ML19305D767
| ML19305D767 | |
| Person / Time | |
|---|---|
| Site: | Haddam Neck File:Connecticut Yankee Atomic Power Co icon.png |
| Issue date: | 03/31/1980 |
| From: | NORTHEAST UTILITIES SERVICE CO. |
| To: | |
| Shared Package | |
| ML19305D761 | List: |
| References | |
| NUDOCS 8004150493 | |
| Download: ML19305D767 (100) | |
Text
.
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HADDAM NECK STATION i
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM l
t ANNUAL ENVIRONMENTAL OPERATING REPORT PART B PERIOD JANUARY 1, 1979 - DECEMBER 31, 1979 1
DOCKET NO. 50-213 LICENSE NO. DPR-61 l
PREPARED FOR THE CONNECTICUT YANKEE POWER COMPANY HADDAM, CONNECTICUT BY THE NORTHEAST UTILITIES SERVICE COMPANY BERLIN, CONNECTICUT I
i i
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e TABLE OF CONTENTS Page No.
1.0 Summary 1-1 2.0 Program Description 2-1 2.1 Sampling Schedule and Locations 2-1 2.2 Samples Collected During Report Period 2-9 3.0 Radiochemical Results 3-1 3.1 Summary Table 3-1
~
3.2 Data Tables 3-13 4.0 Discussion of Results 4-1 5.0 Offsite Dose Consequences 5-1 6.0 Discussion 6-1 Appendix A - Cow and Goat Census for 1979 A-1 Apper'ix B - QA Program B-1 j
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1-1.0 SUMARY j
In compliance with the Environmental Technical Specifications, i
Section 3.2, the radiological environmental monitoring program was continued for the period January through December 1979 around j
l-the Haddam Neck Plant. The Radiological Assessment Section of the i
Northeast Utilities Service Company (NUSCO) has prepared this 1979 report for the Connecticut Yankee Atomic Power Company (CYAPC0).
I All the radiological analyses except for tritium in water and the gama exposure measurements were performed by Interex Corporation of Natick, Massachusetts. Teledyne Isotopes, Inc. performed the j
tritium analyses of water samples and NUSCO performed the gama i
exposure measurements. As part of the overall quality assurance program, an independent check on the primary contractors' labora-tories was performed by using Radiation Management Corporation.
Radiological analyses were performed with gamma exposure measuring i
devices and on samples of air particulates, airborne iodine, soil, cow and goat milk, pasture grass, well water, reservoir water, l
l fruits, vegetables, river water, bottom sediment, shellfish, and fish. The results indicated that the predominant activity was that j
1 from the non-plant related sources of fallout from nuclear weapons testing and naturally occurring radionuclides. The only plant related radioactivity that was seen offsite above the minimum detectable levels 1
(as set by counting statistics) was observed in one measurement of iodine-131 in goats milk taken in April. A resample was obtained at this goat farm and no detectable activity was observed.
It is therefore uncertain whether the activity was plant related or an analysis error.
However, assuming it was plant related, the dose consequences of such a level are addressed in Section 5.
Onsite areas that showed plant effects were in the vicinity of the boron waste storage tanks, the i
i waste gas surge sphere, the discharge canal, and the guard house, l
where the game exposure measurements were above background; the onsite well water which had their higher than normal tritium levels; I
and the station discharge canal where fish had some plant related cesium-137. All the levels were similar to those of previous years
{
l of plant operation.
l I
The variability of levels of radioactive material in environmental media depends on many factors. These factors include plant release i
rates, meteorology, number and size of nuclear weapons tests, sea-l sonal variability of fallout, soil conditions, pasturing habits, i
local terrain, and locational variability of fallout. Significant l
I variations in measured radioactivity could be caused by any one of l
l these factors. Therefore, all of these factors need be considered l
l in order to explain such variations.
l l
l As usual, significant quantities of cesium-137 and strontium-90 measured in both cow and goats milk. These levels are a result of nuclear weapons testing in the 1960's and not the result of plant operation. This is because of insufficient quantities (at least 2000 times less) of these isotopes in plant releases to account for l
the measured concentrations and the absence of chemically similar cesium-134 and strontium-89 which are released in about equal or-a larger quantities from the plant.
l l-1 l
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. -. - ~. - - -
The radiation dose to the general public from the plant's discharges has been evaluated by two methods. One method utilizes the measured station's discharges and conservative transport models and the other utilizes the measured concentrations of radioactivity in the environ-mental media. The maximum whole body dose (station boundary) that i
could occur to a member of the general public as a result of the plant's discharges was 0.9 millirem and the average dose to a member of the public residing within 50 miles of the plant is 0.0011 millirem. These doses are 0.2 percent and 0.0006 percent of the corresponding Federal (and State) standards for annual permissible doses to the public from man-made radiation, which are 500 millirem and 170 millirem, respectively. Background radiation sources in Connecticut give members of the public a 4
dose of 130 millirem per year. Thus the plant's effect on the public is minimal.
l l
l l-2
2.0 PROGRAM DESCRIPTION 2.1 Sampling Schedule and Locations The sample locations and the sample types and frequency of analysis are given in Table 2-1 and 2-2 and Figures 2.1, 2.2 and 2.3.
The program as described here is that which is required by Environmental Technical Specification 3.2.
2-1
TABLE 2-1 CONNECTICUT YANKEE RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM and Analysis (#
Sample Type. Frequency
-Distance Garama Air Milk (d)
Location
&Direc t ion (a)
Dose Particulate Soil Vegetation Water T rrestrial Stations 1.
On site fence near boron waste etorage tanks 0.5 miles, N M
2.
On site fence near waste gas surge sphere 0.5 riles N M
3.
On site fence near discharge canal 0.5 miles, SSE
.M 4.
On site fence near guard house 0.5 miles, WNW M
--W1-M2-Q5(I
- )
5.
On site - Injun Hollow Road 0.5 miles, NW H
A2,5 W1-M2-Q5 ('))
A2,5 6.
On site - Substation 1.0 mile, ENE M
7.
Haddam 2.0 miles SE M
Wl-H2-Q5 A2,5 8.
East Haddam 3.0 miles ESE M
Wl-M2-Q5 A2,5 9.
Higganum 3.5 miles WNW M
W1-M2-Q5 A2,5
- 10. Hurd Park Road-East Hampton 3.0 miles NNW M
Wl-H2-QS A2,5
- 11. Middletown
- 10.0 miles NW H
W1-M2-Q5 A2,5 Wl-M2-Q5 (*)
A2,5
- 12. Deep River 88.0 miles SSE M
w b
- 13. North Madison
- 12.0 miles SW M
Wl-M2-Q5 A2,5
- 14. Colchester
- 10.0 miles ENE M
W1-M2-Q5 A2,5 H1,2,4,5
- 15. On Site - Wells 0.5 miles SE
- 16. Well - State Highway Dept.
Q1,2,4,5 East Haddam
- 3.0 miles S Q1,2,4,5
- 17. Well - Injun Hollow Road 1.0 mile, NW
- 18. Well - Haddam 1.0 alle S Q1,2,4,5
- 19. Cow Location #1 1.5 miles NW H3
- 20. Cow Location #2 2.2 miles ESE M3 M3
- 21. Cow Location #3 2.8 miles E M3
- 22. Cow Location #4
- 11.0 miles ENE M3(8)
- 23. Goat Location #1 a 6 miles u I
- 24. Goat Location #2 1.3 miles Nu 10 8
- 25. Fruits & Vegetables A2,3 (h)
TABI.E 2_1 (continued)
~
Sample Type. Frefuency(b) and Analysta("
Dia'tanceg Bottom Direction *)
Sedia'ent Water Fishfi)
She11 fish,
Iocation
_ Aquatic Stations
- 26. Conn. River - Vicinity of intaka 0.5 mile, SSW Q2,3
- 27. Conn. River - Higganus Oght
- 3 mile, NW Q2,5-Q2,3
~
28.
Conn. River - E. Haddam Bridge a2 mile, SE Q'2,5
-29.
Connecticut River, vicinity of,ette 0.75 mile, ESE Q2,5 Q1,2.4.5 Q2,3(II
. Plant Discharge Canal i
Q1,2,4,5 Q2,3(1) 30.
Conn. River - Middletown 89 alle, NW.
m
- 31. ~Houth of the Salmon River 1.5 mile, SE Q2,3 Control Stations
' (a) Distance to nearest half mile (b) W - Weekly,II - Monthly, Q - Quarterly, SA - Semi-Annual, A'- Annual *
(c) 1 - Cross Beta, 2 - Gamma Spectrum, 3 - I-131, St-89, Sr-90,,Co-137, 4 - H-3;i(,- sel89, Sr-90, ca,-137 (d), During the period April through October and ones in February (e) Includes a charconi filter that la to be analyzed weekly for I-131 (f) Analyses are done on the month'ly and quarterly composites (g) A sla11er annlysis will be 'done on allk instead of grass if. the former la avall'able (h) During the harvest acason, when available from commercial farms.
(i) Bullheads and when available perch
l TABLE 22 H1MlHUM DETECTABLE l.EVELS IN ENVIRONMQffAL SAMPl.ES ANDESULTING DOSES Minimum Annual Dose Detectable f.evels' Assotteted Annisal _Intalte with teL' (ares)
Critical Orten Sample Site (HDL)
An_alyets Sample Tyg Crose beta 1 liter 1 pC1/1
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20 pct /I' 440 I Welt and Ittver Water 0.2' home Casma spectrum 3 liter 2.0 pCI/I Sr-89 2 liter 440 1 1.0 pct /l
- 1. 0' bone Sr-90 2 liter 440 1 ro 0.070' whole body b
Cs-137 2 Itter 6.0 pct /1 440 1 0.005' body tissue M-3 2 liter 60 pct /1 0.05 pcl/g' 8'
Casons spectrum 1 kg 0.072 pct /s Sotton Sediment and Soll 1 kg Sr-89 0.036 pct /s Sr-90 1 kg 0.064 pC1/g Cs-137 1 kg 0.05 pct /g' 18.3 kg bone Camma spectrum I kg 0.018 pCl/a 0.08
- 18. 3 b g Fish and Shellft<h 100 g boe.e St-89 0.00s pct /n 0.4 whole body 18.3 na Sr-90 300 g 0.056 pct /g 0.031 Cm-137 100 g wieole body 17 mantle 1 month I arem caposure 71.0 C.sms Onae esponist e Cbtid's thyroid 183 i 0.5 pC /1 i.6 I8) 1 bone
't-333 4 liter 0.08 tel i 1.0 pCl/l bone Milk St-A9 1 liter 0.40 1.0 pCl/l whole body IRI I Sr-90 1 liter 0.0 16 Cs-137 I Iteer 6.4 f.Cf/t I
TABLE 2 2 (Cont'.1)
Hinimum Detectable Annual Dose
- i. eve ln*
Associated with Hnt.' (aren)_
Critical Organ, Annual __ intake Analysis Sascle Stra
_f_mL)
I-131 270m3 0.04 pct /m3
- 0. 5 '
Chtle's thyroid 1100 m3 Sample Type 38 Filtered Air 3
0.01 pct /m Crose Beta 270m Cross Casme 270m3 0.045 pct /m3 8 Caama Spectrum 1.080m3 0.07 pct /m3 8 0.05 pct /g' I-831 1 kg 0.05 pct /s 7.5' '
Child's thyroid Camma spectrum 1 kg Venetation Sr-89 1 kg 0.018 pct /g Sr-90 1 hg 0.009 pCi/g Cm-137 1 k p.
0.014 pCI/r, P3b
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II.ssed en a catti e.se lim wish ca-117 of 1.5 pC1=1 cment per minute
' For 8:s-117 annumisir. *ws Interference from other nuclides Cs-137 used as a refescure source They apply to the activity at the These are ninte.em pr.ortiv al detectable levels (MDt.) as opposed to tiieoretical detection limits.
8 HDL = 2 O background.
done.
tine nf sample culic.Eton.08. Fr.t. eat u lla Inn Council reporte on Radiatlan protection Cielden and amanciated p.e c.I.mto drinkinr, water only k
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23 East Haddom I,,,ii.,i scale of miles G Well Water Sampling Stations e Aquatic Sampling Stations t
FIGURE 2.3 Aquatic and Well Water Sampling Stations l
Haddam Neck Plant
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I 2-8 i
o 2.2 Samples Collected During-Report Period The following table summarizes the number of required samples of each type collected during the present reporting period:
Scaple Type Number of Samples Gamma Exposure Rate (TLD) 167 i
Air Particulates 519 Air Iodine 208 Soil 10 Dairy Milk 32 Goat Milk 12 l
Pasture Grass 3
l Well Water 24 Fruit and Vt3etables 8
River Water 8
Bottom Sediment 12 Fish 23 r
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Shellfish 8
L Total All Types 1,034 e
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4 3.0 RADI0 CHEMICAL RESULTS 3.1 Summary Table t
In accordance with Environmental Technical Specification 5.6.la., Table 5.6-1, a summary table of the radiochemical t
results has been prepared and is presented in Table 3-1.
In the determination of the mean the data was handled as recommended by Health and Safety Laboratory, Idaho: all valid data, including negative values and zeroes were used in the determination of the mean (see part 3.2).
A more detailed analysis of the data is given in section 4.0 where a discussion of the variations in the data brings to light many aspects that are not evident in the summary table because of the basic limitation of such an approach.
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TABLE 3-1 ENVIRONMENTAL RAD 101DCICAL HONITORING PROGRAM SbmARY CONNECTICUT YANKEE ATOMIC 70WER COMPANY. HADDAM NECK PLANT DOCKET 50-213 JANUARY - DECDtBER 1979 NUMBER OF ANALYSIS Am MIN 1) RIM ALL 1 2 1CATOR LOCA110N WITH H1 CHEST ANNUAL MEAN CONTROL IDCATIONS NONROUTINE MEDIUM OR TOTAL NUMBER DETECTABLE IDCATIONS REPORTED PATHWAY OF ANALYSES J
LEVELS (b)
NAME. DISTANCE (b)
(b)
MEASURDfENTS SAMPLED PERFORMED i
(DOL's)(a)
Hean (Range)
AND DIRECTION Mean (Range)
Mean (Ranae)
(c) lodine 27 9 Dairy Farm #2 1-131 0.5 0.03
(-0.1-0.4) 2 elles ESE 0.06
(-0.1-0.4) 0.01
(-0.06-0.10)
'N g
Sr 27.9 Dairy Fara #2 Sr-89 2.0 0.0
(-2.6-1.2) 2 miles ESE 0.3
(-0.9-1.2)
-0.4
(-2.0-0.1) 0 Dairy Fara #3 Sr-90 1.0 8.2 (3.5-13.6) 2.8 miles E 10.9 (7.6-13.6) 5.5 (4.5-7.2) 0 CS 27,9 Dairy Farm #3
[
CS-137 1.0 16.9 (6.4-33.0) 2.8 miles E 24.5 (18.4-33.0) 11.1
~7.2-15.4)
O Coat location #2 Cost Milk lodine 8.5 (pC1/1) 1-131 0.5 0.3
(-0.1-2.5) 1.3 miles NW 0.3
(-0.1-2.5) 0.0
(-0.1-0.1)
O Sr 8.5 Sr-89 2.0
-0.2
(-1.2-1.2)
NA NA
-0.9
(-2.0-0.6)
O Coat location #1 Sr-90 1.0 8.8 (5.6-12.8) 6 alles N 24.1 (21.1-29.6) 24.1 (21.1-29.6) o Coat location #1 CS 8,5 CS-137 1.0 18.4 (13.6-23.7) 6 miles N 50.0 (32.2-66.0) 50.0 (32.2-66.0)
O Coat location #2 Pcature Crass Sr 1.4 0.018 0.02 (NA) 1.3 miles NW 0.02 (NA) 0.01 (0.00-0.02)
(pCi/g)
Sr-89 Coat location #1 0.009 0.11 (NA) 6 miles N 0.14 (0.06-0.27) 0.14 (0.06-0.27)
Sr-90 O
Coat location #2 CS 1,4 0.009 0.07 (NA) 1.3 miles NW 0.07 (NA) 0.05 (0.04-0.05)
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TABLE 3-1 ENVIRONMENTAL RADIOLOGICAL MONITORING PROCRAM SUmtARY CONNECTICUT YANKEE ATOMIC POWER COMPANY. HADDAM NECK PIANT DOCKET 50-213 JANUARY - DECDiBER 1979 3RIMBER OF ANALYSIS AIS MIN 1EM ALL INDICATOR IDCATION WITH HIGHEST ANNUAL MEAN CONTROL IDCATIONS NONROUTINE MEDIUM OR TOTAL NIMBER DETECTABLE IDCATIONS REPORTED PATHWAY OF ANALYSES LEVELS (b)
NAME. DISTANCE (b)
(b)
MEASUREMENTS SAMPLED PERFORMED (IOL's)(a)
Mean (Range)
AND DIRECTION Mean (Ranae)
Mean (Range)
(c)
East Haddam Bridge Botton Sediment Sr 48
-0.004 (-0.009--0.001) 2 miles SE 0.001
(-0.004-0.008)
-0.004
(-0.021-0.008)
(PC1/g)
Sr-89 0.072 Higganum Light Sr-90 0.036 0.014 (0.008-0.017) 3 miles NW 0.015 (0.005-0.031) 1.015 (0.005-0.031) o East Haddam Bridge CS 4.8 0.045 (0.019-0.074) 2 miles SE 0.132 (0.086-0.246) 11.117 (0.045-0.246)
CS-137 0.036 0
0.0 NA NA 3.0 1-131 0.2 0
0.M M
NA 3.M CS-134 0.2 0
2-54 0.2 0.00 NA NA 0.00 0
co-58 0.2 0.00 NA NA 0.00 0
East Haddam Bridge Co-60 0.2 0.00 2 miles SE 0.02 (0.00-0.04) 0.01 (0.00-0.04)
O Higganum Light Zr-95 0.3 0.00 3 miles NW 0.01 (0.00-0.04) 0.01 (0.00-0.04) 0 Nb-95 0.00 NA NA 0.00 Plant Discharge K-40 1.0 12.7 (10.6-15.7) 0.5 miles ESE 12.7 (10.6-15.7) 11.0 (6.6-14.7) 0 4
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TABLE 3-1 ENVIRONMENTAL RADIOIDCICAL MONITORING PROGRAM
SUMMARY
CONNECTICUT YANKEE ATOMIC POWER COMPANY HADDAM NECK PLANT DOCKET 50-213 JANUARY - DECD1BER 1979 NUMBER OF ANALYSIS AW MINIMIM ALL I E ICATOR IDCATION WITH HICHEST ANNUAL MEAN CONTROL IACATIONS NONROUTINE MEDIUM OR TOTAL NUMBER DETECTABLE LOCATIONS REPORTED PATHWAY OF ANALYSES LEVELS (b)
NAME. DISTANCE (b)
(b)
MEASUREMENTS SAMPLED PERFORMED (E L's)(a)
Mean (Range)
AND DIRECTION Mean (Ranae)
Mean (Ranae)
(c)
F1t h -
Intake Vicinity Sr 93 o => (-o *'-o oio o 5 in ssa o a) (-o oo'-o oia o oo)
<-o = '-o = ')
gg;;;d-5,-o, 0.m.
o Middletown 0.077 (0.042 4.162) 9 miles W 0.101 (0.083 4.11 0 0.101 M.0W.W Sr-90 0.009 0
Plant Discharge CS 12 3 0.058 (0.020-0.111)
Ona14.5 miles ESE 0.066 @.0M.W
- 0. m M.0240N CS-137 0.009 O
Y N
O 0.M NA NA 0.00 I-1 31 0.05 0
0.M NA NA 0.00 CS-134 0.04 0
h-54 0.05 0.00 NA NA 0.00 0
Co-58 0.04 0.00 NA NA 0.00 o
Co-60 0.04 0.00 NA NA 0.00 0
l Zr-95 0.1 0.0 NA NA 0.0 o
Nb-95 O.J3 NA NA 0.00 0
Intake Vicinity K-40 0.5 2.1 (0.9-4.0) 0.5 miles SSW 2.3 (1.7-4.0)
L.8 (1.4-2.0)
O
e TABLE 3-1 ENVIRONMENTAL RADIOLOGICAL MONITORING PROGRAM
SUMMARY
CONNECTICUT YANKEE ATOMIC POWER COMPANY. IIADDAM NECK PIANT DOCKET 50-213 JANUARY - DECDtBER 1979 NUMBER OF ANALYSIS AW MINIMUM ALL INDICATOR LOCATION WITH HIGHEST ANNUA 1 MEAN CONTROL LOCATIONS NONROUTINE MEDIUM OR TOTAL NUMBER DETECTABLE LOCATIONS REPORTED PATHWAY OF ANALYSES LEVELS (b)
NAME. DISTANCE (b)
(b)
MEASUREMENTS SAMPLED PERFORMED (m L's)(a)
Mean (Range)
AND DIRECTION Mean (Range)
Mean (Range)
(c)
Fish - Other Sr 8.4
-0.004 (-0.015-0.015)
NA NA
-0.002
(-0.005-0.002)
(pC1/g)
Sr-89 0.018 Plant Discharge 0.14 (0.07-0.26)
Canal-0.5 miles ESE 0.15 (0.07-0.26) 0.07 (0.05-0.09)
St-90 0.009 Plant Discharge CS d,4 0.082 (0.015-0.222)
Canal-0.5 miles ESE 0.099 (0.0)3-0.222) 0.047 (0.034-0.059)
CS-137 0.009 Ce(Lt) 8.4 0.00 NA NA O.00
~"
l-131 0.05 CS-134 0.04 0.00 NA NA 0.00 o
Mn-54 0.05 0.00 NA NA 0.00 o
Co-58 0.04 0.00 NA NA O.00 o
Co-60 0.04 0.00 NA NA 0.00 o
Zr-95 0.1 0.00 NA NA 0.00 o
Nb-95 0.00 NA NA 0.00 Plant Discharge 2.9 (2.2-3.9)
Canal-0.5 miles ESE 3.0 (2.2-3.9) 2.6 (1.5-3.6)
K-40 0.5
l FOOTNOTES t
For Ge(Li) measurements the MDL's = 2 x /2B where B = background. For a.
all others, MDL = 2 x 0 background. These MDL's are based on the absence of large amounts of interfering activity (excluding naturally occurring radionuclides). Deviations by about factors of 3 to 4 can occur, exclud-ing Technical Specification Items, b.
Analytical results are handled as recommended by HASL (" Reporting of l
Analytical Results from HASL," letter by Leo B. Higginbotham). Negative j
values were used in the determination of the mean.
Nonroutine reported measurements are defined in Section 5.6.2b of the c.
Technical Specifications.
d.
First number is the number of indicator measurements, the second is the number of control measurements.
3 c.
Assuming 270 m / paper.
3 f.
Assuming 1080 m.
g.
Quarterly composites.
h.
NA--Not Applicable i
e O
3-12
3.2 Data Tables The data reported in this section are strictly counting statis-tics. The reported error is two times the standard deviation of the net activity. Unless otherwise noted, the overall error is estimated to be 2 to 5 times that listed.
Because of counting statistics, negative values, zeroes and numbers below the Minimum Detectable Level (MDL) are statis-tically valid pieces of data. For the purposes of this report, in order to indicate any background biases, all the valid data are presented.
In instances where zeroes are listed after significant digits, this is an artifact of the computer data handling program.
Data are given according to sample type as indicated below.
1.
Gamma Exposure Rate 2.
Air Particulates, Gross Beta Radioactivity 3.
Air Particulates, Weekly I-131 4.
Air Particulates, Monthly Quantitative Gamma Spectra 5.
Air Particulates, Quarterly Strontium and Cesium 6.
Soil 7.
Milk - Dairy Farms 8.
Milk - Goat Farms 9.
Pasture Grass 10.
Well Water 11.
Reservoir Water 12.
Fruits & Vegetables
- 13. Heat, Poultry and Eggs 14.
River Water 15.
Bottom Sediment 16.
Shellfish 17.
Fish
[
There was no commercially available meat, poultry, or eggs for which the feed was grown within 10 miles of the site.
4
-9, 3-13
LOCATION KEY FOR DATA TABLES CONNECTICUT YANKEE 1
Boron Waste Storage Tanks Fence - N,.5 miles 2
Waste Gas Surge Sphere Fence - N,
.5 mileo 3
Discharge Canal Fence - SSE,.5 miles 4
Guard House Fence - WNW,.5 miles 5
Injun Hollow Road - NW,.5 miles 6
Substation - ENE,1 mile 7
Haddam - SE, 2 miles 8
East Haddam - ESE, 3 miles 9
Higganum - WNW, 3.5 miles 10 Hurd Park Road - NNW, 3 miles llA Middletown - NW, 10 miles 12A Deep River - SSE, 8 miles 13A North Madison - SW,12 miles 14A Colchester - ENE, 10 miles 15A On Site Wells 1 & 2 - SE,.5 miles 16A State Highway Dept. - E. Haddam - S, 3 miles 17 Well - Injun Hollow Road - NW,1 mile 18 Well - Haddam - S,1 mile I
19 Cow Location #1 - NNW, 1.5 miles 20 Cow Location #2 - ESE, 2 miles 21 Cow Location #3 - E, 3 miles 22 Cow Location #4 - ENE, 11 miles i
23A Goat Location #1 - N, 6 miles 24 Goat Location #2 - NW, 1.3 miles 25 Within 10 miles of plant 35 Beyond 10 miles of plant 26 Conn. River - Intake Vicinity - SSW,.5 miles 27A Conn. River - Higganum Light - NW, 3 miles 28A Conn. River - E. Haddam Bridge - SE, 2 miles 29 Plant Discharge Canal - ESE,.5 miles 30A Conn River - Middletown - NW, 9 miles 31 Mouth of Salmon River - SE, 1.5 miles 40B Near Intake Structure - SSW,.5 miles 41B Picnic Area - NW,.5 miles 42B Mouth of Discharge Canal - ESE,.5 miles SlB Conn. Valley Hospital - NW, 7.5 miles 52B Mt. Higby - WNW,12.5 miles 43B Moodus - NE, 2.0 miles 44B Shailerville (Horton Rd.) - SSW,.5 miles 45B Haddam Jail (Jail House Rd.) - WSW,1.0 miles i
P l
A - Control Stations B - Site not required by ETS e
3-14
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4.0 DISCUSSION OF RESULTS Gamma Exposure Rate v~ The gamma exposure rate is determined from the integral exposure measured over periods of about cae month using thermoluminescent dosimeters. Dosimeters are placed at a number of on-site locations, as well as at inner and outer environmental locations. The results of the measurements are shown on Table 1 (see the proceeding tables). The dosimeters utilized for these measurements are subject to inherent self-irradiation which has been determined for each dosimeter. The results in Table 1 have been corrected for this effect. The range of the correction factors was 0.3 uR/hr to 3.1 uR/hr with a mean of approximately 1 uR/hr. The data for 1979 exhibit the same trends as that of previous years; there was no significant dif ference between the off-site inner and outer rings of locations, thus indicating no off-site effects' from plant operations. The on-site locations at the boron waste storage tank, the waste gas surge sphere, discharge canal and guard house were the only locations showing any plant effects. At these locations there was an annual average of from 1 uR/hr to 10 uR/hr due to direct radiation from the station. These locations are within the on-site fenced in area and remote from areas where members of the general public are usually allowed. Dosimeters at areas where the public are allowed, such as the picnic area and the mouth of the discharge, indicated no contribution from the station. Air Particulates and Iodine Air is continuously sampled at a number of locations by passing air through a particulate filter. The filters are collected weekly and counted for gross beta. Results are shown in Figure 4-1 and Table 2. The gross beta activity at all locations remained at a relatively constant low level throughout 1979. There were no severe increases as seen in 1977 and 1978 and the usual increase ia spring and summer was lacking because of the absence of recent atmospheric nuclear testing in the northern hemisphere. Measured levels of the inner and outer rings of stations showed no signifi-cant differences (see Figure 4-1), thus indicating no contribution from the station. At a selected few of the air particulate locations are included charcoal canisters for the collection of iodine. The results, shown on Table 3, indicate no levels of iodine -131 activity above the HDL (Minimum Detectable Level - see Table 3-1, Column 3) at any location throughout 1979. In some instances (approximatley 10%), there are positive values greater than the calculated error. This small percentage is expected due to statistics. Therefore, there was no measurable plant related activity. The weekly air particulate filters are composited monthly for a gamma spectral analysis (Tables 4A-4L). The results, as usual, indicated trace amounts of naturally occurring Th-228 and the L l 4-1 a
presence of cosmic produced Be-7. These monthly analyses further support the indications of the gross beta activity. There is a lack of detectable levels of the recent fallout (and reactor produced) nuclides of Ru-103, Zr-95, Nb-95 and Ru-106 and there is no significant difference between the outer and inner locations. Cs-137 is also not detectable (seen above MDL's) in any of the samples and there is no Cs-134 seen at all. Therefore these results indicate the lack of any measurable plant effects. For the measurement of strontium and total cesium (chemistry), the air particulate filters are composited quarterly. The results are shown on Table 5. The analyses presented in this table are much more sensitive indicators of radioactivity than the monthly gamma spectra because the compositing results in large volumes being measured and the chemistry allows a high degree of sensitivity. Although the chemistry allows such a high degree of sensitivity, it does not allow the separation of Cs-134 and Cs-137. The results here are for the total cesium. The yearly average of the quarterly cesium values and the monthly Cs-137 Geli spectrometry agree favorably. The levels as seen in 1979 are less than those seen in 1978. There is no difference between the indicator and control stations and no Cs-134 indicated in any of the monthly gamma spectra. This indicates that what is being measured in the quarterly composites for cesium is only Cs-137. Therefore, the origin of the Cs-137 is not plant related and its origin is weapons testing fallout. The quarterly composites further confirm all the preceding analyses of the air particulates. There is no Sr-89 detectable (above MDL,'s) in any of the samples showing the lack of fresh fallout or plant effects. Sr-90 is seen in all of the samples at lower levels than those seen in 1978 and shows no difference between indicator and control stations. 9 In conclusion, since there were no differences in measured levels between the indicator and control locations and no detectable I-131, Cs-134, and Sr-89, there were no indications of any plant effects. Soil Samples are taken annually (see Table 6) at each of the air parti-culate sample locations. The only activity that was observed in these samples was that of naturally occurring nuclides of Ra-226, Th-228 and K-40 and fallout from the previous nuclear weapons testing nuclides of Sr-90 and Cs-137. The levels of Sr-90 and Cs-137 were essentially unchanged from that observed in the past four years. Cow's Milk No I-131 was detected above the minimum detectable level of 0.5 pCi/l in any of the samples (see Table 7). This is typical of samples taken around this station. The only instances where I-131 has ever been seen in past years are those which were affected by recent nuclear weapons testing. 4-2
Sr-90 was seen in all samples. All the results were below 15 pCi/l and typical of those seen in the last three years. Sr-89 was not 2 detected above MDL's in any of the samples indicating that the Sr-90 is resulting only from weapons fallout. As with Sr-90, Cs-137 was seen in all the samples. The levels ranged from 6 to 33 pCi/1, approximately the same as in 1976, 1977 and 1978. The values of Cs-137 listed in Table 7 are actually those for total cesium chemistry. All of these chemistry analyses were confirmed by gamma spectrometry. Gamma spectrometry also indicated the absence of Cs-134 at levels above the MDL, indicating that the Cs-137 is fallout and not plant related. For a more detailed discussion of the variability of the Sr-90 and Cs-137 concentrations in milk see Section 6.0. Goat's Milk i Unlike cow's milk, there was one sample which showed a detectable level of I-131 (Table 8). A resample, taken nine days later, showed the absence of any I-131 activity as did the rest of the goat milk samples. The dose consequence of the I-131 is discussed in Section 5. As usual, the levels of Sr-90 are somewhat higher than those observed in cow's milk, thus indicating a difference in either dietary habits or metabolism. This is also the case for Cs-137. The levels of both these nuclides are higher in the control station than in the indicator station (for an explanation as to the cause of this variability see Section 6.0). There is also an absence of detectable levels of Sr-89 and Cs-134 which further indicates that the levels of Sr-90 and Cs-137 are related to past weapons fallout and are not plant related. Pasture Grass Samples of pasture grass are required by Technical Specifications to be taken if milk samples become unavailable. The resulting samples show similar effects as that of the milk. The only detectable levels were those of the naturally occurring nuclides of K-40, Ra-226 and Th-228 and fallout nuclides of Sr-90 and Cs-137. The absence of Sr-89 and Cs-134 confirmed the fact that there were no plant effects. Well Water Well water samples showed activity levels similar to those in previous years. Gross beta values were generally in the 1 to 3 pCi/l range except for the control well at the State Highway Department which had values from 4 to 8 pCi/1. This well has shown these same relatively high values in previous years. The only other activity that is actually detectable is that of naturally occurring, fallout produced and reactor produced tritium (H-3). The measured levels in all the wells are normal and similar i 4-3 i
to previous years. Because the on-site wells are in the ground water flow path between the discharge canal and the river, they continued to show the usual high tritium levels. The water from these wells in only used in process streams at the station. These levels were not reported as Anamalous Measurements as a result of an understanding with the NRC staff. The values of Ra-226 seem to indicate its presence but this is not the case. The isotope actually counted by the gamma spectrometer here was Bi-214, a daughter product of Ra-226 which are usually in equilibrium. But this is not always true for well water samples. Special radium (Ra) analyses of some 1976 samples, also showing high values of Bi-214, confirmed that this water met with the EPA drinking water standards. Reservoir Water As in previous years no indication of plant isotopes were found. The only detectable activity seen here is that of gross beta, which showed levels similar to those of previous years. Fruits and Vegetables As usual, this pathway did not show any indication of plant effects. There were no detectable levels of Sr-89, Cs-134, or I-131 in any of the samples. The only detectable activities were those of fallout produced Sr-90 and Cs-137 and of naturally occurring K-40. The predominant activity was that of K-40. The levels of Sr-90 and Cs-137 were essentially the same in both indicator and control stations and are similar to those of previous years. River Water The river water samples at the control (background) station are quarterly composites of weekly grab samples. At the indicator station, near the area of discharge from the plant, is located a continuous sampler. As in previous years the gross beta activity is in the range of 2 to 4 pCi/1. The only other detectable activity is that of tritium (H-3). This tritium at the indicator station is plant related as has been seen in the past. There is no dose consequence of these tritium levels since the river water is not used for drinking. Bottom Sediment All samples showed the predominance of naturally occurring nuclides of K-40, Ra-226 and Th-228. The only other activity above MDL's is that of Cs-137, with levels lower at the indicator station than at the control stations. This along with the fact that there was no Cs-134 detected indicates that the Cs-137 is only fallout related. This is unlike last year when the cesium (Cs) releases were greater, there was plant related Cs-137 and Cs-134 seen for the first time in these samples. With the decrease in cesium releases, the plant 4-4
o effects were not detectable. Traces of Sr-90 below MDL's show no dif ferences between indicator and control stations and therefore are f rom fallout and not plant related. Shellfish As usual, the only activity above MDL's in these samples were Sr-90, Cs-137 and naturally occurring K-40, Ra-226 and Th-228. The Cs-137 shows no dif ference between indicator and control stations and the levels of Sr-90 and Cs-137 have remained about the same in the last four years indicating that these two isotopes are only fallout related. Fish-Bullheads Similar to shellfish, the only nuclides that were detectable above MDL's were Sr-90, Cs-137 and naturally occurring K-40 with the predominant being K-40. Sr-90 and Cs-137 were seen at levels typical of the past three years. The Sr-90 levels were seen in varying quantities at all three locations and with the absence of any detectable Sr-89 indicates that the Sr-90 is from the fallout of nuclear weapons testing and not a result of plant discharges. As in 1978, the Cs-137 is higher for the samples taken from within the discharge canal than for the control station samples and hence could be plant related. The dose consequence of such a level is discussed in Section 5.0. Fish - Perch and Other These samples show the same effects as the bullhead samples. The predominant activity was from naturally occurring K-40. The only other activity that was detectable was Sr-90 and Cs-137. As with bu11 heads, there was no detectable Sr-89 seen in any of the samples and the Sr-90 was seen in varying quantities at all three locations. Therefore, the Sr-90 is not plant related. The Cs-137 also is quite variable, but is somewhat higher in the discharge canal sample. This same trend was seen in 1978. The dose consequence of such a level is also discussed in Section 5.0. c 4-5 l L.
FIGURE 4-1 l COMPARATIVE MONTHLY VALUES j -~ -~ --- ~ ~y-- GROSS BETA RADIOACTIVITY -t - ~ ~ AIR PARTICULATES i i 1979 J I 4 i I ' I i i l i I ? _.a__ _...7 g G Inner Sthtions l i i' .04 -j i l l l 1 j i Oouter stations l i - - - - - ~ [ l l Theerrokinthese 4 values is appT5xicmraly i .003 i [ ~~~ N ~ g. l / l f'O \\ \\ Ul .y: i i i ( -. _._ m a N + l c. i l <_.l ) I .A f I 4 1 . _ - -_ _ _ _ _ _]-._ i i l 't l i I i f t-l t' k .02 l, J j I ~' s '[ t i l l... r--- I I }- - _, l I ._.._._a I i .01 } l t l~ l l l l l l i i i i I t-i . --__. p ..__.L _i t I i i j i i' i J l i i l I I .y i i 4 I. I i i Jan Feb' Mar Apr !!ay Jun
- Jul, Aug Sep Oct Nov Dec 4-6
o 5.0 0FFSITE DOSE CONSEQUENCES The off-site dose consequences of the station's radioactive liquid and airborne discharges have been evaluated using two methods. The first method starts with the station's measured radioactive discharges and utilizes conservative modele to simulate the trans-port mechanism through the environment to man and hence compute the maximum doses to individuals and the O to 50 mile population dose. The results of these computations have already been submitted to the NRC in the 6 month Radioactive Effluent Release Reports written in accordance with Environmental Technical Specification 5.6.lb. This method, although conservative (i.e., computes higher doses than that which actually occur) has the advantage of providing an upper bound estimate of the dose consequences in those cases where the actual dose cannot be measured because they are so small as to be well below the capabilities of convential monitoring techniques. 3 The second method utilizes the results of the concentrations of radioactivity, in various environmental media, e.g., milk, fish, and then computes the dose consequences from the consumption of these foods. t The results of both methods are compared in Table 5.1. For gaseous releases, the only detectable activity was I-131 in one goat milk sample. The less than values given for method 2 are the doses which would be calculated if the annual average activity was equal to the minimum detectable level. Although the liquid releases are also low, traces of plant related activity could be detected in fish caught in the discharge canal. The doses presented in Table 5.1 are the doses to the maximum individual. That is, the dose is calculated at the location of 7 maximum effect from the plant effluents. For example, the dose via the fish pathway is calculated for fish caught in the discharge canal and the external gamma dose is calculated at the site boundary which is nearest the discharge and has the greatest number of hours of wind blowing to that location from the site. Thus, the calculated doses for all other locations will be less than that shown. The dose to an average individual within 50 miles from the site is not presented in Table 5.1 because it cannot be calculated using Method 2. However, Method 1 yields the following results for the period January-December 1979 for the average individual: ANNUAL WHOLE BODY DOSE DUE TO AIRBORNE EFFLUENTS = 0.00025 mrem ANNUAL WHOLE BODY DOSE DUE TO LIQUID EFFLUENTS = 0.00087 mrem Thus, it can be seen that the dose to the average individual is much less than the dose to the maximum individual. In order to provide perspective on the doses in Table 5.1 the standards for 1979 on the allowable maximum dose to an individual 5-1 x-- ~
in the general public and the allowable average dose per person to a large group of population are given in Table 5.2. It is obvious that the impact of the station operation when measured against these standards for public exposure lead to the conclusion that the dose consequences are in general nonexistent and definitely not significant. The monitoring program is adequate to detect the i effects of the stations' discharges well before they are of a magnitude to approach the standards for allowable public exposure. 5 I t 5-2 l l
TABLE 5.1 COMPARISON OF DOSE CALCULATION HETil0DS IIADDAN NECK STATION JANUARY-DECEMBER 1979 II) PATHWAY ORGAN HET110D I HET110D 2 AIRBORNE EFFLUENTS 1. External Ganana Dose Max. Ind. -Whole Body 3.4 x 10"I ) ND(3) 2. Inhalation Max. Ind.-Thyroid 2.6 x 10 NAD } 4.8 x 10~I -l -3. Goat's Milk Max. Ind.-Thyroid 1.3 x 10"I 8.2 x 10~ LIQUID EFFLUENTS 4.8 x 10,2 ~ 1. Fish Max. Ind.-Whole(gdy 0.58 Max. Ind.-Liver 0.78 7.3 x 10 -2 Ind.-GI(LLI)(5) 2.77 NAD(4) 1.0 x 10 Max. (1) Hethod 1 uses measured station discharges and meteorological data and conservative t ransport to man models. Hethod 2 uses measured concentration in environmental media. (2) Maximum individual - The maximum individual dose is the dose to the most critical age group (child for inhalation, infant for milk), at the location of maximum concentration of plant related activity. The dose to the average individual is much less than the maximum individual dose. (3) The plant effects were so small that they could not be distinguished from fluctuations in natural background. (4) NAD - No activity detected above the minimum dectable level. The less than value reported is the dose corresponding to the HDL. (5) The maximum organ based on Method I was the GI-LLI gastro intestinal tract - lower large intestine. For Hethod 2 the maximum organ was the liver. (6) Does not include the maximum potential dose of 0.45 mrem to an individual from abnormal releases. Doses due to these incidences were not detected in the environmental samples. n
O TABLE 5.2 STANDARDS FOR PUBLIC EXPOSURE TO RADIATION DOSE (MILLIREM) ITEM CATEGORY FRC(1) NCRP(4) ICRP(6) (1) Whole Body Maximum 500 500 500 2) Average 170 170 170 (2) Thyroid Maximum 1500 1500(5) 1500 Average 500 (3) Bone Maximum 1500 3000(5) 3000 Avera ge 500 (4) Bone Marrow ( Maximum 500 500 500 Average 170 (5) Skin Maximum 3000(5) 1500(5) 3000 Average (6) Other Organs Maximum 1500( ) 1500(5) 1500 Average (1) Federal Radiation Council, Radiation Protection Guides, Reports 1 & 2, May 1960 & September 1961. (2) Average dose to a large population group. (3) Bone Marrow and other blood forming organs. (4) National Council on Radiation Protection and Measurements, Maximum Permissable Dose, Report 39, 1971. (5) Values are 1/10 and 1/30 of the Occupational Worker Limits. (6) International Commission on Radiological Protection, Maximum Permissable Dose, Publication 9,1965.
e i 6.0 Discussion The variability of the levels of radioactivity in environmental media depends on many factors. These factors include station release rates, meteorology, number and size of nuclear weapons tests, seasonal variability of fallout, soil conditions (mineral content, pH, etc.), pasturing habits of animals, local terrain, and locational variability of natural background. All of these factors need to be considered in order to explain the levels of radioactivity in the environment. Any one could cause significant variations in measured radioactivity. A failure to consider these factors could cause erroneous conclusions. For example, consider the levels of Sr-90 and Cs-137 meas 2 red in cow and goat milk. A casual observer could notice that in some cases the levels of these two isotopes are higher at farms closer to the station than at those further away from the station. The station effluents might at first appear to be responsible. However, the investigation of the following facts proves this conclusion wrong. 1. The station accurately measures Sr-90 and Cs-137 in its releases. Based on these measurements and proven models developed by the Nuclear Regulatory Commission, concentrations in the environment i can be calculated. These calculations (generally conservative, see Section 5.0) show that insufficient quantities (by more than a factor of 1000) of Sr-90 and Cs-137 nave been released from the station to yield the measured concentrations in milk. 2. Sr-89 and Sr-90 have similar chemical properties as do Cs-134 and Cs-137. Based on this fact and the ratios of these isotopes in the measured releases from the station, station related Sr-90 could not be detected without detecting Sr-89 and station related Cs-137 could not be detected without detecting Cs-134. i l Since station related Sr-89 and Cs-134 were not detected, the levels observed in the dairy milk samples are from weapons testing. 3. Since dairy milk sampling began in the 1960's, years prior to plant operation, the immediate station areas have always shown higher levels of weapons fallout related Sr-90 and Cs-137 (see Figures 6-1 and 6-2). The ratio of activity between the locations has not changed with plant operation. All areas show the same significant decrease in radioactivity since the 1964 Nuclear Test Ban Treaty. 4. Local variability of Sr-90 and Cs-137 in milk is common through-out the United States. Due to the variability in soil con-ditions, pasturing methods, rainfall, etc., it is the rule rather than the exception. Therefore, it is not surprising-that certain farms have higher levels of radioactivity than other farms. 6-1 m - r-
Based on these facts, the observation that the station effluents are responsible is obviously false. The cause must be one or more of the other variables. Northeast Utilities has carefully examined the data throughout the year and has presented in this report all cases where plant related radioactivity can be detected. An analysis of the potential exposure to the population from any plant related activity has been performed and shows that in all cases the exposure is insignificant. As in previous years, this data is being submitted to, and will be reviewed by the appropriate regulatory bodies such as the Nuclear Regulatory Commission, Environmental Protection Agency and Connect-icut Department of Environmental Protection. l 9 6-2
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Source-1966 - 1973 Connecticut State.Lepartment of Health--average of 1 to 4 samples from each farm-all months 1974 Ioyo webcast Utilities Dct:.--samples from 4 farms for the nonths of Feb and Apr through Oct.
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APPENDIX A Cow and Goat Census for 1979 4 A-1
DAIRY COWS WITHIN 15 MILES OF CONNECTICUT YANKEE AS OF JUNE 1979 Dairy # Name & Address No. of Cows Direction Distance 110 Alfred C. Anderson 30 WSW 17 miles 216 Northford Road Wallingford, CT 06492 66 Charles D. Anderson 18 NW 9.5 miles Blague Dairy Farm 56 Strong Avenue Portland, CT 06480 125 Fred J. & Lawrence Augur 74 WSW 5 -.les Forrest Road Northford, CT 06472 (North Branford) 111 Walter Augur & George Cooke 196 WSW 17 miles Co Ag Fa rm, Inc. 180 Northford Road Wallingford, CT 06492 50 Burton L. Avery Sr. 64 ENE 14 miles Burton L. Avery Farm RFD #4 Rathbun Hill Road Colchester, CT 06415 (Salem) 65 Elbridge F. Ball 16 NNE 16 miles RR 2 Hebron, CT 06248 33 Henry, Albert, and/or Roger Berten 58 W 8 miles Berten's Farm Haddam Quarter Road Durham, CT 06422 43 Dr. David B. Bingham 64 E 11 miles Bingham Farm Rte. 82, RFD 3 (Salem Farm) Colchester, CT 06415 (Salem) 102 Bilger Bros. 32 WNW 15 miles Hickory Grove Farm 705 Westfield Road Meriden, CT 06450 ( i I i
. Dairy # Name & Address No. of Cows Direction Distance 20 E. Leroy Brock 38 WNW 8 miles Brock Farm 796 Ridge Road Middletown, CT 06457 63 William & Shirley Bramley 24 NE l').5 miles Bromley Farm P. O. Box 24 Hebron, CT 067.31 (Amston) 32 Henry Bugai 186 W 12.5 miles Powder Hill Dairy Farm Powder Hill Road Durham, CT 06422 34 Tony Caltabiano 49 W 11.5 miles Friendly Acres Dairy Farm Parmalee Hill Road, RFD Durham, CT 06422 112 David Cella 21 W 14.5 miles 899 Old Rock Hill Road Wallingford, CT 06492 113 Cella Bros. 150 WSW 14 miles Whirlwind Hill 2 No. Branford Street Wallingford, CT 06492 94 Joseph Cieniewicz 46 NW 17 miles Lower Lane Dairy Lower Lane Road Berlin, CT 06037 35 Clark Brothers 29 W 11.5 miles New Haven Road Durham, CT 06422 12 D.B.A. Stoney Hill Farm 47 NE 4.5 miles Waterhole Road Colchester, CT 06415 (Farm in East Hampton)
. Dairy # Name & Addre ss No. of Cows Direction Distance 4 William Dil! 96 ENE 6.5 miles Cloverdale larm Beebe Road East Haddam, CT 06423 98 Frank Dornfried 40 WNW 18 miles 159 Edgewood Road Kensington, CT 06037 92 John W. Dwyer 55 f,SW 16 miles 119 Tanner Marsh Road Guilford, CT 06437 114 Carl Farkas 53 WSW 14 miles 1390 Whirlwind d'11 Road Wallingford, CT 064?? 164 Foothills Farm 63 N 15 miles RFD Hebron. Ci 06248 44 Stuart & Judith Gadbois 1700 E 14 miles RFD #4 Colchester, CT 06415 (Salem) 115 Harold C. Gehrke, Sr. 74 W 15 miles Fairlawn Dairy Farm 178 Grieb Road Wallingford, CT 06492 5 Mortimer A. Gelston 65 ESE 2.5 miles Maple Ridge Farm RFD, Maple Avenue East Haddam, CT 06423 58 Laurel G. Gerow 48 NNE 14.5 miles Wellesway Farm RFD Hebron, CT 06248 12 Goldberg Brothers Farm 50 NNW 17.5. miles 1203 Hebron Avenue i Glastonbury, CT 06033 6 Grandpa Hill Farm 69 ENE 6 miles R.S., R.S. Jr. Cone RFD, Box 251 East Haddam, CT 06423 l l l l
. t Dairy # Name & Address No. of Cows Direction Distance 103 Charles Greenbacker & Sons, Inc. 48 W 14.5 miles Farm #1 743 Murdock' Avenue Meriden, CT 06450 104 Charles Greenbacker & Sons, Inc. 124 W 14.5 miles Farm #2 743 Murdock Avenue Meriden, CT 06450 93 Thomas W. Haggarty 48 SW 13 miles RFD #2 Hoop Hole Road Guilford, CT Co437 i 13 Halls Pride. Farm 23 NNW 2.5 miles John and/or Beverly Hall RR #1 HaJdam East Hampton, CT 06424 95 John Hanson 34 WNW 15 miles 506 Spruce Brook Road Berlin, CT 06037 149 J. Ely Harding 67 SE 12 miles Ashlawn Farm Old Lyme, CT 06371 21 Wilbur R. Harris 35 WNW 7 miles RFD #2 174 Wilcox Road Middletown, CT 06457 22 Willie Harvey 75 WNW 7 miles Lee Street Middletown, CT 06457 23 Higgins Fa rm, Inc. 69 NW 13 miles 837 Ridgewood Road Middletown, CT 06457 59 Hills Farm 77 NhE 14 miles 527 Gilead Street Hebron, CT 06248 24 Edward Hills 42 NW 6 miles Brooks Road Middletown, CT 06457 l
. Dairy # Name & Address No. of Cows Direction Distance 69 Henry L. Killan 33 NNW 14 miles Roaring Brook Farm 77 Tryon Street South Glastonbury, CT 06073 25 John Kolman 62 WNW 12.5 miles Meriden Road (Middlefield) Middletown, CT 06457 116 John F. Kranyak 4s WSW 14 miles 1349 Whirlwind Hill Road Wallingford, CT 06492 73 Kristoff Brothers 200 N 15 miles Hyland Farm 183 Bailey Street Glastonbury, CT 06033 99 Edward Kristopik 64 WNW 17 miles 532 Kensington Road Kensington, CT 06037 14 John L. Kruger 14 N 1.5 miles RFD #1 Haddam, CT 74 Louis P., Michael W., Paul J. Longo 130 N 16 miles Minnechaug Farm 2992 Hebron Avenue Glastonbury, CT 06033 64 Mapleleaf Farm, Inc. 145 NNE 14.5 miles Route 2 Gilead, CT 06248 (Hebron) 150 Edward G. Marsh 10 SE 16 miles Mile Creek Road Old Lyme, CT 06371 117 Masonic Charity Foundation 33 W 17.5 miles Masonic Home Farm Wallingford, CT 06492 77 Charles Matway Est. 23 NNW 13 miles Box 238 Brook Street Rocky Hill, CT 06067
. Dairy # Name & Address No. of Cows Direction Distance 45 Marvin S. or Alice Maynard 46 NE 9.5 miles RFD #2 Colchester, CT 06415 101 Judson Meigs 30 NW 17 miles Webster Street Newington, CT 06111 78 John W. Meisterling 46 NW 15.5 miles Meisterling Dairy Farm Box 385 France Street Rocky Hill, CT 06067 28 William J. and/or Thomas E. Mintz 96 WNW 12 miles Walnut Hill Farm Jackson Hill Road Middlefield, CT 06455 t 100 Munson Bros. Dairy 64 WNW 17 miles 756 Kensington Road Kensington, CT 06037 46 John George Mohrlein 58 NE 8.5 miles RFD #1 Colchester, CT 06415 138 Raymond Muschinsky 26 ESE 14.5 miles Grassy Hill Road East Lyme, CT 06333 126 Newton Brothers 26 WSW 17.5 miles Village Street Northford, CT 06472 16 Steven F. Pach 20 E 3.0 miles Pach Stock Farm Town Street Moodus, CT 06469 (Farm in East Haddam) 128 Richard Page 67 WSW 19 miles Totoket Road North Branford, CT 06471 129 Judson W. or Pamela A. Page 62 WSW 19.0 miles Mill Road East North Haven, CT 06473
. Dairy # Name & Address No. of Cows Direction Distance 127 Walter Palasiewski 56 WSW 17.5 miles Box 42, Forest Road Northford, CT 06471 96 Henry Pekrul 75 NW 17 miles 65 Symour Road Berlin, CT 06037 60 Douglas H. Porter 175 KNE 13.5 miles Porter Farm, Inc. RfD #1 Hebron, CT 06248 83 Robert W. Raudat 40 WSW 8 miles Mid Valley Acres Old Durham Road Killingworth, CT 06417 36 Richard H.; Richard R. Rowe 43 W 8.5 miles Box 4 Higganum Road Durham, CT 06422 61 Ronald G. Saglio 71 NNE 15 miles Wood Hill Farm RFD #1 Hebron, CT 06248 17 Richard Saltus 40 N 6 miles Saltus Farm i Middletown Avenue East Hampton, CT 06424 29 Linus L. Sanstrom, Jr. 31 W 12.5 miles Strickland Road Middlefield, CT 06455 47 Helen Savitsky 29 NE 8 miles RFD #1 Colchester, CT 06415 30 Gustave Schmaltz 65 WNW 12.5 miles Far View Farm Jackson Hill Road Middlefield, CT 06455 79 Steven Schultz 20 NW 15.5 miles 132 France Street Rocky Hill, CT 06067 l l l l
8-Dairy # Name & Address No. of Cows Direction Distance 26 George E. & Marion K. Seifert 35 WNW 8 miles Arbutusland Farm Kelsey Street Middletown, CT 06457 118 Robert C. Self & Janet M. Self 107 W 14.5 miles Fieldstone Farm 63 Grieb Road Wallingford, CT 06492 105 Sievert Dairy Farm, Inc. 50 WNW 13 miles Johnson Avenue Farm #1 Meriden, CT 06450 + 48 Swider, Blanche & Walter 48 ENE 11 miles RFD #3 Colchester, CT 06415 119 Albert Tartaglia, Jr. 16 WSW 16.5 miles 25 No. Airline Road i Wallingford, CT 06492 l i 151 Leon H., Jr. and John J. Tiffany 89 SE 11.0 miles Sterling City Road Old Lyme, CT 06371 120 Tomlinson Cros. 72 WSW 17 miles Three Meadows Farm 355 Woodhouse Avenue Wallingford, CT 06492 121 Claude Tremper 38 WSW 17.5 miles 595 Woodhouse Avenue Wallingford, CT 06492 49 Garry and/or Nadine Vaill 16 E 13.5 miles Forsythe Rd. RFD (Salem) Colchester, CT 06415 62 Jonas & Jane Valys 198 NNE 14.5 miles RFD #1 Hardy Road Hebron, CT 06248 122 Thomas J. Wall 78 W 13 miles 963 Northrop Road Wallingford, CT 06492 97 Mary Wasilewski 45 NW 15 miles Riverside Farm RFD #2 Berlin, CT 06037 (Rocky Hill) 1
.- Dairy # Name & Address No. of Cows Direction Distance 123 Sophie Werbiski 21 W 14 miles North Farms 1069 North Farms Road Wallingford, CT 06492 106 ' Richard L. Westfort 89 WNW 13.5 miles 543 Allen Avenue Meriden, CT 06450 124 Dwight Williams & Sons 60 WSW 16 miles 989 East Center Street Wallingford, CT 06492 37 Raymond R. Wimler 130 WSW 11 miles 4 Guilford Road Durham, CT 06422 i 9 4 4 a I
GOATS WITHIN 20 MILES OF CONNECTICUT YANKEE AS OF SEPTEMBER 1979 Dairy # Name & Address No. of Goats Direction Distance 89 Al-Sa Acres Dairy 18 SW 14.5 miles Emily Bolduc 1029 Hoop Pole Road North Guilford, CT 06437 134 Alan Arch 1 ESE 16.5 miles 27 Marion Drive East Lyme, CT 55 Jason Baker 2 NNE 11 miles Jones Street Hebron, CT 85 Cheryl Barnaba 1 S 12.0 miles E. Pond Meadow Road Westbrook, CT i 8 Philip Bourdon 18 N 7.5 miles Young Street (Rt. 196) East Hampton, CT 06424 163 Annette Beatty 1 ENE 16.5 miles Goshen Hill Road Lebanon, CT 57 Jeff Beaudoin 5 NE 12 miles Old Colchester Road Amston, CT 27 Fred Berner 3 WNW 10.5 miles 27 Ross Road Middlefield, CT-18 Loren Blackford 2 WNW 10.0 miles 35 Knowles Avenue Middletown, CT 06457
. Dairy # Name & Address No. of Goats Direction Distance 56 Joan Bowers 5 NNE 16 miles 350 Wall Street Hebron, CT 42 T. C. Bradshaw 4 NE 7.0 miles Rt. 149 Colchester, CT 38 Lawrence Brown 11 ENE 11.0 miles West Road Colchester, CT f 68 Marilyn Carini 5 N 12.5 miles 797 Mott Hill Road 1 South Glastonbury, CT 51 Nelson Chamberlain 2 NNE 17 miles 51 Webster Lane Hebron, CT i 90 Rosemary Chicoine 1 SW 13.5 miles 1027 Hoop Pole Road North Guilford, CT i 80 Karen Connelly 7 SSW 7.5 miles 277 Roast Meat Hill Road Killingworth, CT 165 Sara Cross 2 NNE 14 miles Rt. 85 Hebron, CT 75 Fenny Damiata 1 15i 13.5 miles 43 North Road Cromwell, CT 9 Susan Dickerson 10 N 6 miles 14 Skinner Road East Hampton, CT 06424 e ~-
. Dairy # Name & Address No. of Goats Direction Distance 1 Don Donofrio 18 NW 1.5 miles Indian Hollow Road Haddam, CT 40 Elizabeth Gillman 2 NE 8.5 miles Cato Corner Road Colchester, CT 87 Michael Garritta 2 S 11.5 miles 254 Cow Hill Road Clinton, CT 2 Norman Horton 1 ESE 6 miles Clark Hill Road East Haddam, CT 135 Marvin E. Johnson 3 ESE 15.5 miles 20 Scott Road East Lyme, CT 136 Ellie Korineck 5 ESE 15 miles 233 Upper Pattagansett Road East Lyme, CT 70 Kim Kristoff 5 N 15 miles Marlborough Road Clastonbury, CT l 39 Jay & Maurice Lizotte 3 NE 11.5 miles Old Hebron Road Colchester, CT 4 81 Beverly Lapham 3 SSW 12 miles River Road Killingworth, CT i 67 Kenneth LaRoche 7 NNW 9.5 miles South Road Portland, CT
\\ Dairy # Name & Address No. of Goats Direction Distance
- 140 Dan Mazzella 4
ESE 18 miles 49 Fairhaven Road Niantic, CT i 82 Donald McDougall 3 SSW 7.5 miles Alders Bridge Road Killingworth, CT 148 Francis McTigue 2 SE 11.5 miles 9 Lyme Street Old Lyme, CT
- 166 Lynn Miller 5
ENE 16.5 miles Goshen Hill Road Lebanon, CT 31 Kerry Monroe 2 W 10.5 miles Wallingford Road Durham, CT 107 Jeff Nagy 1 WSW 17 miles 175 Pond Hill Road Wallingford, CT 53 Elaine Phillips 11 NNE 16.0 miles 310 Burnt Hill Road Hebron, CT 108 Robert Pogmore 11 W 14.5 miles 177 Williams Road Wallingford, C! 7 Fred Riedinger 4 SE 2.5 miles Camp Bethel Road Haddam(, CT
- 141 Walter Reifeiss 3
ESE 18 miles Flanders Road Niantic, CT i
- Goats do not graze, are grain fed.
o o Dairy # Nam, & Address No. of Goats Direction Distance 52 Cynthia Ruth 1 NNE 13.5 miles 8 Porter Road Hebron, CT 167 Jamie Sabo 8 NE 18 miles Rt. 87 Lebanon, CT 15 William Sattler 3 ENE 2.5 miles RFD #1, Box 71 Moodus, CT 41 Joseph Schall 9 ENE 10.5 miles West Road Colchester, CT
- 19 Martha Seifert 1
WNW 8 miles Kelsey Street Middletown, CT 06457 l 88 John Sevanick 1 S 14.5 miles 11 Neck Road Clinton, CT 91 Robert Sperry 7 SW 18.5 miles 22 Broad Street Guilford, CT l
- 86 Victor Trudeau 4
S 11.5 miles 174 Horse Hill Road Westbrook, CT 76 Santo Vinci 2 NW 13.5 miles Coles Road Cromwell, CT 10 Christine Walters 2 NNW 5 miles 96 Chestnut Hill Road East Hampton, CT 06424
- Not used for human consumption, fed to other animals.
Dairy # Name & Address No. of Goats Direction Distance
- 3 Jane Wagoner 2
ESE 6.5 miles l A. P. Gates Road East Haddam, CT 71 Charles Walstedt 11 N 13.5 miles 51 Wassue Road Glastonbu y, CT 54 Kathy Waters 4 NNE 15.5 miles Burnt Hill Road Hebron, CT i 11 Yvonne Webber 2 N 5.5 miles Skinner Street East Hampton, CT 06424 l l 109 Russell Woodman 1 W 18 miles 35 David Drive Wallingford, CT 84 Walter Zanelli 1 W 4.5 miles Brainard Hill Higganum, CT ~ P b O' i
F APPENDIX B Quality Control B-1
i t i t Introduction Northeast Utilities Service Company (NUSCO), acting as the agent for [ i both the Northeast Nuclear Energy Company (NNECO) and the Connecticut l Yankee Atomic Power Company (CYAPCO), maintains a quality assurance (QA) program of its primary contractor of radiological analyses, Interex Corporation (Teledyne for H-3 in water samples). This is accomplished by the use of three types of quality control and is in addition to that [ performed internally by Interex Corporation and by their participation in EPA's Environmental Radioactivity Laboratory Intercomparison Studies f Program. The three types of quality control are: a) Duplicate analyses of actual s'urveillance samples with one laboratory. This type of quality centrol allows an evaluation of the contractor's precision or reproducibility of results. I I b) Cross-check analyses of actual surveillance samples with more than j one laboratory. This intercomparison allows the determination of what agreement the primary contractor has with another laboratory. [ c) Analyses of " spiked" samples. This type of quality control allows 4 a check on the contractor's accuracy of results. t" Method The number and type of QA samples are given in Table 1. In general, the objective was to obtain between 10 and 20 percent of the samples as QA r samples. The results of the program are shown in Tables 2, 3 and 4. i These three tables correspond to the three types of quality control. i For I-131 spikes in milk, the acceptance criteria is based on the require-I ment that the measured value be within 30 percent of the spike. The acceptance criteria for all the rest of the QA is based on the standard l deviation in counting statistics (1 signa,e) only. The standard deviation is divided into the difference between the two measurements (6). The j result then has to satisfy the acceptance criteria as developed from a U.S. Department of Health, Education, and Welfare document, Radioassay i Procedures for Environmental Samples (January 1967). For all Geli analyses the criteria that need be satisfied is that A/ebe less than or equal to 3. For chemistry and beta counting, where the overall error is expected to be higher than the calculated error based on counting statistics only, the acceptance criteria is that A/ebe less than or equal to 4. Conclusion j i For Precision (Table 2), the requirement is that the unacceptable results be less than 10 percent of the number of measurements for that type of ( measurement. General statistics indicate that this value should be approximately 2.5 percent for counting statistics, but other non-counting statistical errors exist such as sample volume, sampling, etc. Hence, i 10 percent has been found to be reasonable criteria. From the totals at 1 the bottom of-Table 2 this requirement is satisfied. l l 1 l B-2
s ~ For Interlaboratory Comparisons (Table 3) the requirement is less stringent than both Precision and Accuracy, that is the unacceptable results be less than 20 percent of the number of measurements for that type of measurement. From the totals at the bottom of Table 3 this requirement is satisfied for all cases except that of Cs (chemistry) in milk. The i problem was investigated by verifying all of the Cs (chemistry) results by Geli spectrometry (Cs-137 Geli). The Geli show acceptable results. For the case of Accuracy, only the p' contractor receives only a small rimary contractor need satisfy the acceptance criteria. The secondary number of samples thus making the evaluation of the secondary contractor difficult. The requirement that need be satisfied by the primary contractor here is the same as that for Precision, that the unacceptable results be less than 10 percent of the number.of measurements for that type of measurement. From the totals at the bottom of Table 4 this requirement is satisfied for all cases except for Gross Beta in air particulates. The investigation of this problem revealed a problem with the geometry method in which the spikes were prepared. This has been corrected. l I B-3 i
s e Table 1 Number of Quality Contro1* Samples Number of Number of Routinea,b Sample Type QC Samples Required Samples Milk 28 112 c Well Water 18 28 Sea Water 3 16 River Water 8 8 Reservoir Water 1 0 Soil 1 16 Bottom Sediment 4 26 Aquatic Flora 4 12 Fish 9 40 Shellfish 3 52 Lobster 0 12 Fruits and Vegetables 0 16 Pasture Grass 0 4 Air Particulate - Gross Beta 37 1092 - Geli 20 252 - Chemistry 8 84
- An additional program is performed by the contractor a - Total for both Millstone and Connecticut Yankee b - Depends on availability c - QC breakdown does not include H-3 analysis; total number of tri-tium QC samples was 29.
l l B-4 l \\
s e Table 2 I-Precision Acceptance Number of Measurements i Media Analysis Criteria Acceptable Unacceptable Milk Sr A/c < 4* 13 1 Sr 4/o ~I 4 14 0 Cs (chemistry) 4/o li 4 14 0 Cs (Geli) A/o53 14 0 187 Water Sr A/o < 4 6 0 H-3 A/c54 7 0 Soil & Geli's A/c < 3 3 0 Bottom Sr A/o li 4 2 1 l ~' Sediment Aquatic Geli's 4/c < 3 5 1 Sr A/c54 4 2 Total Sr's A/c ;E 4 39 4 Cs (chemistry) A/c ;[ 4 14 0 Celi A/o < 3 22 1 i H-3 A/o54 ~7 0
- A = difference between the two values o = standard deviation l
t
i f 4 Table 3 Interlaboratory Comparisons l I Acceptance Number of Measurements Media Analysis Criteria Acceptable Unacceptable t t Milk Sr A/o < 4* 4 2 ss Sr gjg 7 4 5 1 Cs (chemistry) A/o 7 4 2 4 l 13' Cs (Geli) A/c33 6 0 Water Sr A/o < 4 8 0 H-3 A/o34 12 0 4 Soil & Geli's A/c < 3 2 0 Bottom Sr A/c 7 4 2 1 ~ Sediment l Aquatic Gell's A/c < 3 5 2 Sr A/o < 4 6 1 + Total Sr's A/o < 4 25 5 H-3 A/o 7 4 12 0 Geli A/o I 3 13 2 Cs (chemistry) 4/o34 2 4
- A = difference between the two values a = standard deviation l
L ( I t 9 4 b l I I
Table 4 Accuhacy* (Results of Spikes) Number of Measurements i Acceptable Unacceptable Acceptance Primary Secondary Primary Secondary Media Analysis Criteria Contractor Contractor Contractor Contractor 133 Milk I A* * < 30% 4 3 0 1 l Sr A/oj 4*. 4 1 0 0 1 Cs{ total) A/o < 4 2 l 7 Ca A/07 3 4 1 0 0 88" 0 Cs A/o[ 3 2 I Wster . Celi A/o < 3 10 3 2 1 Sr A/o7 4 12t 4 0 0 H-3 A/c5 4 8 2 0 0 i Aquatic
- Geli A/o < 3 1
1 1 0 i Sr A/07 4 2 0 0 1 i Air
- Gross 8 4/o< 4 33 4
Particulate Geli A/o7 4 20 0 Cs (total) A/07 4 8 0 f Sr A/07 4 8 0 33' Total 1 a < 30g 8 3 0 1 Sr 4/07 4 26 5 0 1 Cs (total) A/o7 4 10 1 Geli A/07 3 37 5 3 1 H-3 A/o < 4 8 2 0 0 i i
- Air iodine is not reported as this program is under evaluation.
t
- A = difference between the two values a = standard deviation t
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