9 (3/48) JDKS 3.5 (l/12) 2.3 (2/10)
(2.2-3.5) (3.5-3.5) (l. 6-2. 9)
Ca-60 1350 (48/48) JDKS 1400 (12/12) 1500 (12/12)
(890-2000) (l 000-1600) (1300-1890)
NOTE: See footnote at end of table.
r---*- .. r--, l ......J l..._....* ..J I *. -...* ;
TABLE 26
SUMMARY
OF DATA FOR THE SURRY NPS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM - 1983 (Sheet 2 OF 7)
Name of Facility; SURRY Nuclear Power Station Docket Nos. 5-280; 50-281 Location of Facility: SURRY County, Virginia Reporting Period: 10 January - 31 December 1983 Medium 'or Pathway Type and Location with Highest Annual Mean Sampled Total Number Lo~1er A11 I ndi ca tor Control LocarHns (Units of of Analyses Limit of Locations Name, Di stance Mean (fl ( 2 ) Mean { f)
Measurement) Performed Detection (l) Hean (fl (Range) and Direction (Range) (Range)
Precipitation Gross Beta 4 6.8 {12/12/) ss 6.8 {12/12) 3.8 (9/12)
(pCi/l) {l. 5-37) {l. 5-37) (1.3-14)
Gamma Spec Cs-134 15 LLD LLD Cs-137 18 LLD LLD lJ1 co Tritium-30 2000 660 (2/12) ss 660 {2/12) 410 {3/12)
{570-750) (570-750) (190-630)
River Water Gamma Spec - 26 Monthly Co-58 15 12 {l/13) SURRY DISCIIARGE 12 (1/13) LLD (pCi /l) {12-12) (12-12)
Co-60 15 15 {2/13) SURRY DISCHARGE 15 {2/13) LLD
{3. 8-27) (3.8-27)
Ba-140 60 LLD LLD Cs-134 15 LLD LLD Cs-137 18 2.6 {1/13) SURRY DISCHARGE 2.6 (1/13) LLD
{2.6-2.6) (2.6-2.6)
K-40 53 (1/13) SURRY DISCHARGE 53 (1/13) LLD (53-53) (53-53)
Sr 13
- 5 1.0 (1/13) SURRY DI SCIIARGE 1.0 (1/13) 1.6 (1/13)
(1.0-1.0) (1.0-1.0) (1.6-1.6)
Sr 13 .68 (1/13) SURRY DISCHARGE
- 68 ( 1 /13)
- 92 ( 2 /13)
{.68-.68) (.68-.68) (. 86-. 98)
Fe-59 30 LLD LLD La-140 15 LLD LLD Mn-54 15 LLD LLD Nb-95 15 LLD LLD Zn-65 30 LLD LLD Zr-95 30 LLD LLD NOTE: See footnote at ehd of table.
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TABLE 26
SUMMARY
OF DATA FOR THE SURRY NPS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM - 1983 (Sheet 3 OF 7) .
Name of Facility: SURRY Nuclear Power Station Docket Nos. 5-280; 50-281 Location of Facility: SURRY County, Virginia Reporting Period: 10 January - 31 December 1983 Medi um or Pathway Type and Location with Highest Annual Mean Sampled To'ta l Number Lo~1er All Indicator Control Locaf~~ns (Units of of Analyses Limit of Locations Name, Di stance Mean ( f) ( 2 l Mean ( fl Measure men tl Performed Detection (l) Mean (fl (Range) and Direction (Range) (Range)
Bi-Monthly Gamma Spec - 30 River Hater Co-58 15 5.5 (1/30) SD 5.5 (1/6) LLD (pCi /1) (5. 5-5. 5) (5.5-5.5)
Cs-134 9.8 (1/30) SD 9.8 (1/6) LLD (9.8~9.B) (9.B-9.B)
Cs-137 18 7.4 (2/30) SD 11 (1/6) LLD Ul (3. 7-11) (11-11)
\.D Tritium - 10 2000 660 (7/8) SI 1500 (1/2) 250 (2/2)
(220-1500) (1500-1500) (200-290)
Ba-140 60 LLD .HD
. Fe-59 30 LLD LLD La-140 15 LLD LLD Mn-54 15 LLD LLD Nb-95 I Zn-65 Zr-95 15 30 30 LLD LLD LLD LLD LLD LLD Surface Hater Gross Beta - 8 4 6.5 (8/8) cc 13 (2/2) no control (pCi /1) (1.4-23) (2.0-23)
Gross*Alpha - 8 6.8 (2/8) SR 9.6 (1/2)
(4. 0-9. 6) (9.6-9.6)
- I ~ ** .
- 1.- ..:** :,
1** .*;
l l
1*
I/ell Hater (pCi/1)
Gross Beta - 8 Gross Alpha - !l Tritium - 30 2000 4 5.8 (8/8)
(1.8-Jl)
LLD 400 (2/8)
(230-560)
JMTN ss 8.6 (2/2)
(6.1-11) 560 (1/2)
(560-560) no control f)i
- .;..,/'*1 I
I1 NOTE: See footnote at ~nd of table.
1 iI i.
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j l
TABLE 26 SUHHARY OF DATA FOR THE SURRY NPS RADIOLOGICAL ENVIRONMENTAL HONITORING PROGRAM - 1983 (Sheet 4 OF 7)
Name of Facility: SURRY Nuclear Power Station Docket Nos. 5-280; 50-281 Location of Facility: SURRY County, Virginia Reporting Period: 10 January - 31 December 1983 Medium or Pathway Type and Location with Highest Annual Mean Sampled Total Number Lo~1er Al 1 Indicator Control LocaH?ns (Units of 'of Analyses Limit of (l) Locations Name, Dis ta nee
- Mean (fl (2 ) Mean (fl Measurement) Performed De tee ti on Mean (f) (Range) and Direction (Range) (Range)
Clan,s Gamma Spec - 30 (pCi/kg (wet)) K-40 1400 (16/24) HIP 1700 (4/6) 4200 (2/6)
(2 50-4600) . (440-4200) (4200-4200)
Mn-54 130 LLD LLD Fe-59 260 LLD LLD Co-58,60 130 LLD LLD Zn-65 260 LLD LLD Cs-134 130 LLD LLD Cs-137 150 LLD LLD
.j
- i Oysters Gamma Spec - 18 J (pCi/kg (wet)) K-40 890 (12/18) DWS 1200 (4/6) None j Mn-54 Fe-59 130 260 (480-1700)
LLD LLD (480-1700)
LLD LLD I Co-58,60 l 130 LLD LLD Zn-65 260 LLD LLD
,j Cs-134 130 LLD LLD Cs-137 150 LLD LLD I
l .Crabs Gamma Spec - 3 (pCi/kg (wet)) K-40 2400 (3/3) SD 2400 (3/3) None j (1700-3100) (1700-3100)
! Fe-59 260 LLD LLD Co'-58,60 130 LLD LLD Zn-65 260 LLD LLD Cs-134 130 13 (1/3) SD 13 (1-/3) None (13-13) (13-13)
.! Cs-137 150 18 (1/3) SD 18 (1/3) None j (18-18) (HHS)
~1
! NOTE: See footnote at end* of table.
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, TABLE 26
SUMMARY
OF DATA FOR THE SURRY NPS RADIOLOGICAL ENVIR0t.M£NTAL MONITORING PROGRAM - 1983 (Sheet 5 OF 7)
Name of Facility: SURRY Nuclear Power Station Docket Nos. 5-280; 50-281 Location of Facility: SURRY County, Virginia Reporting Period: 10 January - 31 December 1983 Medium or
/ Pa tllway Type and Location with Highest Annual Mean I Sampled Total Number Lower All Indicator Control LocaH?ns Mean (f) ( 2 )
- l (Units of of Analyses Limit of (1 l Locations Name, Di stance Mean (fl
}
- Measurement) Performed Detection Mean (fl (Range) and Di rec ti on (Range) (Range) j
- i
! Fish (pCi/kg (wet))
Mn-54 130 LLD LLD Fe-59 260 LLD LLD Co-58 130 100 (1/4) SD 100 (1 /4) None (100-100) (100-100)
Co-60 130 50 (1/4) SD 50 (1/4) None (50-50) (50-50)
Zn-65 260 LLD LLD Cs-134 130 6.7 (1/4) SD 6. 7 (1/4) None (6. 7-6. 7) (6.7-6.7)
Cs-137 150 12 (1/4) SD 12 (1/4) None (12-12) (12-12) i River Bottom
.1 Gamma Spec - 11 Sediments j (pCi/kg (dry)) Bi-214 1000 (9/10) SD;IIIP 1100 (2/2); (2/2) 1200 (1/1) 1 (810-1200) (1100-1100); (1000-1200) (1200-1200)
Pb-214 960 (9/10) HIP 1200 (2/2) 1300 (1/1)
.:j (690-1400) (970-1400) (1300-1300)
Ra-226 1000 (9/10) HIP 1200 (2/2) 1300 (1/1)
.] (750-1300) (1000-1300) (1300-1300) i Pb-212 870 (9/10) SI;POS 970 (2 /2; (2/2) 1200 (1/1)
I l (500-1000) (950-990;940-1000) (1200-1200)
.j Tl-208 940 (9/10) 1300 (2/2) 1300 (1 /1}
IHP i Ac-228 (970-1300) (1200-1300) (1300-1300) j 790 (6/10) ll IP 860 (2/2) 1400 (1/1)
(610-1100) (610-1100) (1400-1400)
J K-40 14000 (10/10) POS 17000 ( 2 /2) 17000 (1/1)
-'j (3000-17000) (17000-17000) (,17000-17000)
.J J i 11
.,:i NOTE: See footnote at end of table *
.J
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TABLE 26
SUMMARY
OF DATA FOR THE SURRY NPS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM - 1983 (Sheet 6 OF 7)
Name of Facility: SURRY Nuclear Power Station Docket Nos. 5-280; 50-281 Location of Facility: SURRY County, Virginia Reporting Period: 10 January - 31 December 1983
~iedium or Pathway Type and Location with Highest Annual Mean Sampled Total Number Lower All Indicator Control Locaf~?ns (Un its of of Analyses Limit of (l) Locations Name, Di stance Mean (f) <2 > Mean ( f)
. Measurement) Performed De tee ti on Mean (f) (Range) and Direction (Range) (Range)
River Bottom Cs-134 150 560 (8/10) SD 1300 (2/2) LLD Sediments (190-1300) (1200-1300)
(cont'd) Cs-137 180 1200 (10/10) SD 2600 (2/2) 860 ( 1 /1)
(56-2900) (2 300-2900) (860-060)
Co-60 670 (7/10) SD 1700 (2/2) LLD (310-240) (930-2400)
Bi-212 LLD 1100 (1/1)
(1100-1100)
Co-5!\ 1900 (1/10) SD 1900 (1/2) LLD 1900-1900) (1900-1900)
Water Fowl Gamma Spec - 1 (pCi/kg (wet)) K-40 420 (1/1) HIR 420 (1/1) None (420-420) (420-420)
Mn-54 130 LLD LLD Fe-59 260 LLD LLD Co-58,60 130 LLD LLD Zn-65 260 LLD LLD Cs-134 130 LLD LLD, Cs-137 150 4.7 (1/1) HIR 4.7 (1/1) None (4.'7-4.7) (4. 7-4. 7)
Be-7 42 (1/1) 42-(1/1) None (42-42) (42-42)
Vegetation Gamnra Spec - 7 (pCi /kg (wet)) Cs-134 80 LLD LLD Cs-137 60 LLD LLD K-40 3600 *( 7 /7) BROCK 4100 (3/3) None (2100-4900) (2300-5600)
Sr 6 Sr 6 NOTE: See footnote at *end of table.
.. _.J I
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eC TABLE 26 SUMMAkY OF DATA FOR THE SURRY NPS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM - 1983 (Sheet 7 of 7)
Name of Facility: SURRY Nuclear Power Station Docket_ Nos. 5-280; 50-281 Location of Facility: SURRY County, Virginia
- Reporting Period: 10 January - 31 December 1983 Medium or Pathway Type and Location with Highest Annual Mean Sampled To ta l Number Lower All Indicator Control LocaH?ns (2)
(Un its of of Analyses Limit of Locations Name, Di stance Mean ( fl -Mean (fl (1)
Measurement) Performed Detection Mean (f) (Range) and Direction (Range) (Range)
Soil Gamma Spec - 6 (3)
(pCi/kg (dry)) Bi-214 780 (6/6) ss 1300 (1/1) None (270-1300) ( 1300-1300)
Pb-214 940 (6/6) ss 1700 (1/1) None (560-1700) ( 1700-1700)
°'
w Ra-226 870 (6/6) ss 1500 (1/1) None (560-1500) (1500-1500)
Pb-212 580 (6/6) ss 1100 (1/1) None (100-1100) (1100-llOO)
Tl-208 770 (6/6) ss 1600 (1/1) None (410-1600) (1600-1600)
Ac-228 1100 (4/6) ss 1700 (1/1) None (470-1700) (1700-1700)
K-40 8300 (6/6) ss 15000 (1/1) None (2100-15000) (15000-15000)
Cs-134 LLD LLD Cs-137 520 (5/6) CP 830 (1/1) None (270-830) (830-830)
Bi-212 1700 (1 /6) ss 1700 (1/1) None (1700-1700) (1700-1700)
,I Cs-137 540 (1/6) ss *540 (l/6) None I (540-540) (540-540)
\
lj TLDs Gamma Dose - 172 0.23 (155/155) 10 0.36 (4/4) 0.27 (8/8)
\ (mR/day) per RG 4.13 (0.11-.82) (0.20-0.97) (0.12-0.74) r
-*1- (ll LLD is lower limit of detection as defined and required in USNRC Branch Technical Position on J An Acceptable Radiological Environmental Monitoring Program, Revision 1, November 1979.
)J (2)' (f) is the ratio of positive results to the number of samples analyzed for the parameter of interest (3) Station SS not s~lected as the location with the highest average when a true, off site alternative was available.
I V. CONCLUSIONS Results of the 1983 R~diological Environmental Monitoring. Program for the Surry Nuclear Station have been presented. Generally the fesults were as expected for normal environmental samples. Naturally occurring activity was observed in the expected sample media in the activity ranges.
One onsite station contained activity of probable plant origin in air particulate samples*and also showed a higher than normal exposure rate.
This station is not a true indicator of environmental contamin*ation.
l.,
tl
--~ Occasional samples of nearly all media showed the presence of man-made isotopes. These have been discussed individually in the text. Observed Ll activities were at very lqw concentrations and of no significant dose consequence.
[--:,.. Anomalous TLD readings were observed but there was no basis for
[ __ concluding that these resulted from any station operations.
Based on the evidence of the environmental monitoring pro~ram the station appears to be operating within regulatory limits.
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64
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