ML19276F568
| ML19276F568 | |
| Person / Time | |
|---|---|
| Site: | FitzPatrick  |
| Issue date: | 03/30/1979 |
| From: | Gorman B POWER AUTHORITY OF THE STATE OF NEW YORK (NEW YORK |
| To: | |
| Shared Package | |
| ML19276F567 | List: |
| References | |
| NUDOCS 7904060172 | |
| Download: ML19276F568 (185) | |
Text
{{#Wiki_filter:. . . - - - - - - poler AlHHORITY OF TliE STATE OF fel YORK ANi1UAL BNIR0tEfffAL OPERATING REPORT PARTB: RADIOLOGICALREPORT JANUARY 1,1978-DECEMBER 31,1978 JhES A. FITZPATRICK flUCEAR PGER PlMIT FACILITY OPERATING LICENs3 DPR-59 DoCKETllUMBER50-!53 PREPAREDBY: B. GORMAN WITH ASSISTANCE FROM: K. SZELUGA R. BURNS 7 9 0 4 0 6 01~ll 2
TABLE OF CONTENTS Page I. INTRODUCTION 1 A. Introduction 2 B. Program Objectives 3 II. PROGRAM IMPLEMENTATION AND DESIGN 4 A. Sample Methodology 5 B. Analysis Performed 8 C. Changes in Program 8 III. SAMPLE SUMMARIES 11 IV. ANALYTICAL RESULTS 35 V. RESULTS STATISTICS AND llIST0 GRAMS 67 VI. DATA SUMMARIES AND CONCLUSIONS 120 A. Lake Program 121
- 1. Periphyton 121
- 2. Bottom Sediments 123
- 3. Mollusks 124
- 4. Gammarus 125
- 5. Fish 126
- 6. Lake Water 127 B. Land Program 128
- 1. Air Particulates 128
- 2. Air Particulate Composites .- 129
- 3. Airborne I-131 129
- 4. Environmental TLD's 131
- 5. Radiation Monitors 131
- 6. Milk 131
- 7. Milch Animal Census 132
- 8. Other Land Samples 133 C. Conclusions 134 D. References 135 VII. HISTORICAL DATA 136 VIII. FIGURES AND MAPS 161 -
i
LIST OF TABLES Page Table 1 Required Sample Cc11ection and Analysis 36 (Lake Program) Table 2 Required Sample Co11cetion and Analysis 37 (Land Program) Tabic 3 Periphyton Results 38 Table 4 Bottom Sediment Results 39 Tabic 5 Mollusk Results 40 Table 6 Gammarus Results 41 Tabic 7 Fish Results 42 Table 8A Water Composite Results, Gross Beta 43 Tabic 8B Water Composite Results,11-3, Sr-89, Sr-90 44 Tabic 9 Water Composite Results, Gamma Isotopic 45 Tables 10,11 Particulate Filter Results, Gross Beta 46 Table 12 Particulate Composite Results, Gamma Isotopic 50 Tables 13,14 Airborne I-131 Results 52 Table 15 TLD Results 56 Table 16 Radiation bbnitor Readings 57 Table 17 Milk Results, I-131 61 Table 18 Milk Results, Gamma Isotopic, Sr-90 62 Table 19 Milch Animal Census Results 63 Table 20 Food Product Results 65 ii
LIST OF FIGURES Page Figure 1 Off-Site Environmental Station and TLD Locations 163 Figure 1A Off-Site /On-Site Radiological Monitoring Stations 164 Figure 2 On-Site Environmental Station and TLD Locations 165 Figure 3 Milk, Meat, Poultry, Eggs Sample Locations 166 Figure 4 Milch Animal Census Locations 167 Figure 5 Regional Physographic Shp 168 Figure 6 Graph - Periphyton (Cc-144) 169 Figure 7 Graph - Periphyton (Co-60) 170 Figure 8 Graph - Bottom Sediment (Cs- 137) 171 Figure 9 Graph - Bottom Sediment (Co-60) 172 Figure 10 Graph - Mollusk (Mn-54) 173 Figure 11 Graph - Mollusk (Co-60) 174 Figure 12 Graph - Fish (Cs-137) 175 Figure 13 Graph - Fish (Sr-90) 176 Figure 14 Graph - Lake Water (gross beta) 177 Figure 15 Graph - Air Particulate (gross beta) 178 Figure 16 Graph - Milk (Cs-137) 179 Figure 17 Graph - Milk (I-131) . 180 Figure 18 Graph - Milk (Sr-90) 181 iii
I. INEODUCTION
l-A INTRODUCTION The Power Authority of the State of New York (PASNY) is the owner and licensee of the James A. FitzPatrick Nuclear Power Plant (JAFNPP) which is located on the eastern portion of the Nine Mile Point promontory approximately one-half mile due east of the Niagara Mohawk Power Corpor-ation (HMPC) Nine Mile Point Nuclear Station (NMPNPS) . The NMPNPS unit
#1 is located on the most western portion of the site and is a boiling water reactor wi th a design capacity of 610 MUe. The NMPNPS has been in commerical operation since the fall of 1969. Located between the JAFNPP and NHPNPS, Nine Mile Point unit #2 is under construct!on. NMPNPS unit
#2 will have generation capacity of 1100 MWe and is expected to be completed in 1984. The JAFNPP is a boiling water reactor with a power output of 820 MWe (net). Initial fuel loading of fhe reactor core was completed in November of 1974. Initial criticality was achieved in late November, 1974.
The site is located on the southern shore of Lake Ontario in Oswego County, New York, approximately seven miles northeast of the city of Oswego, New York. Syracuse, New York is the largest metropolitan center in the area and is located forty miles to the south of the site. The area consists of partially wooded land and shoreline. The land adj acen t to the site is used mainly for recreational and residential purposes. For many miles to the west, east and south the county is characterized by rolling terrain rising gently up from the lake, com-posed mainly of glacial deposits. Approximately 34 percent of the land area in Oswego County is devoted to farming. The Radiological Environmental Monitoring Program for the Fitz-Patrick Plant is a site program with responsibility for the program shared by the Power Authority and Niagara Mohawk. identical Technical Speci fications for radiological moni toring of the environment a*. lows for joint sampling and analysis. Data generated by the program is shared by the two facilities with review and publication of the data undertaken through each organization. This report is submitted in accordance with S.cction 5.6.1 of Appendix B, to DPR-59, Docket 50-333. Environmental reports of this nature have been compiled and submitted in semi-annual and annual reports since 1974. This report contains data from samples representing the period from January 1, 1978 to December 31, 1978.
l-B PROGRAM OBJECTIVES The objectives of the Radiological Environmental Monitoring Program are as follows:
- 1. To determine and evaluate the effects of plant operation on the environs and to verify the effectiveness of the controls on radioactive material sources.
- 2. To monitor and evaluate natural radiation leve!s in the environs of the JAFNPP site.
3 <> meet the requirements of applicable federal regulatory guides and limits.
- 4. To provide information by which the general public can evaluate the environmental aspects of nuclear power using data which is factua: and unbiased.
8
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II, Paocani IMPLEMENTATI0fl AND DESIGN 8
ll PROGRAM IMPLEMENTATION AND DESIGN To achieve the objectives listed in Section I-B, sampling and analysis are performed as outlined in Tables 1 and 2 in Section IV. The sample collections for the radiological program are performed by two groups. Texas instruments incorporated, Ecological Services Branch (TIES) performs much of the environnental sampilng. TIES is presently performing the Nine Mile Point Aquatic Ecology Study at the _ site which is required by Section 4.1, Appendix B of DPR-59 The staff required by TIES to perform this study is used to perform the terrestrial sampling required for the site radiological monitoring program. In-plant and remaining terrestrial sampling is performed jointly by the JAFNPP and NMPNPS staf fs.
- 1. SAMPLE COLLECTION METHODOLOGY A. Lake Water (surface water)
The two indicator stations are the respective inlet canals at JAFNPP and NMPNPS. These samples are composited using con- , tinuously running pumps which discharge into large holding tanks. The control station sample is collected from the city of Oswego water intake. The sample is drawn from the intake prior to treatment and is composited in a large sample bottle. Quarterly composi te samples are made up f rom proportional all-quotes of monthly samples. B. Air Particulate / lodine The air particulate glass fiber filters are approximately two inches in diameter and are placed in sample holders in the intake line of a vacuum sampler. Directly down stream from the particulate filter is a 2x1 inch charcoal cartridge used to absorb airborne radiolodine. The samplers run continuously and the charcoal cartr!dges and particulate filters are changed _ on a weekly basis. The particulate filters are composited on a monthly basis by location (off-site, on-site) af ter being counted for gross beta activity. The air sampling stations are located in two rings surrounding the site. The on .ite locations ring the terrestrial area around the plants inside the site boundary.
B. Air Particulate / lodine (Continued) The on-site sampling network is composed of 9 stations. The off :lte air monitoring locations range 6 to 17 miles from the site and is composed of 6 stations. Ai r moni toring locations are shown on Figures Vlli-1, Vill-IA and Vill-2. C. Milk Milk samples are collected in polyethylene bottles from the bulk storage tank at each sampled farm. Before the sample is drawn the tank contents are agi tated from 3 to 5 minutes to assure a homogenous mixture of milk and butterfat. Two gal-lons are collected during the first week of each month from each of the five farms. An additional one gallon is collected from each farm at mid-month to make up the second half of the monthly composite. The complete composite is made up from one gallon collected during the first week of the month and one gallon from the mid-month collection. The samples are frozen and shipped to the analytical contractor within 24 hours of collection in insulated shipping containers. The milk sampling locations are found on Figure Vill-4.
- d. Meat, Poultry and Eggs Semi-annually one kilograrc of meat is collected from locations within a 10 mile radius of the site. Weekly phone calls are made to the local slaughter houses to determine availability of slaughte; d live stock from within the sampling area.
Whenever possible meat samples are collected from locations previously used. Semi-annually one kilogram of poultry and one kilogram of eggs are collected f rom each of three locations within a 10 mile radius of the site. Attempts are made to collect poultry and eggs at the same time as the meat samples. The poultry and eggs are frozen and shipped in insulated containers. Whenever possible samples are obtained from on ously sampled farms (see Figure Vill-3).
. F. Human Food Crops
- Human food crops are collected during the late summer harvest season at locations previously sampled, if available. One kilogram each, of the two types of frui ts and/or vegetables f rom each of the three locations within a ten mile radius of the site are collected. The types of fruits and vegetables sampled depends on what is locally available at the time of collection. Attempts are made to collect at least one broad-leaf type vegetable from each location. The fruits and vege-tables are chilled prior to shipping and shipped fresh in insulated containers (see Figure Vill-3).
d G. Soil Samples Soil samples are required once every three years. No samples were collected during 1978. Soll samples will be collected again during the 1980 sample season. H. Fish Samples Available fish species are removed from the Nine Mile Point Aquatic Ecology Study monitoring collections during the spring and fall collection periods. Samples are collected from a combination of the four on-site sample transects and one off-site sample transect (see Figure Vlil-1). Available species are selected under the following guidelines:
- 1. 0 5 to 1 kilogram of edible portion only of a maximum of 5 species per location.
- 2. Samples composed of more than one kilogram of single species from the same location are divided into samples of 1 kilogram each prior to shipping. A maximum of three samples per species per location are used. Weight of samples are the edible portions only.
Selected fish samples are frozen immediately after collection and segregated by species and location. Samples are shipped frozen within two weeks in insulated containers.
- 1. Gammarus Gammarus (f resh water shrimp) saniples are collected by TIES personnel during the spring and fall season from two on-site locations and from one off-site location. A 0.5 m Tucker Trawl (333 u) 1.0 m Hensen Net (571 u), boxtraps and arti-ficial substrates are used to collect samples. The Gammarus samples are removed from the sampling gear, frozen and shipped to the analytical contractor in insulated shipping containers.
J. Mollusks During the spring and fall seasons at two'on-site and one off-site location benthic samples are collected. The mollusks are collected by d' vers and sorted. The tissue is removed from the shell, frozen and shipped for analysis in insulated con-tainers. K. Bottom Sediments One kilogram of bottom sediment sample is collected at two on-site locations and one off-site location. Samples are collected at the same time and location as the mollusk sanples, where possible, by a diver. The samples are placed in plastic bags, sealed and shipped for analysis in insulated containers. _7_
L. Periphyton Peripyhton samples are collected in the spring and fall season from two on-site locations and one off-site location. Peri-phyton is collected from natural and/or artificial substrates (plexiglass slides). The periphyton is scraped from the substrates into vials, labeled, frozen and shipped in insu-lated containers for off-site analysis. M. TLD (direct radiation) Thermoluminescent dosimeters (TLDs) are used to measure direct radiation in the JAF/NMP-1 environment. The TLD stations are placed 'round the site using a three :one division. The first group of TLDs are located within the site boundary and are called "on-site" TLDs. The second set of TLDs are called "si te boundary" stations and are located at approximately the site perimeter. The third division of TLD stations are the "off-site" stations, located at the off-site air monitoring stations. Each TLD set is made up of 2 CaSO 4 dosimeters (2 chips per dosimeter), scaled in a polyethylene package to insure dosi-meter integrity. The TLD packages are further protected by placement in plexiglass " birdhouses", or bv tape sealing to supporting surfaces. The dosimeters are ct'lected, replaced and evaluated on a quarterly basis.
- 2. ANALYSIS PERFORMED The environmental radiological surveillance saaple analysis is performed by Radiation Management Corporation (RMC) except for the particulate =amples and iodine cartridges which are cou 'eu on site. These two sample media are counted on site to eilitate the compositing of the air particulate filters after gross beta analy-sis and the timely anclysis of charcoal cartridge for Iodine-131.
Other environmental radiological analyses are also performed by RMC. Tables 1 and 2 in section III list the media and the associ-ated analyses. ,
- 3. CHANGES IN Tile PROGRAM A. In April of 1978 the Analytical Contractor for the site environmental surveillance program was changed from the Eberline Instrument Corporation, Midwest Facility, West Chicago, Illinois (EIC) , to the Radiation Management Corpor-ation, Philadelphia, Pennsylvania.
B. A fifth milk sampling locar? was added to the 19'3 sampling program to serve as a cr k c! .ocasion. This farm, designated as location number 13 i, ' > - -eport is located approximately 22 miles south-southwt ok .c site. The sampling station is considered outside the iniluence of the plant.
C. Surface water samples for the first six nonths of the 1978 program were analyzed on site in the plant radiochemistry lab. Starting with July,1978, surface water samples were sent off site for analysis. RMC now p<rforms the analysis as listed in Table 1 Section III. The change in analytical labs resulted in an increase in sensitivity and climinated possible in-plant background interference. D. Air particulate composite sampics prior to July 1978 were analyzed on site in the plant radiochemistry laboratory. The July 1978 air particulate composite sample and subsequent samples were analyzed off site by P.MC. RMC now performs gamma spectral analysis of air particulate composites. As in item C above, the change in analytical laboratories resulted in an incre ', in sensitivity and eliminated possible in-plant background interference.
- c. The milk sample station designated as location number 4 (see Figure VIII-4) is new for the 1978 sampling season. On2 of the farms used in previous sampling seasons declined to participate in the sampling program for 1978. This replacement sampling station was found prior to the beginning of the 1978 grazing season and is located approximately 7 miles east-southeast of the site.
D
III. SMPLE SuT% RIES
III. SAMPLE SU5MARIES Environmental sample data is summari&cd by the following methods:
- 1. All sample data is summarized in table form. The tables are titled " Environmental Sample Statistical Analysis" and use the following format:
- 1. Sample medium
- 2. Type of analysis performed
- 3. Number of analyses performed
- 4. Range of detectable 1cvels. The data column is labeied " lower limits of detection". This wording is not intended to indicate that inclusive data is based on 4.66 sigma of background.
S. Mean value of the data, based on positive measured values. (1)
- 6. Standard Deviation, based on positive measured values.
(The standard deviations represent the variability of measured results for different samples rather than single sample uncertainty). (1)
- 7. Maximum and Minimum values
- 8. Range of the data, calculated by subtracting the minimum value from the maximum value.
- 2. Tables are provided for selected sample media and contain data summaries based on quarterly mean values. These tables are titled " Environmental Sample Summary."
(1) Only positive measured values are used in statistical calculations. The use of MDLs in these calculations would result in the means being biased high and the standard deviations being biased low.
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EtNIROTO' ENTAL SAMPLE STATISTICAL AMLYSIS MEgUti PATiflAY TYPE OF A'lALYSIS NUMBER OF LOWER LIMITS STANDARD liAXIMUM filNIMUi1 SAMPLED PERFOR'iED AtlD Af1ALYSIS OF t'EAN DEVIATION VALUE VALUE RAfiGE (UNITS) IS0 TOPE PERF0P11ED DEIECTION (MANGE) LAKE PERIPHYTON Cs-137 5 0.006 0.11 0.006 0.19 0.05 0.14 pC1/g (wet) Ce-144 5 0.070 0.36 0.50 1.10 0.09 1.01 (cor.tinued) Ra-226 5 0.009-0.070 0.03 0.01 0.04 0.02 .02 Th-232 5 0.02-0.060 0.03 A 0.03 0.03 0.00 Cs-134 5 0.005-0.010 0.011 A 0.01 0.01 0.00 LAKE M0LLL'SK CA M ISOTOPIC I pCi/g (wet) CO:: TROL Be-7 2 0.07-0.10 <CL - - - - K-40 2 0.20-0.30 <EL - - - -
- !n-54 2 0.02 <MDL - - - -
Co-00 2 0.02 (MDL - - - - Ra-226 2 - 0.08 A 0.03 0.08 0.00 Th-232 2 0.08 0.07 A 0.07 0.07 0.0) C2-137 2 0.01 <EL - - - - Cs-134 2 0.01-0.02 <MDL - - - - INM CATOR Be-7 4 0.09-0.10 0.20 A 0.20 0.20 0.00 K-40 4 0.2-0.40 0.60 A 0.60 0.60 0.00 th-54 4 0.03-0.05 0.73 0.93 1.10 0.35 0.75 Co-60 4 0.03-0.04 0.14 0.11 0.22 0.06 0.16 Ra-2 2 6 4 0.06 0.19 0.06 0.23 0.12 0.11 Th-232 4 0.07-0.10 <CL - - - - A - ONLY OME POSITIVE VALUE, NO STAT!STICS POSSIBLE M M M M M M M M M M M M M M M M M
ENVIRONMENTAL SAMPLE STATISTICAL A% LYSIS MED{U:1 . TYPE CF ANALYSIS NUMBER CF LO'.!ER LIMITS STANDARD f1AXIMUM 111N!MUl1 PATOWAY SAMPLED PERFORI'.ED AND ANALYSIS OF MEAN DEVIATI0il VALUE VALUE RANGE (UNITS) ISOTOPE PERF0P11ED DEji ( MiGE)ECTION LAKE MCLLUSK CAMA ISOTOPIC pCi/g (wet) CONTROL (cont.) Cs-137 2 0.01 4DL - - - -
, Cs-134 2 0.01-0.02 <MDL - - - -
$I INDICATOR Be-7 4 0.09-0.10 0.20 A 0.20 0.20 0.00 K-40 4 0.2-0.40 0.60 A 0.60 0.60 0.00 Mn-54 4 0.03-0.05 0.73 0.93 1.10 0.35 0.75 Co-60 4 0.03-0.04 0.14 0.11 0.22 0.06 0.16 Ra-226 4 0.06 0.19 0.06 0.23 0,12 0.11 Th-232 4 0.07-0.10 <MDL - - - -
LAKE MOLLUSK Sr-89. Sr-90 pC1/g (wet) C0" TROL Sr-S9 2 0.02 0.02 A 0.02 0.02 0.00 Sr-90 2 - 0.14 0.02 0.15 0.12 0.03 LAKE MOLLUSK pC1/g (set) _IJNDICATOR Sr-89 4 0.02-0.03 0.05 0.03 0.07 0.03 0.04 Sr-90 4 - 0.14 0.03 0.18 0.10 0.08 A - ONLY ONE FCSITIVE VALUE, H0 STATISTICS POSSIBLE
ENVIRONMENTAL SAMPLE STATISTICAL ANALYSIS MED[UM PATNAY TYPE OF ANALYSIS NUMBER OF LOWER LIMITS STANDARD f%XIMUM MINIMUM SAMPLED PERFORMED AND ANALYSIS OF MEAfl DEVIATI0tl VALUE VALUE RAtlGE (UNITS) ISOTOPE PERFORi:ED DE{tECTigf1 ( ANGE LAKE BOTTOM CAru ISOTOPIC SEDIMI.NT -90 pCi/q (dry) v ! T RO'. K-40 2 - 12.00 1.41 13.00 11.00 2.00 1 Co-60 2 0.06-0.07 <MDL - - - - 8 Ra-103 2 0.03 <cL - - - - S5-125 2 0.01 0.10 A 0.10 0.10 0.00 Cs-134 2 0.05 <MDL - - - - Cr-137 2 - 0.61 0.15 0.71 0.50 0.21 Bala-140 2 0.05-0.06 <MDL - - - - Ra-226 2 - 0.97 0.04 1.00 0.94 0.06 Th-232 2 - 0.85 0.07 0.90 0.80 0.10 Sr-90 2 - 0.05 0.01 0.04 0.06 0.02 I.AKE SOTTOM CA"MA ISOTOPIC SEDIMEST ISDICATOR pCi/g (dry) K-40 4 - 13.25 2.22 15.00 10.00 5.00 Co-60 4 - 0.65 0.59 1.50 0.18 1.32 Ra-103 4 0.03-0.04 0.04 A 0.04 0.04 0.00 Sb-125 4 0.10 <McL - - - - Cs-134 4 0.05-0.06 0.30 A 0.30 0.30 0.00 Cs-137 4 - 0.99 0.80 2.10 0.24 1.86 Ssla-140 4 0.08-0.06 0.09 A 0,09 0.09 0.00 Rc-226 4 - 0.46 0.14 0.62 0.30 0.32 Th-232 4 - 0.53 0.15 0.70 0.40 0.30 Sr-90 4 0.01-0.02 0.015 A 0.015 0.015 0.00 A - 0:JLY C'!E POSITIVE VALUE, NO STATISTICS POSSIBLE M M M M - M M M M M M M M M M M M
ENVIRONMENTAL SAMPLE STATISTICAL ANALYSIS MED{UM TYPE OF ANALYSIS NUMBER OF LOWER LIMITS STANDARD f1AXIMUM MINIMUM PAThW SAMPLkb PERFORI1ED AND ANALYSIS OF MEAN DEVIATION VALUE VALUE RANGE (units) ISOTOPE PERFORMED ECTi DgiANGEgN LAKE CAFf4ARUS GA?DIA ISOTOPIC pC1/g (wet) Sr-89, Sr-90 CONTROL Be-7 2 0.20 0.05 A 0.05 0.05 0. 00 K-40 2 0.40 0.80 A 0.80 0.80 0.00 Mn-54 2 0.005-0.02 <MDL - - - - Cs-137 2 0.02 0.028 A 0.028 0.028 0.00 Ce-144 2 0.10 0.03 A 0.03 0.03 0.00 Ra-226 2 0.05 0.027 A 0.027 0.027 0.00 Sr-89 2 0.03-0.07 < MDL - - - - Sr-90 2 - 0.14 0.01 0.14 0.13 0.01 b INDICATOR 7 Be-7 4 0.70-0.70 0.09 A 0.09 0.09 0.00 K-40 4 0.10-0.20 1.05 0.49 1.40 0.70 0.70 Mr-54 4 0.009-0.05 0.10 A 0.10 0.10 0.00 Cs-137 4 0.07-0.08 0.05 0.00 0.05 0.05 0.00 Ce-144 4 0.20-0.70 0.08 A 0.08 0.08 0.00 Ra-226 4 0.03-0.20 <MDL - - - - Sr-89 4 0.04-0.2 <MDL - - - - Sr-90 4 - 0.17 0.04 0.21 0.13 0.18 A - ONLY ONE POSITIVE VALUE, NO STATISTICS POSSIBLE
ENVIRONMENTAL SAMPLE STATISTICAL ANALYSIS MED UM PATb{'AY SAMPLED TYPE OF ANALYSIS FERFOR'iED AND NUMBER OF ANALYSIS LOWER LIMITS OF MEAN STANDARD DEVIATION MAXIMUM VALUE MINIMUM VALUE RANGE (UNITS) ISOTOPE PERF0PJiED ECTI LgoANGEgN LAKE FIS!! GX01A ISOTOPIC pCi/g (wet) Sr-39, Sr-90 ccNTROL K-40 9 - 2.94 1.11 5.70 1.90 3.80 g Mn-54 9 0.01-0.03 <MDL - - - - es ts-137 9 0.02 0.09 0.05 0.20 0.04 0.16 f Ce-141 9 0.01-0.03 <MDL - - - - Ce-144 9 0.06-0.10 0.11 A 0.11 0.11 0.00 Sr-89 9 0.005-0.02 <MDL - - - - St-90 9 0.003-0.005 0.01 0.004 0.015 0.004 0.01 INDICATOR K-40 19 - 2.06 0.49 2.90 1.10 1.80
!b-54 19 0.009-0.02 0.02 A 0.020 0.020 0.00 Cs-137 19 0.02 0.08 0.02 0.10 0.03 0.07 Cc-141 19 0.006-0.03 0.03 A 0.030 0.030 0.00 Ce-144 19 0.04-0.10 <MDL - - - -
Sr-69 19 0.006-0.01 0.010 0.001 0.015 0.014 0.001 Sr-93 19 0.003-0.006 0.013 0.006 0.025 0.004 0.021 LAKE WATER GROSS EETA AALYSIS CCNTROL FCi/1 12 9.10 3.55 1.58 6.10 0.50 5.60 H ICATOR 24 9.40-9.50 4.53 2.62 11.10 0.60 10.50 A - 0:4Lv of;E POSITIVE VALUE, NO STATISTICS POSSIBLE M M M M M M M M M M M M M
EfNIR0 iMENTAL SAMPLE STATISTICAL ANALYSIS MED{UM TYPE OF ANALYSIS NUER OF PATHWAY LOWER LIMITS STANDARD MAXIMUM MINIMUM SA& LED FERFOREED AND ANALYSIS OF MEAN PEVIATION VALUE VALUE RANGE (UNITS) ISOTOPE PERFORMED DETECTION (RANGE) TRITIU:: LAKE 'JATER CONTROL 4 None 303.75 127.51 490.00 215.00 275,00 ANALYSIS pC1/1 INDICATOR 8 None 389.38 119.94 560.00 253.00 307.00 h Sr-89 y CCNTROL 4 0.90-5.00 <MDL - INDICATOR 8 0.90-5.00 0.70 0.10 0.80 0.60 0.20 Sr-90 CfNTROL 4 2.00 0.90 0.10 1.00 0.80 0.20 INDICATOR 8 2.00 0.80 0.30 1.10 0.40 0.70 LAKE 'JATER CAT!A ISOTOPIC
- A"ALYSIS CONTROL pC1/1 Co-C0 12 0.60-3.20 14.53 8.38 24.10 8.50 15.60 Fe-59 12 0.70-19.90 <MDL - - - -
Ma-54 12 0.30-3.00 5.40 2.J3 7.40 3.40 4.00 Co-SS 12 0.30-7.90 12.20 A 12.20 12.20 0.00 Nb-95 12 0.30-S.30 <MDL - - - - Cs-137 12 0.40-9.80 <MDL - - - - Cs-1 % 12 0.30-8.70 <MDL - - - - Cr 12 3.00-51.20 <MDL - - - - Ce-141 12 0.40-8.00 <rDL - - - - Bala-140 12 0.60-26.10 21.60 A 21.60 21.60 0.00 2n-65 12 3.01-17.40 <*nt - - - A - ONLY Cf:E P03ITIVE VALUE, NO STATISTICS POSSIBLE
ENVIRONMENTAL SAMPLE STATISTICAL ANALYSIS MEDJUM 111NIMUM TYPE OF AMLYSIS NUMEER OF LOWER LIMITS STANDARD !!AXIMUM PAT 9Y RANGE SAMP! D PEPf0PJ1ED AND ANALYSIS OF MEAN DEVIATION VALUE VALUE (UNITS) ISOTOPE PERFORiiED DgiANGE)ECTION LAKE k'ATER CAMPA ISOTCPIC A!:ALYSIS CONTROL (cent.) pCL/1 1-133 12 1.00-6.00 <MDL - - - - 1 $I INDICATOR Co-60 24 0.50-3.20 19.10 9.08 33.00 4.00 29.0 Fc-59 24 0.70-16.50 <MDL - - - - ltn-54 24 0.40-12.10 5.38 3.81 9.00 0.60 8.40 Co-53 24 0.40-7.90 8.60 6.65. 13.30 3.90 9.40 Nb-95 24 0.40-13.50 <MDL - - - Cs-137 24 0.50-8.20 3.55 1.34 4.50 2.60 1.90 Cs-134 24 0.40-6.60 <MDL - - - Cr-51 24 3.00-46.30 4GL - - - - Ce-141 24 0.60-6.90 9.00 A 9.00 9.00 0.00 Bala-140 -24 0.70-23.60 22.80 A 22.80 22.80 0.00 Zn-65 24 2.00-17 al' 19.50 A 19.50 19.50 0.00 I-133 24 1.00-6.00 3.40 A 3.40 3.40 0.00 AIRBORNE GROSS BETA ACTIVITY PARTICL' LATE CONTROL 315 0.14 0.13 0.66 0.01 0.65 ANALYSIS pC1/m3 1sntcATOR 466 No. e 0.10 0.09 0.34 0.01 0.33 A - ONLY ONE POSITIVE VALUE, NO STATISTICS POSSIBLE M M M M M M M M M '
ENVIRONMENTAL SAMPLE STATISTICAL ANALYSIS MEgUM TYPE OF ANALYSIS NUMBEP, 0F LOWER LIMITS STANDARD 11AXIMUM MINIMUM PATHNAY SAMPLED PERFORMED AND ANALYSIS OF MEAN DEVIATION VALUE VALUE RANGE (Uru Ts) ISOTOPE PERFORMED ECTi DgJNGEgN AIRBORNE GATA ISOTOPIC P.1RTICf3. ATE CCNTROL MALYj t s
, pC1/7 Co-(0 12 0.500 1.73 2.15 5.60 0.03 5.57 3
ba X10 Fe-59 12 0.275-0.627 <MDL - - - - 7 Mn-54 Ca-53 12 0.30-0.40 0.99 1.07 2.64 0.06 2.53 12 0.11-0.41 0.89 0.03 0.91 0.87 0.04 Nb-95 12 0.20-0.40 2.39 0.814 3.81 1.32 2.49 Zr-95 12 0.40-0.60 1.05 0.45 1.65 0.47 1.19 Cs-137 12 None 1.83 1.07 '4.20 0.75 3.45 Cs-134 12 0.11-0.40 0.34 A 0.34 0.34 0.00 Jr-51 12 0.85-3.00 0.91 A 0.91 0.91 0.00 Cr-144 12 None 8.78 7.95 24.00 3.20 20.80 Sala-140 12 0.16-1.03 4.68- 4.31 7.73 1.63 6.10 I-131 12 0.16-0.21 2.50 A 2.50 2.50 0.00 INDICATOR 1431 12 0.16-0.25 4.60 A 4.60 4.60 0.00 Cc-60 12 None 2.25 4.33 15.30 0.32 14.98 Fe-59 12 0.19-0.59 <MDL - - - - th- 5 '. 12 0.30 0.68 0.70 2.45 0.21 2.24 Co-55 . 12 0.10-0.23 0.31 0.26 0.69 0.03 0.61 r5-95 12 0.10-0.20 0.87 0.53 1.56 0.24 1.32 2r c5 12 0.20-0.30 0.97 0.49 1.55 0.43 1.13 Cs-137 12 None 1.60 1.04 3.31 0.30 3.01 Cs-134 12 0.10-0.21 <MDL - - - - Cr-51 12 0.70-1.72 <MDL - - - - C<-144 6 Note 5.13 5.23 15.0 1.53 13.30 Bala-140 12 0.10-0.80 2.27 2.07 4.49 0.41 4.09 A - ONLY ONE POSIT!'/C VALUE, NO STATISTICS POSSIBLE
ENVIROEENTAL SAMPLE STATISTICAL ANALYSIS MEDJUM NUP3ER OF LOWER LIMITS STANDARD fiAXIMUM MINIMUM TYPE OF ANALYSib FATh!)AY EEAN [EVIATION VALUE VALUE PANGE SAMFLED FERF0FJ'ED AND ANALYSIS OF (UNITS) ISOT0FE FERFOR"ED 0{SANT,E)ECT10i1 AIRBORNE ICDINE CWO'A ANALYSIS ANa1.YSIS ICCINE -131 315 0.02-0.20 0.03 0.01 0.04 0.03 0.01 pC1/e 3 C0"TR3L INDICATOR 468 0.01-0.17 0.04 0.02 0307 0.02 0.05 i N y EN'.'IRC? MENTAL TOTAL DCSE TC ET.ADINOS F E S. QARTER mret/qtr. CFF SITE 10.33 1.51 12.00 8.00 4.00 First Q2arter 6 - 10.00 2.03 Second Quarter 5 - 11.00 0.71 12.00 7 - 10.14 1.95 13.00 7.03 6.00 7.trl Q2arter 11.57 1.51 14.00 10.03 4.00 teerth Quarter 7 - SITE E0'NDRY Tirst 7.;arter 5 - 11.00 2.35 14.03 9.00 5.00 Se2ond Quarter 5 - 11.60 0.55 12.C1 11.00 1.03 10.40 0.f9 11.00 9.00 2.03 Third Quarter 5 - Faurth quarter 5 - 11.60 1.14 13.03 10.00 3.03 A - ONLY ONE PCSITIVE VALUE, NO STATISTICS FOSSIELE E E - M M g
ENVIRONMENTAL SAMPLE STATISTICAL ANAtYSIS .. MED PATH)JUM AY SAM? LED TYPE OF ANALYSIS NUMBER OF LOWER LIMITS STANDARD NAXIMUM MINIMUM PERFORiiED AND ANALYSIS OF MEAN DEVIATION VALUE VALUE RANGE (UNITS) ISOTOPE PERFOR'1ED DE{ECTION b ANGE) CONT INL'0'!S DOSE RATE RADIATION LOCATION MO5ITORS mr/hr (average renth1, OFF-SITE value). C 12 - 0.029 0.006 0.040 0.020 0.022 1
$I -
ON-SITE D- 1 12 0.029 0.007 0.043 0.020 0.023 D-2 12 - 0.022 0. 00 5 0.030 0.015 0.015 E 12 - 0.020 0.002 0.022 0.016 0.006 F 12 0.016 0.002 0.020 0.014 0.006 C 12 0.04 0 0.007 0.047 0.020 0.027 li 12 - 0.026 0.003 0.031 0.021 0.010 I 12 - 0.016 0.003 0.020 0.013 0.007 J 12 - 0.019 0.004 0.030 0.013 0.017 K 12 0.018 0.003 0.025 0.015 0.010 MILK ANALYSIS 10 DINE-131 pCi/1 te_c.iTION
;b 1 7 0.10-0.20 <MDL - _ _ _
- n. 2 7 0.10-0.20 <MDL . . _ _
- 50. 3 7 0.20-0.30 <MDL - _ _ _
No- 4 7 0.20-0.30 0.19 A 0.19 0.19 0.00 M. 5 (control) 7 0.10-0.20 <MDL - _ _ _ l A - ONLY ONE POSIT!VE VALUE, NO STATISTICS F3SSIBLE
ENVIRON:1 ENTAL SAMPLE STATISTICAL ANALYSIS MED UM PATH {lAb e SAMPLE (UNITS) TYPE OF ANALYSIS PEEFOPEED AND NUMEER OF ANALYSIS LOWER LIMITS F OF MEAN STANDARD DEVIATION f%XIMUM VALUE MINIMUM VALUE RANGE ISOTOPE PERFORMED D.,jECTIgN U ANGE MILK ANALYSIS GMC'A ISOTOPIC pC1/1 Sr-90 J.0_ CATION
, No. 1 7 - 6.27 1.03 740 4.70 2.70 ra Na. 2 7 -
5.16 1.25 7.30 3.40 3.90 4.67 1.84 I No. 3 7 - 8.10 2.50 5.(0 No. 4 7 - 7.60 1.70 10.00 5.20 4.80 No. 5 (control) 7 - 5.89 2.04 9.00 3.00 6.00 MILK ANALYSIS OMC4A ISOTOPIC pC1/1 LOCATION No. 1 K-40 7 - 1422.86 308.21 1900.00 960.00 940.00 Cs-137 7 - 11.60 8.75 30.00 3.50 26.50 Na. 2 K-40 7 - 1371.43 298.41 1600.00 800.00 800.00 Cs-137 7 - 6.99 2.57 12.00 3.70 8.30 No. 3 K-40 7 - 1347.14 241.99 1600.00 930.00 670.00 Cs-137 7 - 5.70 2.26 9.70 3.40 6.30 NO. 4 K-40 7 - 1478.57 336.47 1900.00 950.00 950.00 Cs-137 7 - 15.46 8.28 33.00 9.20 23.80 A - ONLY ONE POSITIVE VALUE, NO STATISTICS POSSIBLE M M M
....- g . . g g - - - - -
ENVIRONMENTAL SAMPLE STATISTICAL ANALYSIS MED{UM TYPE OF ANALYS:S NUMBER OF LOWER LIMITS STANDARD MAXIMUM MINIMUM PATOWAY VALUE RANGE SAMPLED PERFORIED AND ANALYSIS OF MEAN DEVIATION VALUE (units) ISOTOPE PERF0F11ED DFIECTION CO NGE ) MILK ANALYSIS GA}StA ISOTOPIC pCi/1 LOCATION (cont.) No. 5 K-40 (c ont rol) 7 - 1284.29 221.50 1600.00 990.00 610.00 i Cs-137 7 - 5.83 1.98 7.30 2.40 5.40 t.n PEAT 6 POULTEY GAT 4A ISOTOPIC pCi/g (wet) IADICATOR - Be-7 10 0.03-0.04 4TL - - - - K-40 10 - 2.10 0.46 2.80 1.50 1.3 St,- 54 10 0.03-0.04 <MDL - - - - Sb-125 10 0.003-0.01 0.01 A 0.01 0.01 0.00 Cs-137 10 0.004-0.005 0.021 0.011 0.040 0.013 0.027 R.2-226 10 0.006-0.01 0.013 A 0.013 0.013 0.00 CHICKEN EGGS GASD% ISOTOPIC pCi/g (wet) I'Q!CATOR 3e-7 4 0.03-0.04 <MDL - - - - K-40 4 - 1.08 0.32 1.40 0.72 0.68 it,-54 4 0.03-0.04 <MDL - - - - sb-125 4 0.009-0.01 <!DL - - - - Cc-137 4 0.04-0.05 <MDL - - - - 2a-226 4 0.008-0.01 <MDL - - - - A - Or:LY ONE POSITIVE VALUE, NO STATISTICS POSSIBLE
EINIRONMENTAL SAMPLE STAT!STICAL Ai!ALYSIS MED{UM T'PE OF ANALYSIS NUMEER OF LOWER LIMITS STANDARD MAXIMUM MINIMuit PATfBAY RANGE SAMPLED PERFORIiED AtlD ANALYSIS OF MEAN DEVIATION VALUE VALUE (UnTS) ISOTOPE PERF0PJ1ED DgnANGE)ECTION PRODUCE CA..IA
.* ISOTOPIC pC1/g (vet)
K-40 9 None 2.21 1.39 4.80 0.80 4.0 th-54 9 0.003-0.01 0.011 A 0.011 0.011 0.000 3 Sb-125 9 0.007-0.04 <MDL - - - - $i Cs-137 Ra-226 9 9 0.003-0.01 0.006-0.03 0.01
<KDL A
0.01 0.01 0.00 Be-7 9 0.02-0.10 0.07 A 0.07 0.07 0.00 I-131 9 0.003-10.00 <MDL - - - - A - ONLY 0:4E POSIT!VE VALUE, NO STATISTICS POSSIBLE M
w -- - - - umsmus - - --mme - - -
ENVIRONMENTAL SAMPLE
SUMMARY
Medium / Sample Location Nuclide 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Water pCi/1 Monthly Composite NMP Inlet Co-60 16.0 < 8.1 <1.2 <2.3 Fe-59 <14.6 <13.9 <2.2 <2.7 Mn-54 < 7.0 < 1.0 < 1.1 < 1. 0
..o-58 < 1.3 < 7.5 <1.1 <l.0 Nb-95 < 6.3 < 6.3 < l .1 <1.0 Zr-95 <11.5 < 10. 5 <l.6 <1.7 Cs-137 < 4.6 < 7.5 <1.2 <l.3 Cs-134 < 6.4 < 5.7 <l.5 <1.3 Cr-51 <43.7 < 41. 0 <7.7 < 7.3 Ce-141 < 7.6 < 6.4 <1.5 < 1. 0 Ba-La-140 <21.8 < 22.4 <1.6 <2.0 Gross Beta < 7.5 3.6 2.5 <2.0 b <1.5 y JAF Inlet Co-60 11.2 < 17. 7 <l.3 Fe-59 <12.7 <13.6 <1.9 <2.7 Mn-54 1.4 < 3.8 <0.8 <1.0 Co-58 < 1.3 < 9.4 <0.8 < l .0 Nb-95 < 6.4 < 6.2 <1.1 <1.0 Zr-95 <10.8 <10.9 <1.5 <1.7 Cs-137 < 7.4 < 7.1 <1.2 <2.0 Cs-134 < 5.8 < 6.0 <1.5 <3.0 Cr-51 <42.1 <43.8 <7.0 <9.7 Cc-141 < 6.3 < 6.5 <1.5 <1.7 Ba-La-140 <21.5 <21.8 <1.6 <2.0
. css Beta < 8.4 7.5 2.1 3.1
ENVIRONMENTAL SAMPLE
SUMMARY
Medium / Sample Location Nuclide 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Water (Cont.) pCi/1 Monthly Raw City Composite Water Co-60 14.5 < 1.1 <1.5 <2.0 Fe-59 <16.9 <13.7 <2.2 <2.7 Mn-54 0.0 < 4.6 <0.8 <1.3 Co-58 < 2.6 < 6.7 <0.8 <1.0 Nb-95 < 6.9 < 6.3 <1.1 <1.0 Zr-95 <11.1 <11.7 <1.5 <2.0 Cs-137 < 8.2 < 7.1 <1.1 <1.3 Cs-134 < 7.0 < 5.9 <1.4 <1.3 Cr-51 <45.0 <42.5 <7.7 <8.7 Ce-141 < 7.1 < 6.5 <1.1 <1.7 Ba-La-140 <23.7 <22.2 <1.9 <2.0 Gross Beta < 6.5 4.4 2.3 2.8 5
, .g , , , y ENVIRONMENTAL SAMPLE SUhNARY bledium/ Sample Location Nuclide 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Airborne pCi/m 3 Particulate On-Sites Gross Beta Filters D1 0.11 0.18 0.14 0.03 D, 0.10 0.16 0.13 0.04 E' O.10 0.17 0.08 0.03 F 0.11 0.18 0.14 0.05 G 0.10 0.16 0.14 0.05 11 0.07 0.15 0.12 0.02 I 0.06 0.12 0.11 0.03 J 0.07 0.12 0.09 0.02 K 0.04 0.10 0.10 0.02 Off-Sites hi C 0.11 0.27 0.16 0.05 Di 0.10 0.23 0.16 0.05 D, 0.09 0.26 0.18 0.05 E' O.11 0.26 0.17 0.06 F 0.10 0.25 0.21 0.05 G 0.09 0.25 0.14 0.04
4 0
. I v
b d *t *t en en en M M NM en tn en en en =t U Cy C. O. O. O. O. O. O. O. O. O. O O. O. O. O. OCOOOOOOO OOOOOO M V V V V V V V V V V V V V V V u
'T b
o w 4 d *t 't M et M rn N N 0 J *t M et M in et O O' O. O O. O. O O. O. O. O. O. O. O. O. O O. OOOOOOOOO OOOOOO 9 V V V V V V V V V V V V V V V rn b c M b d en 't en en 't N N N N rn M rn en et en 3 Cy O. O. O. O. O. O. O. O. O. O. O. O O. O. O. OOOOOOOOO OOOOOO "U V V V V V V v v v V V V V V V C N 4 O H b d "tinLnLnLnLnentnen 4 D M en D Ln D Cy O O O. O. O. O. O . O. O. O. O O. O. O O. OOOOOOOOO OOOOOO M V V V V V V V V V V V V V V V
.O
-e O
7 in
.e4 ve Q
- en N O .-4 .ee O l U Z M G.
> C W O M O O M f ..< M p ..< (f) ( <. c3
.e to e D U e %
(n O C mN % MN 4 O CO'4WCCwnW O UCOWWO
)
C. sn 1 O "C - a E d d
- M O
E t/J O '/. N 03 O O g O *H o U k .cf. 3e ,o 44 y
"O b
.e d 4
.C d 0
N Z ='C UV ENVIRONMENTAL SA5fPLE SUBMARY Medium / Sample Location Nuclide 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Airborne pCi/m 3 Particulate On-Site Co-60 5.9E-03 9.0E-04 6.lE-04 8.6E-04 Composite Fe-59 < 4. 0E-04 < 3. 6E-04 < 3.0E-04 < 3.0E-04 Mn-54 1.3E-03 4.0E-04 < 2.6E-04 4.4E-04 Co-58 < 3.9E-04 <3.4E-05 <l.3E-04 <l.4E-04 Nb-95 2.3E-03 2.2E-03 <2.1E-04 <l.0E-04 Zr-95 1.0E-03 9.4E-04 <2.0E-04 <2.0E-04 Cs-137 1.6E-03 2.8E-03 <1.7E-03 3.6E-04 Cs-134 <l.8E-03 <1.8E-04 <l.7E-04 <l.6E-04 Cr-51 <l.3E-03 <l.4E-03 <9.3E-04 <8.0E-04 Ce-141 <3.7E-04 <5.9E-04 <1.0E-04 <1.6E-04 Ba-La-140 <1.9E-03 <l.0E-03 < 2.0E-04 <l.6d-04 I-131 <9.3E-04 <l.lE-04 <l.0E-04 <l.6E-04 O Cc-144 ND ND 8.8E-03 1.6E-03 7 Be-7 ND ND 2.4E-02 2.7E-02 Ru-106 ND ND <4.3E-03 <l.0E-03 Sb-125 ND ND 8.2E-04 <3.7E-04 ND = Not Detected /No MDL
ENVIRONMENTAL SAMPLE SU5 MARY Medium / Sample Location Nuclide 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Airborne pCi/m 3 Particulate Off-Site Co-60 3.5E-03 6.8E-04 <1.0E-03 1.0E-03 Composite Fe-59 <5.7E-04 <2.SE-04 <4.3E-04 <4.3E-04 Mn-54 1.5E-03 7.2E-04 <4.0E-04 <4.7E-04 Co-58 < 7. 3E-03 <1.5E-04 < 2. 7E-04 <1.7E-04 Nb-95 2.9E-03 1.9E-03 < 3. 7E-04 <2.7E-04 Zr-95 1.4E-03 7.3E-04 < 6.0E-04 <4.3E-04 Cs-137 1.2E-03 2.6E-04 2.5E-03 1.1E-03 Cs-134 <2.7E-04 <2.0E-04 <3.3E-04 < 3. 0E-04 Cr-51 <2.1E-03 <6.22-04 < 2. 3E-03 <2.0E-03 Ce-141 <6.5E-04 <4.7E-04 < 3. 7E-04 <3.7E-04 Bata-140 < 3. 2E-03 6.7E-04 <4.3E-04 <4.7E-04 I-131 <1.7E-03 <1.9E-04 <2.3E-04 <2.0E-04 d, Cc-144 ND ND 2.9E-03 4.1E-03 'f Be-7 ND ND 3.2E-02 7.0E-02 Ru-106 ND ND < 5.1 E-0~ <3.0E-03 Sb-125 ND ND <1.2E-03 <S.3E-04 ND = Not Detected /No MDL
ENVIRONh! ENTAL SAFIPLE SUSB!ARY Fledium/ Sample Location Nuclide 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Direct Radiation Continuous On-Sites nrem/qtr b!onitors (G51) D1 51.8 72.1 55.2 77.3 47.5 56.8 50.8 37.5 D2 E 36.7 45.9 44.2 44.2 F 36.7 32.8 35.3 33.1 G 84.2 96.1 94.9 72.9 11 49.7 59.0 61.9 59.6 I 30.2 34.9 35.3 37.5 J 30.2 41.5 44.2 48.6 K 36.7 39.3 39.7 39.7 Off-Site C 67.0 80.8 57.4 48.6 TLDs Off-Site mrem /qtr 10 11 10 12 Site Boundary mrem /qtr 11 12 10 12 On-Site mrem /qtr 48 50 41 40
=
ENVIRONh! ENTAL SAh!PLE SUhMARY bledium/ Sample Location blap #* Nuclide 1st Quarter 2nd Quarter 3rd Quarter 4th Qur.rter pCi/1 Ingestion 1 16 I-131 NS <0.2 < 0. 2 < 0. 2 K-40 960.0 1500.0 1500.0 Cs-137 10.0 17.9 5.9 Sr-90 6.3 7.1 5.5 2 4 I-131 NS < 0.1 < 0. 2 <0.2 K-40 800.0 1470.0 1470.0 Cs-137 5.5 9.0 5.5 Sr-90 5.0 5.3 5.1 3 14 I-131 NS <0.2 <0.2 < 0. 2 K-40 1700.0 1340.0 1430.0 Cs-137 3.9 7.6 4.4 d, Sr-90 4.5 5.8 3.5 T 4 25 I-131 NS < 0. 2 < 0. 2 < 0. 2 K-40 950.0 1500.0 1630.0 Cs-137 12.0 14.3 17.7 Sr-90 10.0 7.1 7.3 5 13 1-131 NS < 0. 2 < 0. 2 < 0. 2 K-40 1200.0 1230.0 1360.0 Cs-137 7.8 7.0 4.0 Sr-90 7.6 6.9 4.3 NS = Not Samples (not in grazing season)
- Figure 4 M M M M M M M M M
IV. ANALYTICALRESULTS
--g.. g g g g g g TABLE 1 SAh!PLE COLLECTION AND ANALYSIS SITE RADIOLOGICAL ENVIRON 5tENTAL E!ONITORING PROGRAh!
A. LAKE PROGRAh!(1) h!EDIA ANALYSIS FREQUENCY (4) LOCATION (2)
- 1. Fish GeLi, 89Sr 4 90 Sr 2/yr 2 onsite 1 offsite
- 2. 51011usks GeLi, 89Sr G 90 Sr 2/yr 2 onsite 1 offsite
- 3. Gammarus GeLi, 89Sr 6 90 Sr 2/yr 2 onsite 1 offsite
, 4. Bottom Sediments GeLi, 90Sr 2/yr 2 onsite 1 offsite 8
- 5. Periphyton GeLi 2/yr 2 onsite 1 offsite
- 6. Lake Water GB, GSA or GeLi El Comp. 3(3) 311, 89S r, 90S r Qtr. Comp.
Notes: (1) Program continued for at Icas+ three years after the startup of James A. Fitzpatrick Nuclear Power Plant. (2) Onsite locations samples collected in the vicinity of discharges, offsite samples collected at a distance ci at least five miles from site. (3) The three lake water samples to include Nine blile Point Unit 1 intake water, James A. Fit: Patrick intake water, an? Oswego City water. (4) Sampics of items 1 through 5 collected in spring and fall when available.
TABLE 2 SAMPLE COLLECTIG:; AND ANALYSIS SITE RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM B. LAND PROGRAM (1) MEDIA ANALYSIS FREQ"ENCY NO. OF LOCATIONS LOCATIONS
- 1. Air Particulates GB W At least 10 9 onsite 6 offsite GSA M Comp. (6)
- 2. Soil GSA, 90Sr Every 3 years 15 9 onsite 6 offsite
- 3. TLD Gamma Dose Qtr. 20 14 onsite 6 offsite
- 4. Radiation Monitors Gamma Dose C la 9 onsite 1 offsite u
Y 5. Airborne - I131 GSA W At least 10 9 onsite 6 offsite
- 6. Milk 1 M 4l7) (8)
GSA, 90Sr M Comp.
- 7. Iluman Food Crops GSA, 131 I A 3 (S)
- 8. Meat, Poultry, Eggs ,
GSA Edible Portion SA 3 (S Notes: (Cont.) (6) Onsite sampics counted together, offsite counted together, any high count sampics counted separately. (7) Frequency applied only dnring grazing season. (8) Samples to be collected from farms within a 10-mile radius having the highest potential concentrations of radionuclides. Abbreviations: M Comp. - Monthly composite of weekly or bi-weekly samples A - Annually BW - Bi-weekly (alternate wks.) GB - Gross beta analysis W - Weekly Qtr. - Quarterly GeLi - Gamma spectral analysis on a GeLi system (quantitative) M - Monthly SA - Semiannually GSA - Gamma spectral analysis on a Nal system (quantitative) C - Continuous M M M M - M M M M M
TABLE 3 CONCENTRATIONS OF GAW EMITTERS IN PERIPHYTON SAMPLES Results ;n linits of pCi/g(wet) t 2 sigma 6-27-78 COLLECTICN NUCLIDES to - SITE FOUND 6-23-78 8-23-78 Off-Site Be-7 0.09t0.07 0.35t0.06 00 K-40 1.710.3 2.210.2 Mn-54 (0.007 0.01110.n07 Co-60 (0.01 0.01310.005 Zr-95 <0.02 0.01220.009 Nb-95 0.019t0.009 <0.004 Ra-106 <0.07 0.09t0.05 Cs-137 0.02310.009 0.06320.or9 Ce-144 0.10t0.06 0.13f0.05 Ra-226 <0.02 0.07110.009 Th-232 (0.03 0.04:0.03 JAF Be-7 0.07 0.04 0.33!0.05 03 K-40 1.Ito.2 2.7 0.1 Mn-54 <0.006 0.00S!0.005 Co-60 < 0. 00 5 0.030rC.006 Zr-95 0.01910.009 0.01410.005 Nb-95 0.01710.007 0.034+0.008 Ru-105 <0.04 0.0610.04 Cs-137 (0.006 0.07230.007 Ce-144 0.09!0.03 0.1220.02 Ra-226 (0.009 0.02420.007 NMPP Be-7 0.3t0.1 0.59t0.06 02 K-40 1.2 0.3 2.120.2 Co-60 0.03 0.01 0.1010.01 Zr-95 0.03 0.02 0.010t0.008 Nb-95 0.04t0.02 0.028 0.008 Ru-106 <0.1 0.09:0.05 Cs-134 <0.01 0.011 0.005 Cs-137 0.05t0.02 0.1210.01 Ce-144 <0.07 0.11 0.03 Ra-226 (0.03 0.042t0.008 Th-232 <0.05 0.0310.02 , hPPW Be-7 1.810.4
- 31 K-40 1.010.6 .
Nb-95 0.0910.04 Ru-103 0.04!0.04 Cs-137 0.19t0.05 Ce-144 1.110.3
- Na S e ple hequired.
~M - - - - .
TABLE 4 CONCENTPATIONS OF Sr-93 AND CAK'A EMITTERS IN SEDIMENT SAMPLES Results in Units of pCi/g(dry) i 2 sige.a COLLECTION COLLECTION GA!!'A EMITTERS SITE DATE Sr-90 K-40 Co-60 Fu-103 Tb-125 Cs-134 Cs-137 Bata-140 Ra-226 Th-232 Off-site 6-27-78 0.06120.003 11 1 <0.06 <0.03 0.120.1 (0.05 0.7120.09 (0.05 1.0!0.1 0.920.2 00 10-02-78 0.C410.01 1312 <0.07 <0.03 <0.1 <0.05 0.5010.08 <0.06 0.9420.09 0.810.2 JAF 6-29-73 0.01520.005 15t2 1.5!O.2 0.0410.04 <0.1 0.3020.07 2.120.2 <0.08 0.320.8 0.420.2 03 NMPP 6-27-78 <0.02 1421 0.3Ct0.06 <0.03 <0.1 <0.06 0.6310.09 0.0910.09 0.520.2 0.720.2 8 02 U$ '10-02-78 (0.02 1422 0.5510.C8 <0.04 <0.1 <0.05 1.020.1 <0.05 0.6220.09 0.620.2 i NMPW 10-02-78 <0.01 1021 0.1820.05 <0.04 <0.1 <0.05 0.2410.08 <0.06 0.420.1 0.4t0.2 01
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TABLE 8A LAKE WATER SAS!PLES MONTilLY COMPOSITE GROSS BETA pCi/1 Date N3fP- 1 JAF OSWP 1/78 < 9.5 <9.4 <9.1 2/78 7.1 0.8 7.8 0.8 4.6 0.7 3/73 5.9 0.5 8.0 0.6 5.8 0.5 4/78 5.7 0.6 7.3!0.8 6.1 0.6 5/78 7.4!0.6 11.li0.7 4.3!0.6 6/78 2.8 0.8 4.1 0.8 2.9 0.7 7/78 2.7 0.6 2.8 0.6 3.4!0.7 8/78 3.6!0.7 2.9 0.6 3.0 0.7 9/78 1.2i0.5 0.6 0.5 0.5 0.5 10/78 2.410.6 2.8!O.7 2.7!0.7 11/78 3.5 0.7 3.3 0.7 2.8 0.6 12/78 3.3!0.6 3.3 0.6 2.9t0.6 I I
TABLE 8B LAKE WATER SAMPLES QllARTERLY COMPOSITE pCi/1 _ Location Date 11- 3 Sr-89 Sr-90 NMP-1 1st qtr/78 390!120 <5.0 <2.0 JAF 1st qtr/78 560 120 <5.0 <2.0 OSWP ist qtr/78 490 120 <5.0 <2.0 NMP-1 2nd qtr/78 314 160 <1.1 1.0!0.4 JAF 2nd qtr/78 560 140 <1.2 1.1 0.5 OSWP 2nd qtr/78 282 160 <1.1 1.0!0.4 NMP 3rd qtr/78 256 86 0.8!0.4 0.4 0.3 JAF 3rd qtr/78 377 87 0.6 0.5 0.6 0.3 OSWP 3rd qtr/78 288 85 <0.8 0.8 0.3 NMP-1 4th qtr/78 253!170 <0.9 1.1 0.3 JAF 4th qtr/78 405 170 0.7 0.6 0.6 0.3 OSWP 4th qtr/78 215!170 <0.9 0.9 0.3
---.--.-i-- - m
TABLF. 9 MONTHLY P.ATLR COMPOSIT!'S CAMMA ACTIVITY pCi/l ISOTCOE J ANU ARY FL3tUARY MARCH APRIL LMY JUNL JULY AUGUST SEPTLN3tR OCTOBER h0VEMD LI, DECLM3LR NINE MILE POINT UNIT I INLET Co-00 0.0118.0 20.0119.6 23.1116.6 17.2117.9 4.0116.1 < 3. 2 * < 0. 6 < 1.0 < 2.0 <2.0 < 2.0 < 3.0 fe-59 < 14. 0 <16.5 < 13. 3 <15.2 <12.2 <14.2 <0.7 < 3.0 < 3.0 <3.0 < 3.0 < 2.0 lb-54 0.02 9.9 <12.1 9.0til.7 0.01 9.6 0.01 9.7 < 3. 0 * <0.4 < 2.0 < l.0 < l.0 < l.0 < 1.0 Co-58 0.0! 5.7 < 3. 8 0.01 6.8 < 7.9 < 7.3 < 7.26 <0.4 < 2.0 < l.0 < 1. 0 < l.0 < 1.0
.Nb-95 < 5.6 < 7.3 < 6.1 < 6.1 < 6.6 < 6.2 <0.4 < 2.0 < l.0 < 1. 0 < l.0 < l.0 2r-95 <11.1 <!2.0 < 11. 3 < 10. 9 < 10. 5 <10.2 < 0. 7 < 2.0 < 2.0 <2.0 < 2.0 < 1.0 Cs-;37 < 6.8 4.51 5.5 2.61 6.6 < 7.5 < 7.8 < 7. 2 <0.5 < 2.0 < l.0 < 2. 0 < 1.0 < 1.0 Cs-134 < 6.3 < 6.6 < 6.4 < 5.6 < 5.9 < 5.5 <0.4 < 2. 0 < 2.0 <l.0 < l.0 < 2.0 Cr-51 < 39.7 <45.2 < 16. 3 <40.5 < 41.5 <40.9 < 3. 0 <10.0 <10.0 < 7. 0 < S.0 < 7.0 Cc-141 9.02 2.1 < 6.9 < 6.8 < 6.5 6.4 < 6.4 < 0. 6 < 2.0 < 2.0 <1.0 < l.0 < 1.0 BaLa-140 <20.0 <23.0 < 21. 2 <21.8 < 22.5 22.82 2.6 <0.7 < 2.0 < 2.0 <2.0 < 2.0 < 2.0 JAMES A. FITZPATRCK INLET Co-60 0.0218.2 22.0!!9.7 11.5218.1 17.0217.9 33.0218.7 < 3.2* <0.5 < 2.0 < 2.0 < 2. 0 < 2.0 < 1.0 Fe-59 < 9.9 < ! 3. 8 < 14. 4 <13.5 <13.3 < 14. 0 <0.7 < 3.0 < 2.0 <3.0 < 3.6 < 2.0 1 Mn-54 0.0t 9.9 0.0111.0 4.1111.4 7.81 9.7 0.6 S.7 < 3. 0* < 0. 4 < 1.0 < l.0 < l .0 < 1.0 < 1.0
[n' Co-58 0.01 5.7 3.91 7.7 0.01 6.2 13.31 2.6 < 7.2 < 7.8 <0.4 < 1.0 < 1.0 < 1. 0 < 1.0 < 1.0 i hb-95 < 6.7 < 6.5 < 6.1 < 6.5 < 6.2 < 5.9 <0.4 < 2.0 < 1.0 < 1. 0 < 1.0 < 1.0 2r-95 < 10. 5 <11.3 < 10. 6 < 9.8 <11.4 <11.5 <0.6 < 2.0 < 2.0 <2.0 < 2.0 < 1.0 Cs-137 < 7.1 < 8.2 < 7.0 < 6.5 < 7.4 < 7.3 < 0. 5 < 2.0 < 1.0 <2.0 < 2.0 < 2.0 Cs-134 < 5.3 < 6.1 < 6.1 < 5.9 < 6.1 < 6.1 < 0. 5 < 2.0 < 2.0 <!.0 < 1.0 < 1.0 Cr-151 < 43.9 <42.8 < 39.6 <43.3 < 42.9 < 45.3 <3.0 < 10. 0 < 8.0 < 9. 0 <10.0 <10.0 Ce.141 < 6.5 < 6.3 < 6.2 < 6.6 < 6.5 < 6.5 <0.6 < 2.0 < 2.0 <2.0 < 2.0 < !.0
.BaLa-140 < 21. 5 < 22.4 <!9.7 <22.8 < 20.1 < 22.4 <0.8 < 2.0 < 2.0 < 2. 0 < 2.0 < 2.0 RAW CITY WATER Co-60 8.Sil8.8 11.0!21.5 24.1218.5 0.0217.1 0.0!!7.5 < 3.2* < 0. 6 < 2.0 < 2.0 < 2.0 < 2. 0 < 2.0 Fe-59 <14.4 <19.9 < 16. 5 < 13. 3 <14.4 <13.3 <0.7 < 3.0 < 3.0 < 3. 0 < 3.0 < 2.0 Mn-54 0.0214.4 0.0112.3 0.0111.2 7.42 9.9 3.4!!0.1 < 3.0* < 0. 3 < 1.0 < l.0 < 2. 0 < 1.0 < l.0 Co-56 < 7.9 0.02 7.5 0.02 6.3 12.21 2.8 0.02 5.1 < 7.8 < 0. 3 < 1.0 < 1.0 < 1. 0 < l.0 < 1.0 Nb-95 < 5.9 < 8.3 < 6. 4 < 6.4 < 6.6 < 5.9 <0.3 < 2.0 < 1.0 <l.0 < 1.0 < 1.0 2r-95 < 10.1 < 12. 8 < 10. 5 < 10. 6 < 12. 5 <12.1 < 0.6 < 2.0 e 2.0 < 2. 0 < 2.0 < 2.0 Cs-137 < 7.5 < 9.8 < 7.4 < 7.4 < 7.1 < 6.9 < 0.4 < 2.0 < l.0 < 1. 0 < 7.0 < l.0 Cs-134 < 5.9 < 8.7 < 6.5 < 6.1 < 5.4 < 6.3 <0.3 < 2.0 < 2. 0 <1.0 < 2.0 < l.0 Cr-51 < 41. 2 < 51. 2 < 4 2. 5 < 4 5. 0 <43.9 < 38. 5 <3.0 <10.0 < 10. 0 < 9. 0 < 10. 0 < 7.0 Ce-141 < 6.2 < 8.6
< 6.4 < 6.5 < 6.5 < 6. 6 <0.4 < 2.0 < 2.0 < 2. 0 < 2.0 < 1.0 Bala-140 < 22. 4 < 26.1 < 22.6 < 22. 3 21.62 3.4 < 21. 4 <0.6 < 3.0 < 2.0 < 2. 0 < 2.0 < 2.0
- Re an a lyz ed . Results decay corrected.
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ae ce e6 e- a. N N e#b .-e oo. eg e e e e e e e e e e e N dL e C e e e e e e e e e e e -e e o o o o o 4 .. .a* e. N N N e e o'l U F- r* P- .* P- m3 en e co m m m m ** *'* ** ** *'s e.4 .4 *4 .-e .* 9 N. TABLE 15 ENVIRONMENTAL TLD READINGS Net Dose in mrem i 2a QUARTER TLD NO. LOCATION 1st 2nd 3rd 4th 3 D1 On Site Missing 27i 3 23! 3 21! 2 4 D2 On Site 14! 4 Missing 122 2 142 2 5 E On Site 131 3 14! 2 12! 2 Missing 6 F On Site 12! 3 12! 2 lot 1 12t 1 7 G On Site 9! 3 10 1 112 2 11! 1 8 C Off Site 12! 3 Missing 13! 2 14! 1 9 D1 Off Site 10! 3 Missing 12! 1 11! 1 10 D2 Off Site 10! 3 11 2 9 2 12! 1 11 E Off Site 102 3 11! 4 72 1 10! 1 12 F Off Site Missing 11! 3 10! 2 11! 1 13 G Off Site 8! 2 10! 1 102 2 10 1 14 SW Oswego 12! 3 12! 2 102 1 132 1 15 Pole 66, W. Bound 9! 2 112 3 92 1 102 2 16 Pole 51, W. Bound 14! 4 122 3 11! 2 121 1 17 Prog. Cen. E. Yard 132 3 13 2 12 2 131 2 18 Prog. Cen. Picnic 11! 3 13 2 lot 2 122 2 19 Pole 9, E. Bound 13! 3 12t 2 112 3 12! 1 20 JAF Shore, W. Bound 25212 Missing Missing Missing 21 Pole 67, E. Bound lot 3 12! 2 11! 3 13 2 22 Pole 53, E. Bound 92 4 111 1 10t 1 lit 1 23 11 On-Site 14 3 16t 2 15! 1 15! 1 24 I On-Site 102 3 132 2 11! 2 12t 1 25 J On-Site 10! 2 12 2 11! 2 13! 2 26 K On-Site lot 2 Missing 12! 2 12 2 27 Light Pole (N) JAF 146!31 157!30 56 5 51! 4 28 Light Pole (E) JAF Missing 37! 4 131!12 201!12 29 N. Fence (E) JAF 36! 7 52t 6 84! 6 96!15 30 N. Fence (MW) JAF 61!11 60! 7 32! 4 107213 31 N. Fence (MW) NMP 38! 7 50! 5 40! 7 371 2 32 N. Fence (W) NMP 26! 4 35! 4 25! 4 25! 2 33 NMP/JAF, Twin Pole (W) of JAF W. Fence 24 4 28! 3 - 24! 3 25 2 34 N of Unit 2 on Lake 16! 3 16! 2 14! 2 16: 2 35 E of Unit 2 on Stor. Bldg. Missing 14: 2 Missing 13 2 36 Pole Tower, FNM-13 13! 4 12t 2 9! 1 12! 1 37 Pole Tower, FNM-14 151 3 17! 2 14! 1 17! 1 38 SE End of Shop on Fence 19 3 221 2 17 2 18! 1 39 NMP-1 ME Gate 516t101 387!40 345!59 371119 40 NE Cate, NMP-1 52! 7 127210 62! 5 44t 1 41 Paint Shop NMP-2 24! 6 35! 4 28! 3 24! 2 42 Turb. Track Bay NMP-2 73!21 Missing 59 6 Missing
I TABLE 16 CONTINOUS RADIATION MONITORS * (GM) mr/hr 1st liALF mR/hr LOCATION PERIOD MIN. MAX. AVE. C Off-Site January 0.019 0.042 0.031 February 0.022 0.042 0.030 March 0.021 0.048 0.031 April 0.024 0.050 0.035 May 0.028 0.055 0.042 June 0.018 0.052 0.035 D 1 On-Site January 0.019 0.050 0.026 February 0.011 0.042 0.023 March 0.010 0.067 0.024 April 0.014 0.042 0.030 May 0.010 0.051 0.025 June 0.022 0.065 0.043 D, On-Site January 0.012 0.028 0.018 February 0.010 0.032 0.021 E March 0.018 0.055 0.028 g April 0.015 0.040 0.030 May 0.015 0.030 0.022 June 0.016 0.033 0.025 E On-Site January 0.012 0.023 0.016 February 0.013 0.027 0.018 E March 0.013 0.024 0.018 5 April 0.014 0.029 0.021 May 0.015 0.030 0.022 g June 0.012 0.010 0.020 E F On-Site January 0.012 0.031 0.020 February 0.010 0.024 0.018 March 0.010 0.020 0.014 April 0.010 0.022 0.014 May 0.010 0.028 0.014 June 0.010 0.025 0.018
- Detectors are ' bugged' to insure onscale readings.
I I I
TABLE 16 (Cont.) CONTINOUS RADIATION MONITORS * (GM) mr/hr 1st ilALF mR/hr LOCATION PERIOD MIN. MAX. AVE. G On-Site January 0.025 0.050 0.040 February 0.027 0.048 0.036 March 0.028 0.062 0.040 April 0.029 0.080 0.040 May 0.029 0.065 0.047 June 0.026 0.065 0.046 11 On-Site January 0.016 0.032 0.024 February 0.015 0.032 0.023 March 0.019 0.035 0.021 April 0.017 0.038 0.024 May 0.016 0.035 0.025 June 0.018 0.045 0.031 I On-Site January 0.010 0.018 0.013 February 0.010 0.040 0.015 March 0.010 0.025 0.014 Aprii 0.010 0.022 0.014 May 0.010 0.023 0.015 June 0.010 0.030 0.020 J On-Site January 0.010 0.021 0.013 Februa ry 0.010 0.015 0.013 March 0.010 0.030 0.017 April 0.010 0.028 0.018 May 0.012 0.030 0.021 June 0.012 0.030 0.018 K On-Site January 0.011 0.025 0.015 February 0.011 0.025 0.018 March 0.011 0.032 0.019 April 0.012 0.032 0.017 May 0.010 0.029 0.019 June 0.010 0.028 0.019
I TABLE 16 (Cont.) CONTINOUS RADIATION MONITORS * (GM) g mr/hr E 2nd liALF mR/hr LOCATION PERIOD MIN. MAX. AVE. C Off-Site July 0.018 0.035 0.025 August 0.018 0.032 0.025 September 0.016 0.040 0.028 October 0.015 0.030 0.025 November 0.015 0.025 0.020 December 0.012 0.030 0.020 D3 On-Site July 0.015 0.065 0.020 August 0.018 0.060 0.025 September 0.010 0.040 0.030 October 0.020 0.500 0.035 November 0.015 0.070 0.030 December 0.028 0.075 0.040 D, On-Site July 0.015 0.025 0.020 August 0.015 0.045 0.020 g September 0.010 0.050 0.030 g October 0.015 0.025 0.018 Novcmber 0.015 0.028 0.018 December 0.010 0.030 0.015 E On-Site July 0.015 0.030 0.020 August 0.015 0.028 0.020 Septenber 0.010 0.030 0.020 October 0.010 0.030 0.020 November 0.010 0.030 0.020 E December 0.015 0.040 0.020 g F On-Site July 0.010 0.028 0.018 August 0.010 0.025 0.015 September 0.010 0.030 0.015 October 0.010 0.030 0.015 November 0.012 0.025 0.015 December 0.010 0.050 0.015
- Detectors are ' bugged' to insure onseale readings.
I I
TABLE 16 (Cont.) CONTINOUS RADI ATION MONITORS * (GM) mr/hr 2nd IIALF mR/hr LOCATION PERIOD MIN. MAX. AVE. G On-Site July 0.025 0.075 0.045 August 0.030 0.070 0.045 September 0.030 0.050 0.040 October 0.025 0.050 0.040 November 0.028 0.200 0.040 December 0.010 0.050 0.020 11 On-Site July 0.020 0.050 0.030 August 0.015 0.040 0.030 September 0.010 0.035 0.025 October 0.015 0.035 0.025 November 0.018 0.035 0.025 December 0.018 0.045 0.030 I On-Site July 0.010 0.025 0.018 August 0.010 0.050 0.015 September 0.010 0.020 0.015 October 0.010 0.030 0.018 November 0.020 0.020 0.020 December 0.010 0.022 0.013 J On-Site July 0.015 0.035 0.020 August 0.015 0.030 0.020 September 0.010 0.040 0.020 October 0.010 0.045 0.030 November 0.015 0.025 0.020 December 0.012 0.023 0.017 K On-Site July 0.012 0.030 0.020 August 0.010 0.030 0.015 September 0.010 0.035 0.020 October 0.010 0.035 0.025 November 0.010 0.025 0.015 December 0.010 0.020 0.015
TA3LE 17 CCNCENTRATICNS OF ICDINE-131 Ih MILK F(sults in Units of pCl/l 2 2 sigm.a STATIO'i* 6-05-75 7-04-78 9-01-78 9-08-73 10-02-78 11-02-73 12-04-76 4 <C.1 <0.2 <0.1 <0.2 <0.2 <0.2 <3.2 13 <0.1 <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 14 <0.2 <0.2 (0.3 <0.2 <C.2 <0.2 <0.3 16 (0.2 <0.2 <0.1 <0.2 <0.2 <0.2 <0.2 25 <0.2 <0.2 <0.2 <0.3 0.1920.07 <0.2 <0.2
*5cc Env. Sample Suntary for Cross Reference to prior years sample locations.
bi
TABLE 18 CONCEIUMI'Cf.3 0F GATA El4!TTERS AND STRONTIlil-90 IN MILK Results in Onits of pCi/12 2 signa 5-05-78 7-04-78 8-01-78 9-00-78 10-02-78 11-C2-78 12-04-73 to to to to to to to STATION NUCLICES 6-19-73 7-17-78 8-14-78 9-18-78 10-16-78 11-11-78 12-18-78 4 K-40 800 r0* 1300t130 15002150 160C2160 1000t160 1230t123 1600t163 Cs-137 5.522.2 7.212.3 7.723.8 1224 6.813.2 3.7 2.1 6.023.0 S r-90 5.021.3 4.8tl.2 4.810.9 6.221.5 7.321.5 4.6t0.3 3.4t0.7 13 K-40 12002120 11001110 12002120 14001140 16002160 990 t93 1500t150 Cs-137 7.E12.3 6.322.1 7.8t3.1 6.823.7 5.512.8 2.411.9 4.2!3.2 S r-90 7.621.0 6.610.9 5.111.1 9.022.3 5.721.0 4.221.3 3.013.6 14 K-40 1100!110* 930293 1500!150 16001160 15002150 1400 t140 1400t140 Cs-137 3.922.0 5.312.1 7.8 t 3. 4 9.713.6 4.522.8 5.31?.3 3.412.8 S r-90 4.510.0 8.121.2 3.811.0 5.5t2.1 5.121.5 2.511.2 3.210.8 d, 16 K-40 9G0196 1200t120 1400 140 1900t190 1E00:160 13002130 1500160 to Cs-137 1022 1413 9.613.6 3016 6.9!3.7 3.5 2.0 7.212.8 S r-90 6.310.9 7.311.0 6.5tl.1 7.422.5 6.611.1 4.721.2 5.110.7 25 K-40 950295 1300t130 14002140 18302180 17002170 1300t130 1]00t190 Cs-137 1223 1713 1615 1014 11t4 9.2?2.9 3326 Sr-90 1021 8.121.0 5.521.4 7.821.4 8.121.3 8.512.1 5.?tl.1
I TABLE 19 Fl!LCll ANIS!AL CENSUS SPRING 1978 TOWN NO. ON MAP blILCll ANIMALS New llaven 1 33C 4 52C 5 22C 21 40C 35 17G Mexico 2 0 l 7 20C E 8 45C 9 g 12 19C E 14 60C 15 45C 20 IG l 22 35C " 23 36C 24 45C E 26 40C E
,27 1C 28 0 g 29 6C 30
- E 33 0 36 0 l 37 31C E Richland 18 55C Lycoming 25 16C llannibal 13 22C Oswego 3
- 6 **
l 10 4C E 11 26C 16 38C E 17 0 E 19 31 1C 32 20C 34 0 C = Cows G = Goats
= Would Not Cooperate
- = Numerous attempts were made to contact this person; all unsuccessful.
TABLE 19 (Cont.) b!ILCli ANib!AL CENSUS SU5!'!ER 1978 TOWN NO. ON StAP bilLCll ANIb1ALS New Haven 1 33C 4 52C 5 23C 21 30C 35 17G Flexico 2 0 7 24C 8 48C 9 ** 12 19C 14 60C 15 42C 20 IG 22 31C 23 37C 24 45C 26 34C 27 1C 28 0 29 3C 30
- 33 0 36 0 37 35C Richland 18 **
Lycoming 25 16C llannibal 13 26C Oswego 3
- 6 10 3C 11 29C 16 30C 17 0 19 31 1C 32 20C 34 0 C = Cows G = Goats
= Would Not Cooperate ** = Numerous attempts were made to contact this person; all unsuccessful.
TABLE 20 CO*4CENTRAT10t.S OF CMitA EMITTERS IN VARIOUS FOOD PRODUCTS Results in Units of pC1/g(wet) i 2 sigma SAMFLE SAMPLE CATE DESCRIPTION Be-7 K-40 Mn-54 Sb-125 Cs-137 Ra-226 N 5-10-78 Beef <0.04 1.510.2 <0.004 <0.01 0.04010.003 <0.01 F 5-14-78 Chicken <0.04 2.510.3 <0.004 <0.01 0.01450.007 <0.01 A 5-17-78 Beef <0.03 1.7t0.2 <0.004 <0.01 0.01410.006 <0.008 K 5-17-78 Chicken <0.03 1.9 0.2 <0.003 <0.008 <0.004 <0.009 K 5-17-78 Esgs <0.03 0.7210.12 <0.004 (0.009 <0.004 <0.01 0 5-18-78 Chicken <0.04 2.010.2 <0.004 <0.01 0.01310.008 <6.01 0 5-18-78 Eggs <0.04 1.410.2 <0.004 <0.01 <0.005 <0.01 L 5-24-78 Eggs <0.03 0.910.1 <0.003 <0.009 <0.004 <0.000 i 0 5-25-78 Goat (0.03 2.010.2 <0.003 0.0110.01 0.03310.005 <0.006 m Y D 8-21-78 Green Beans 0.0710.06 4.8 0.5 <0.006 <0.01 <0.003 <0.01 0 8-21-78 Zucchini Squash <0.04 1.110.2 <0.004 <0.01 (0.005 <0.01 G 8-21-78 Pears <0.04 0.810.1 0.01110.008 <0.01 <0.006 <0.C2 G 8-21-78 Tomatoes <0.04 1.710.2 <0.005 <0.01 <0.005 <0.01 C 8-24-78 Broccoli <0.03 2.3t0.2. < 0.004 <0.01 <0.005 <0.009 C 8-24-78 Cabbage <0.02 1.520.2 <0.003 <0.007 <0.003 <0.006 E 9-13-78 Cat bage <0.09 3.910.5 <0.01 <0.03 <0.01 <0.03 G 9-14-78 Pears <0.1 1.0t0.4 <0.01 <0.04 <0.01 <0.03 1 9-15-78 Tonatoes <0.09 2.810.4 <0.01 <0.03 0.0120.01 (0.03 F 11-15-78 Chicken <0.03 2.810.3 <0.004 <0.01 <0.005 0.01310.008 H 11-15-78 Park <0.03 2.310.2 <0.004 <0.01 0.02010.009 <0.009 J 11-15-78 Pork <0.03 1.610.2 <0.003 <0.009 0.01410.005 <0.003 K 11-15-78 Chicken <0.03 2.7i0.3 <0.003 <0.01 <0.004 <0.01 K 11-15-78 Eggs (0.03 1.310.1 <0.004 <0.01 (0.005 <0.009 M M M M M M M M M M M M M M M
1 3 0 5 1 0 1 2 0 0 0 0 2 1
- 0 0 2 0 a < < 0 <
R 0 4 5 1 0 0 0 0 0 4 7 0 3 0 0 0 0 1 t 1
- 1 6 6 0 s 0 0 1 <
C 0 0 0 0 0 9 5 1 0 1 1 2 0 0 0 0 1
- 0 0 0 0 b < < < <
S a T C
'L C
O R P 4 5 3 3 4 5 0 0 0 0 D a - 0 0 0 0 O m n O g M 0 0 0 0 F i s ( < < < S
) U 2
. C t I t n R o A )
c V t ( e 3 1 2 1 N w I ( 0 0 0 0 0 g 4 1 1 2 1 0 S / - 5 0 4 1 2 R i K E C 2 1 2 1 T p E T L I f M o T M E s A t i i J n 5 3 3 3
; U 7 0 0 0 0 G -
n e 0 0 0 0 F i B < < < ( O s S. f l t 0 u I s e U R F T h N . L O _ : I n T T e G P k s f s C I c g e g R i g e g C h E B E S C E D . E _ T . A 8 8 8 8 D 7 7 7 7 E 5 5 6 0 L 1 1 1 2 P - - - - M 1 1 1 1 A 1 1 1 1 _ S E L P 0 0 8 M M A S
. I
V. RESULTS STATISTICS AND HISTOGRAMS S
V. RESULTS STATISTICS AND IIIST0 GRAMS The 1977 environmental sample data is presented in Section V in table format with associated histograms. A. Special Considerations
- 1) Only measured values were used in histogram and statistical calculations.
- 2) Ifistograms and associated data were generated only for sample medium or sample locations with sufficient data points for adequate graphic depiction (i.e. >5 data points).
B. Format
- 1) Basic statistics - the following statistics are reported with each histogram:
a) Number of data points used in developing the histogram, b) Mean or " average" of all data points used for each histogram. c) Standard Deviation of the data used for each histogram. d) Variance of the data used for each histogram. c) Minimum and Maximum values. f) Range of the data for each histogram. g) Class width used in generating the histogram
- 2) The llIST0GRANS presented in this section are a graphic display of frequency distribtuion, with equal intervals of values marksd on a horizontal axis. The frequency of each interval is indicated by a rectangular bar plotted on a vertical axis.
CELL STATISTICS for each histogram are shown by class number, lower bound, upper bound, frequency of occurrence and relative frequency in percent.
***ENVIFON?' ENTAL 3AMPI,C FTATISTICAL DATA ***
TABLE 3 LAKE PERIPHYTON GAMMA ISOTOPIC pCi/g wet Be-7 INDICATOR STATION SA*4PLC STATISTICS NU!"BER OF SAMPLCS 5.00 MIN D'UP V ALUE 0.07 STANDARD DEV. 0.69 FANGC 1.73 t.CAN VALUE 0.62 FAXIMUM VALUE 1.80 VARIANCE 0.47 CLASS WIDTH 0.20
* *
- H I STOG PAM * *
- CLASS NO. LOWER B. UPPER B. FRCOUCNCY REL.FRCO.%
1 0.0 0.2 1.0 20 2 0.2 0.4 2.0 40 3 0.4 0.6 1.0 20 4 0.6 0.8 0.0 0 5 0.8 1.0 0.0 0 6 1.0 1.2 0.0 0
- 7 1.2 1.4 0.0 0 8 1.4 1.6 0.0 0 9 1.6 1.8 0.0 0 10 1.8 2.0 1.0 20
* *
- PLOT OF HI STOG P A'1* *
- 2.00 .
1.80 . l.50 .. 1.40 . l.20 . D
- a=
1.00 . LaJ E 0.80 . S a: 0.sa . Lt D.40 .
~
0.20 . r
$ $ & tsb tsb A A -
N
.. CLR55 M1DPD1NTE
* *
- C NVII'ONMCNTAL S AM PLC STATISTICAL DATA ***
TABLE 3 LAKC PCRIPHYTON GAMMA ISOTOPIC tCi/g wet K-40 INDICATOR STATION SAMPLC STATISTICS NUMBER OF SAMPLCS 5.00 MINIMUM VALUr 1.00 STANDARD DEV. 0.75 RANGC 1.70 MCAN VALUC 1.62 MAXIMUM VALUE 2.70 VARIANCC 0.56 CLASS WIDTH 0.30
***HISTOCRAM***
CLASS NO. LCUCR B. UPPER B. FREQUENCY REL.FRCO.% 1 2 0.0 0.3 0.3 0.0 0 g 0.6 0.0 0 3 3 0.6 0.9 0.0 0 4 0.9 1.2 2.0 40 5 1.2 1.5 1.0 20 6 1.5 1.8 0.0 0 7 1.8 2.1 0.0 0 8 2.1 2.4 1.0 20 9 2.4 2.7 0.0 0 10 2.7 3.0 1.0 20
*** PLOT OF HISTOCPAM***
2.00 .. 1.80 . l.50 . I.40 .. l.20 . D
==
I.00 . La_I I O.80 . e a 0.s0 . Lt 0.40 . 0.20 . 255 25$ N N N N N 3
. CLR55 MIDPOINT 5 g
***CublPON'1CNTAL SAN 1PLC STATISTICAL DATA ***
TABLE 3 LAKC P Cl!I P!!Y10N GAMMA ISOTOPIC cCi/g wet ub-95 IdDICATOF STATION SAMPLC STATISTICS i4UFBER OF SAMPLES 5.00 MINItUM VALUC 0.02 STANDAPD DEV. 0.03 PANGC 0.07 MCAli VALUC 0.04 M A X I MU'1 VALUC 0.09 VAPIANCE 0.00 CLASS WIDTII 0.01
***llISTOGRAM***
CLASS NO. LOWER t3. UPPCP B. FRCOUCNCY PCL.FPCO.S 1 0.0 0.0 0.0 0 2 0.0 0.0 1.0 20 3 0.0 0.0 1.0 20 4 0.0 0. 0 1.0 20 5 0.0 0.1 1.0 20 6 0.1 0.1 0.0 0 7 0.1 0.1 0.0 0 8 0.1 0.1 0.0 0 9 0.1 0.1 0.0 0 10 0.1 0.1 1.0 20
* *
- PLOT OF !!I STOG P AP * *
- I.00 .
0.90 .. 0.80 . 0.70 . 0.50 . D
=
0.E0 . w 0.40 .
-a 0.30 .
a= 6 0.20 . 0.10 . 25$ E5$ ts$ t:Ei tE5 ts$ tsi tsi t's$ Es$
.. CLR55 MiDPD1NTS
* *
- CWVI FONb Ci4TAL S A.1 PLC STATISTICAL CATA***
TABLC 7 LAKC FISH GAf"'A ISGTOPIC PCi/o wet K-40 CON'Ii'O L STATI ON SAFPLC STATISTICS uuMBCR OF SA'!PLCS 9.00 MININut? VALUC 1.90 STANDAPD DCV. 1.11 PANGC 3.80 MCAN VALUC 2.94 f1AXIrtUP VALUC 5.70 VARIANCC 1.23 CLASS GI DTf! 0.44 I
* *
- EII STOC FAM * *
- CLASS NO. LONCP B. UPPER B. FRCOUCNCY PCL.F9CO.S 1 1.6 2.0 1.0 11 2 2.0 2.5 3.0 33 3 2.5 2.9 1.0 11 4 2.9 3.4 3.0 33 g 5 3.4 3.8 0.0 0 g 6 3.8 4.2 0.0 0 7 4.2 4.7 0.0 0 8 4.7 5.1 0.0 0 9 5.1 5.6 0.0 0 10 5.6 6.0 1. 0 11
* *
- PLOT OF f!ISTGG RA*1* *
- 3.00 .
2.7B . 2.40 . 2.10 . l.80 . D:::= l.50 . W I l.20 -
& a.sa .
m L 0.50 . B.30 . Y Y Y Y Y E.E Y
. CLR55 MIDPOINT 5 g
* *
- ENVI ROdMEiiTAL S A'1PLC STATISTICAL DATA ***
TABLE 7 __ LAKE FISH GAMMA ISOTOPIC pCi/g wet K-40 INDICATOR STATION SAMPLE STATISTICS nut:BER OF SAMPLES 19.00 M IN I MU'1 VALUE 1.10 STANDARD DEV. 0.49 RANGC 1.80 MEAN VALUE 2.07 MAXIMUM VALUE 2.90 VAPIANCE 0.24 CLASS IJIDTH 0.20
* *
- H I STOG RA Al * *
- CLASS NO. LOWER B. UPPER B. FREGUENCY REL.FREQ.1 1 1.0 1.2 1.0 5 2 1.2 1.4 0.0 0 3 1.4 1.6 1.0 5 4 1.6 1.8 4.0 21 5 1.8 2.0 3.0 16 6 2.0 2.2 1.0 5 7 2.2 2.4 4.0 21 8 2.4 2.6 0.0 0 9 2.6 2.8 4.0 21 10 2.8 3.0 1.0 5
* *
- PLOT OF III STOG FA"* *
- 4.00 ..
3.50 . 3.25 . 2.BD . 2.40 D
==
2.00 . LA1 I.50 .
=a
, h a: I.25 . A 0.BD . B.40 . w
* ""~
M. 8'l N 9 - M. 8'l 6 9
- - - - - ~ ~ ~ ~ ~
.. CLR55 MiDPDiNTS
* *
- ENVI ROht' ENTAL STJ'PLC STATIGTICAL DATT***
TAPLC 7 LANC FISH GAWA ISOTOPIC pCi/g wet G r -9 0 CONTROL STATIO 1 g S A'4 PL C STATISTICS g NUMt3CR OF SAMPLCS 6.000 MINIriU!' VALUE 0.004 STANDARD DEV. 0.004 P At1GC 0.011 MCAN VALUC 0.010 MAXINUM VALUE 0.015 VAPIANCC 0.000 CLASS WICTH 0.002 I
* * * !II STOG FAM * *
- CLASS NO. lok.C R B. UPPER B. FREQUENCY PCL.FPCO.1 1 0.000 0.002 0.000 0 3 2 0.002 0.004 0.000 0 E 3 0.004 0.006 1.000 17 4 0.006 0.008 0.000 0 g 5
6 0.008 0.010 2.000 33 g 0.010 0.012 0.000 0 7 0.012 0.014 2.000 33 8 0.014 0.016 1.000 17 9 0.016 0.018 0.000 0 10 0.018 0.020 0.000 0
* *
- PLOT OF III STOC CA'4 * *
- 2.00 ..
l.80 . 1.50 . . 1.40 . 1.20 D I.00 l 2= w I 0.80 . E5 m.sa . a L.a U.40 . 0.20 ED M N = C2 B2 * !E2
.. iii! t3 2 2 m m m = m E a a a aa a a a a a E
. CLR55 MiDPD1NTS g
***C:9VI T U;.!'L:JTAL S AveLC STATISTICAI, i: A T A * *
- TABLC 7 LAKC F I Sli GA*"l1A I SOTOP IC pCi/g wet Sr-90 I:JDICATOF STATION SAMPLC STATISTICS aUMBCR OF SA 1PLCS 14.000 MINIP'Uf' VALUE 0.004 STANDAPD DEV. 0.006 PANGC 0.021
!1CAN VALUC 0.013 " A X I ", U! ~ VALUC 0.025 VAPIANCC 0.000 class WIDTH 0.003
***!!ISTOGFAM***
CLASS NO. LCMCP B. UPPCR B. FREQUCNCY PCL.FPCO.% 1 0 . L 10 0.003 0.000 0 2 0.003 0.006 2.000 14 3 0.006 0.009 1.000 7 4 0.009 0.012 2.000 14 5 0.012 0.015 4.000 29 6 0.015 0.018 2.000 14 7 0.018 0.021 1.000 7 8 0.021 0.024 1.000 7 9 0.024 0.027 1.000 7 10 0.027 0.020 0.000 0
* *
- PLOT OF fiISTOGFA:1* *
- 4.00 .
3.50 . 3.20 . 2.80 . 2.40 . D:2= 2.00 . La l !.50 . I a= 1.20 . La_. 0.80 . D.40 . bbbUbbb a a a a a a a a a a
.. CLR55 MiDPD1NTS
* *
- C t.V I RO Ni'Ci1TA L 3 A:/ PLC STATISTICAL DAT^***
TABLE 7 LANC F IS!! GA' / ISOTOPIC r;Ci/9 we t C_-137 CC:47 EOL ST ATIOt4 SAMPLC STATISTICS hU"BCR OF SAftPLES 8.00 t'IN I t'UM VALUC 0.04 STAi4DARD DEV. 0.05 CANGl: 0.16 MCAN VALUE 0.09 MAXIMUM VALUE 0.20 VARIANCE 0.00 CLASS MIDTH 0.02
***HISTOGRAT1***
I CLASS NO. LOhCP B. UPPCR B. FRCOUCNCY RCL.FRCC.% 1 0.0 0. 0 0.0 0 2 0.0 0. 0 2.0 25 3 0.0 0.1 2.0 25 4 0.1 0.1 1.0 13 5 0.1 0.1 2.0 25 6 0.1 0.1 0.0 0 7 0.1 0.2 0.0 0 8 0.2 0.2 0.0 0 9 0.2 0.2 1.0 13 10 0.2 0.2 0.0 0
*** PLOT OF HISTCGRA'1***
2.00 . 1.80 . 1.00 . 1.40 . 1.20 .. D
==
1.00 . Lu D.80 . a S m 0.s0 . L4 2.40 . 0.20 .
& & & & & & & & & & E
. .. CLF155 M1DPDiNTE
***ENVIRONFCGTAT SAMPLC STATISTICAL DATA ***
TABLE 7 LAku FISH GAMMA ISOTOPIC pCi/g wet Cs-137 INDICATOR STATION SAMPLC STATISTICS NUMBER OF SAMPLCS 17.00 MINIMUM VALUE 0.03 STANDARD DEV. 0.02 RANGC 0.07 MCAN VALUC 0.08 MAXIMUM VALUE 0.10 VARIANCE 0.00 CLASS WIDTH 0.01
* *
- III STOG PAM * *
- CLASS NO. LOWER B. UPPER B. FREQUENCY RCL.FREQ.%
1 0.0 0.0 0.0 0 2 0.0 0.0 0.0 0 3 0.0 0. 0 1.0 6 4 0.0 0.1 3.0 18 5 0.1 0.1 0.0 0 6 0.1 0.1 4.0 24 7 0.1 0.1 5.0 29 8 0.1 0.1 4.0 24 9 0.1 0.1 0.0 0 10 0.1 0.1 0.0 0
*** PLOT OF HISTOGRAM ***
E.00 . 4.50 . H.00 . 3.50 .. 3.00 . D
==
2.E0 W 2.00 . 1.E0 . a= 1a l.00 . 0.E0 .
. iEi Gd 9 a a a a a a a a a a W W G E ES = 5
.. CLR55 MiDPDINTS
* * *EUVIPONMENTAL S AMPLE STATI STICAL DATA ***
T AB LE 8A LAKE WATER FONTILY COMPOSITE GROSS BETA pCi/l BETA CONTPOL STATICN SAMPLE STATISTICS NUMB ER OF S AMPLES 11.000 MINIFUF VALUE 0,500 STANDAFD D EV . 1.581 RANGE 5.600 MEAN VALUE 3.545 MA XI FU M V ALUE 6.100 VARI AN CE 2.499 CLASS WIDTH 0.580 I
*** HISTOGRAM ***
CL ASS NO . LCKER B. UPPER B. FREQUENCY REL.FRE0.% 1 0.400 0.980 1.0 9 E 2 0. 98 0 1.560 0.0 0 5 3 1.560 2.140 0.0 0 4 2.140 2.720 1.0 9 5 2.720 3.300 4.0 36 6 3.300 3.880 1. 0 9 7 3.880 4.460 1.0 9 8 4.460 5.040 1.0 9 9 5.040 5.620 0.0 0 10 5.620 6.200 2.0 18
* *
- PLOT OF HI STCGRAM * *
- I 4.00 .
3.50 3.20 . 2.80 - 2.40 - C
==
2.00 - W I l . fia . O I.20 g . cr La__ 0.80 0.40 . s m omr,J a = = = m m m - -_ H H s s U i -i
.. CLR55 MlDPD1NTE
* * *ENVIPON!: ENTAL SAMPLE STATI STICAL DATA ***
TABLE 8A LAKE WATER FONTELY COPPOSITE GROSS BETA pCif/1 BETA INDICATOR STATICN SAMPLE STATISTICS NUMB ER OF SAMPLES 22.000 MINIFUP VALUE 0.600 STAND AED D EV . 2.622 RANGE 10.500 MEAN VALUE 4.527 MAXIFUM VALUE 11.100 VARIANCE 6.874 CLASS WIDTH 1.070
* * *HI STOGR A M * *
- CL ASS NO. LOWER B . UPPER B. FPEQUENCY R E L. F FEO . t 1 0.500 1.570 2.0 9 2 1.570 2.640 1.0 5 3 2.640 3.710 10.0 45 4 3.710 4.780 1.0 5 5 4. 780 5.850 1.0 5 6 5.850 6.920 1.0 5 7 6.920 7.990 4.0 18 8 7. 990 9.060 1.0 5 9 9.060 10.130 0.0 0 10 10.130 11.200 1. 0 5
* *
- P LOT OF HI STOGRAM * *
- ___ 10.00 -
9.00 . __ B.00 . 7.00 . 5.00 . t: s.aa .
==
LLJ 4.CB . [ a: 3.00 . L.t 2.00 . 1.00 . n; r,-i s U ui W cd cri E" CLR55 MIDPOINT 5
* * *ENVIRONFENTAL S AMPLE STATI STI CAL DATA ***
I TABLE 8B LAKE UATER C U ARTEFLY COFPOSITE STRONTIU M PCi/l S r- 9 0 INDICATOR STATICN 3 SAMPLE STATISTICS l NUMB ER OF SAF.PLES 6.000 MINIEUF VALUE 0.400 ST AND ARD D EV . 0.303 RANGE 0.700 MEAN VALUE 0.800 MAXIbUM VALUE 1.100 VAFIANCE 0.092 CLASS WIDTH 0. 110 I
* *
- H I STOG RA M * *
- CL ASS NO. LOKER B . UPPER B. F FEQ UENCY RE L .F EEQ .1 I 1
2 0.200 0.310 0.310 0.0 0 17 5 0.420 1.0 5 3 0.420 0.530 0.0 0 4 0.530 0.640 2.0 33 g 5 0.640 0.750 0.0 6 0.750 0.860 0.0 0 0 5 7 0.860 0.970 0.0 0 8 0.970 1.080 1. 0 17 9 1.080 1. 190 2.0 33 10 1.190 1.300 0.0 0
* *
- P LOT O F HI STOGP AP *
- I 2.00 .
1.80 - 1.50 . l.40 . 1.20 - U i.00 I 2= w 0.e0 - ca 0.s0 w rv
- i. 0.40 .
0.20 . m m wm n as ma= == m l
~
m & & & & a & =
. CLR55 MIDPOINTE
* * *ENVIRONFENTAL SAMPLE STATI STICAL DATA ***
TAB LE 8B LAKE WATER QUAETEELY COMPCSITE TRITIUP. FCi/l 11 - 3 CONTPOL STATICN SAMPLE STATISTICS NUMB ER OF SAMPLES 4.000 MINIPUM VALUE 215.000 ST AND ARD D EV . 127. 510 RANCE 275.000 ME AN VALUE 303.750 MAXI MJ M V ALUE 490.000 VARI AN CE $$$$$$$$ CL ASS WICT!! 29.500
***HISTCGRAM***
CLASS NO. LOKE R B . UPPER B. F EEQ UEN CY RE L.F FEQ . % 1 205.000 234.500 2.0 50 2 234.500 264.000 0.0 0 3 264.000 293.500 1.0 25 4 293.500 323.000 0.0 0 5 323.000 352.500 0.0 0 6 352.500 382.000 0.0 0 7 382.000 411.500 0.0 0 8 411.500 441.000 0.0 0 9 441.000 470.500 0.0 0 10 470.500 500.000 1.0 25
* *
- P LOT O F HI STCGRA M* *
- 2.00 .
l.80 . 1.50 . 1.40 . 1.20 - U
==
l.00 . LJ 0.80 . ct u) c2: 0.s0 . L 0.40 . 0.20 .
- m. m. m. "'. m "! m. m m. "'
EO m
"r-
~
lE'
~
!E m
Pi m [B m m m W' M"3 ;,3 8-
. CLR55 MIDPOINTE
* * *ENVIFONMENTAL SAMPLE ST ATI STI CAL DATA ***
I TAB LE 8B LAKE WATER QUARTEFLY COMPOSITE TRITIUM FCil/l !!- 3 INDICATOR STATICN g SAMPLE STATISTICS g NUFB ER OF S AMPLES 8.000 MIllIt UM V ALUE 253.000 STAND ARD D EV . 119.936 RANCE 307.000 MEAtJ VALUE 389.375 MAXIMUM VALUE 560.000 VARI AN CE S$$$$$$$ CL7SS WIDTli .31.700 I
* * *lII STOG RA M * *
- CLASS tlO. LOhE R B . UPPER B. F F EQ U ENCY REL.FREQ.%
1 248.000 279.700 2.0 25 2 279.700 311.400 0.0 0 3 311.400 343.100 1.0 13 4 343.100 374.800 0.0 0 g 5 374.800 406.500 3.0 38 5 6 406.500 438.200 0.0 0 7 438.200 469.900 0.0 0 8 469.900 501.600 0.0 0 9 501.600 533.300 0.0 0 10 533.300 565.000 2.0 25
* *
- P LOT O F !!I STOGR A M * *
- I 3.0a .
2.70 . 2.40 . 2.10 . l.80 . O i.sa l 2= L4_1 I l.20 . e e.se . EE a.sa . I a.aa . g m m. m = " . 7 . m. M M & B = N 5 M ~__ m. a
@ m Pi 9 _
m m F1 m x u m g CLR55 MIDP0lNTS I
* **ENVIRONFENTAL S AFPLE ST ATISTI CAL DATA ***
TABLE 9 LAKE UATER FONT 11Y COMPOSITE GAMFA ISOTOPIC [Ci/1 Co-6 0 INDICATOP STATICN SAMPLE STATISTICS SU FB ER OF S AF.PL E S 8.000 MINIlUM VALUE 4.000 ST AND ARD D EV . 9.081 RANGE 29.000 MEAN VALUE 19.100 MAXI MJF VALUE 33.000 VARI AN CE 82.460 CL ASS WID'IH 3.300
* * *H I STCGFA M * * * ~
CL ASS NO. LGKE R B . UPPER B. FFEQUENCY R E L . F R EQ . % 1 2.000 5.300 1.0 13 2 5.300 8.600 0.0 0 3 8.600 11.900 1.0 13 4 11.900 15.200 0.0 0 5 15.200 18.500 2.0 25 6 18.500 21.800 1.0 13 7 21.800 25.100 1.0 13 8 25.100 28.400 1.0 13 9 28.400 31.700 0.0 0 10 31.700 35.000 1. 0 13
* *
- P LOT OF fil STCGR AF.* *
- 2.00 .
1.80 - 1.50 . 1.40 . 1.20 . D I.00 . 0.80 . 0 a= 0.s0 . L4 B.40 . 0.20 .
. r m O "3 m . M ".
r,-i r-- O bE ES R rH3 R R
. CLR55 MIDP0lNTE
* *
- C ,4VI IiON'1 CNTAL S AM PLC STATISTICAL DATA ***
TABLC 10 E AIRLtOPNC PARTICULATE E GCOSS BETA nCi/ cubic roter BETA CONTROL STATION SA!PLC STATISTICS NU*iBER OF SA'dPLCS 315.000 "INI"Uf' VALUC 0.010 g STA:iDARD DEV. 0.134 RANGC 0.650 E l1CAN VALUE 0.144 MAXIMUf1 VALUE 0.660 VARIA!JCC 0.018 CLASS WIDTH 0.070
*** HISTOGRAM ***
CLASS NO. LOWER B. UPPER B. FRCOUCliCY REL.FRCC.% g 1 0.000 0.070 93.0 30 3 2 0.070 0.140 98.0 31 3 0.140 0.210 47.0 15 4 0.210 0.280 39.0 12 5 0.280 0.350 22.0 7 6 0.350 0.420 4.0 1 7 0.420 0.490 8.0 3 8 0.490 0.560 2.0 1 9 0. 560 0.630 1.0 0 10 0.630 0.700 1.0 0
*** PLOT OF HISTOGRAM ***
98.00 . 88.20 78.40 59.50 . K8.80 - 49.00 . O] I 39.20 a: L 29.40 . 19.50 . I 9.90 .
& & & & & & & & & & E
. CLR55 MiDPDiNTS g
***C:iVIROINCNTAL SAVPLC STATISTICAL DATA ***
TABLE 11 AIRBORNC PARTICULATC GROSS tlCTA OCi/ cubic meter BCTA INDICATOR STATIO1 SAf'PLC STATISTICS NUMBCP OF SAMPLCS 651.000 t'INIMUM VALUE 0.006 STANDARD DEV. 0.054 R A r4G C 0.334 MCAiJ VALUC 0.102 MAXI.v0M VALUC 0.340 VARIANCC 0.003 CLASS WIDTH 0.035
***HISTCGPAM***
CLASS NO. LOMCP B. UPPCR B. FRCOUCNCY DCL.FRCO.S 1 0.000 0.035 99.0 21 2 0.035 0.070 85.0 18 3 0.070 0.105 100.0 21 4 0.105 0.140 64.0 14 5 0.140 0.175 49.0 11 6 0.175 0.210 21.0 5 7 0.210 0.245 26.0 6 8 0.245 0.280 15.0 3 9 0.280 0.315 6.0 1 10 0.315 0.350 1.0 0
* *
- PLOT OF rrI s70cpAp* *
- 100.00. .
90.00 . 80.00 . 70.00 .. 50.00 . D z E0.0D w 40.00 .
-a Q 30.00 g .
a= w 20.00 . 10.00 .
. l .
. W W E $ E E A R R A a a a a a a a a & a
.. CLF155 MIDPD1NTE
_ss_
* *
- E:iVI POGYENTAL SAMPLE S'I AT I S'I I CA L DATA ***
I TAELE 12 A I T:i!O F N E PAPTICULATE GAltfe A I SUTUPIC 10-3 PCi/ cubic reter '.' n- 5 4 COWTT,OL STATION g SA"PLC STATIS'/ICS g .4 UMBER OF SAMPLES 7.000 !!IN I5'UM V ALUE 0.059 STAT'DAPD DEV. 1.065 P A t!G C 2.591 MCAu VALUE 0.988 M A X I M U5' VALUE 2.640 VARIANCE 1.133 CLASS WIDTH 0.270 I
* *
- H I STOG PN1 * *
- CLASS t10. LOWER B. UPPED B. PPEQUENCY REL.FRCO.) I 1 0.000 0.270 3.0 43 E 2 0.270 0.540 1.0 14 5 3 0.540 0.810 0.0 0 4 0.810 1.000 0.0 0 g 5 1.080 1.350 0.0 0 g 6 1.350 1.620 1.0 14 7 1.620 1.890 0.0 0 8 1.890 2.160 1.0 14 9 2.160 2.430 0.0 0 10 2.430 2.700 1.0 14
* *
- PLOT OF H I STOG PA" * *
- I 3.00 .
I 2.70 2.40 .. 2.la .. l.80 I.ED - CJ E 1.20 . Q 0.90 . E a: E La 0.50 . 0.30 . N? m - -
. N.
N. Y.
._. _ ~
. M
~
D.
~ I
. CLR55 M1DPD1NTS g
* **EhVIRONFENTAL SAMPLE STATISTICAL DATA ***
TABLE 12 MONTHLY P ARTICULATE COMPOSITE GAMPA ISOTOPIC 10-3 FCi/ cub.ic me ter Mn-54 INDICA 10F STATION SAFPLE STATISTICS NUMB ER OF SAMPLES 10.000 MINIEUM VALUE 0.210 ST AND ARD D EV . 0.697 RANCE 2.240 FIAN VALUE 0.675 MAXIFUM VALUE 2.450 VAFIANCE 0.486 CLISS WIDTH 0.230
***HISTOCRAM***
CL ASS NO. LOKE R B . UPPER B. F FEQUENCY REL.FPEQ.t 1 0.200 0.430 6.0 60 2 0.430 0.660 2.0 20 3 0.660 0.890 0.0 0 4 0.890 1.120 0.0 0 5 1.120 1.350 1.0 10 6 1.350 1.580 0.0 0 7 1.580 1.810 0.0 0 8 1.810 2.040 0.0 0 9 2.040 2.270 0.0 0 10 2.270 2.500 1. 0 10
* *
- P LOT O F HI STOG RA M * *
- 5.00 .
E.40 . 4.80 . 4.20 . 3.50 . D
==
3.00 . q 2.40 O a: 1.80 . L I.20 - 0.50 .
. Pi d W EE K 9 R 9 9 R
- n m
. CLR55 MIDP0lNTE
* *
- CWVI CUtJf1Li;TAL S A:1PLC STATISTIC.TL DATA ***
TABLE 12 AIPBOPNC PARTICULATE GAMMA ISOTOPIC 10-3 rCi/ cubic teter Co-60 CO;4TPOL STATIO:J S A i1 P L C STATISTICS NU.'!BCR OF SA:1PLCS 9.000 f11 nit'UM VALUC 0.030 STA.4DARD DEV. 2.148 I?A N G C 5.570 l MCAN VALUE 1.733 " A XI'auM VALUC 5.600 5 VARIANCE 4.613 CLASS UIOTH 0.563 I
* * * !! I STOG R A'1 * *
- CLASS NO. LOWER B. UPPER B. FPCOUCNCY FCL.FPCC.%
1 0.000 0.563 4.0 44 g 2 0.563 1.126 0.0 0 5 3 1.126 1.689 2.0 22 4 1.689 2.252 1.0 11 5 2.252 2.815 0.0 0 6 2.815 3.378 0.0 0 7 3.378 3.941 0.0 0 3 3.941 4.504- 0.0 0 9 4.504 5.067 1.0 11 10 5.067 5.630 1.0 11
* *
- PLOT OF 'II STOC PAM * *
- I s.ee .
'I 3.50 g
3.20 2.80 _. 2.40 U:2= 2.se E 5 LAl l.60 Q l.20 . E a: E w D.80 . 0.40 . re ed : -: ni i,i -i =7 e u E
. CLR55 MiDPD1NTS g
* **ENVIPONFEN'I AL SAMPLE STATI STICAL DATA ***
TABLE 12 MONTIILY P AFTI CULATE COMPCSITE GAMFA I SOTOPIC 10-3 pC i/ cub. ic r:e te r Co.-6 0 I!;DICATOF STATION SAMPLZ STATISTICS NUFB EF OF SAFPLES 11.000 MINIbUF VALUE 0.320 STANDAPD DEV. 4.3 78 RANGE 14.980 ME AN VALUE 2.255 MA XI FU M V ALUE 15.300 VAF I AN CE 19.163 CLISS WID'IH 1.520
* * *H I STOGR A M * *
- CL ASS NO. LChE P B . UPPER B. F PEOUENCY RE L. F FEO . %
1 0.300 1.820 8.0 73 2 1.820 3.340 2.0 18 3 3.340 4.860 0.0 0 4 4.860 6.380 0.0 0 5 6.380 7.900 0.0 0 6 7.900 9.420 0.0 0 7 9.420 10.940 0.0 0 8 10.940 12.460 0.0 0 9 12.460 13.980 0.0 0 10 13.980 15.500 1.0 9
* *
- P LOT OF liI STCG RAl!* *
- 8.00 .
7.20 . s.4a . E.50 . 4.80 . D
=e=
4.ea . 3.20 . S a= 2.40 . L I.50 . B.sa - m m m g m m R N E
~ m m m
. . a _.: M &
- ~ =- w n m - - - -
. CLR55 MIDPOINTE
* *
- ENVII'ONMENTAL SA!1PLC STATI'3T ICA L DATA ***
TABLE 12 AIRBORNC PARTICULATC GAVMA ISOTOPIC 10-3 pCi/ cubic rctet Nb-95 CONTROL STATIO!J SAliPLC STATISTICS NUbfBCR OF SAMPLES 6.000 FiI N I M U 5" VALUC 1.320 STANDAFD DLV. 0.814 RANGC 2.490 f!CAIJ VALUC 2.393 P' A XI t'UN VALUC 3.810 VA R I AiJCC 0.663 class WIDT!I 0.253 I
* * *1f I CTOG R AM * *
- CLASS tJO . LCKCR C. UPPCR 3. FRCOUCUCY REL.FRCO.%
1 2 1.300 1.553 1.553 1.0 17 g 1.806 0.0 0 5 3 1.806 2.059 1.0 17 4 2.059 2.312 1.0 17 5 2.312 2.565 2.0 33 6 2.565 2.318 0.0 0 7 2.818 3.071 0.0 0 8 3.071 3.324 0.0 0 9 3.324 3.577 0.0 0 10 3.577 3.830 1.0 17
* *
- PLOT OF IIISTOG RAM * *
- 2.00 .
I 1.80 . 1.50 . 1.40 . 1.20 - D
==
1.00 . W 0.80 . E5 a.se . a L.s 2.40 . B.20 .
. mmm_m
._: W W W a sm,m W M M M E
. CLR55 MIDPDINTS g
* *
- ENVIRONMENTAL SAMPLE STATI STI CAL DATA ***
TABLE 12 MONTHLY P ARTICULATE COMPCSITE GAMMA I SOTOPIC 10- 3 IC i/c ub.ic me te r N b- 9 5 II;DICATOP STATION SAMPLE STATISTICS NUfG ER OF sat:PLES 7.000 MINIlmte VALUE 0.240 STAT;D APD DEV. 0.529 RANGE 1.320 MEA?J VALUE 0.866 MAXIFUM VAL UE 1.560 VARI AN CE 0. 28 0 CL ASS WIDTil 0. 14 0
* * *III STOGR AM * *
- CL ASS NO. LOWE R B . UPPER B. FFEOUENCY REL.FFEQ.%
1 0.200 0.340 1.0 14 2 0.340 0.460 1.0 14 3 0.480 0.620 1.0 14 4 0.620 0.760 1.0 14 5 0.760 0.900 0.0 0 6 0.900 1.040 0.0 0 7 1.040 1.180 1.0 14 8 1.180 1.320 0.0 0 9 1.320 1.460 0.0 0 10 1.460 1.600 2. 0 29
* *
- PLOT OF HI STCGRAM * *
- 2.es .
1.80 . l.BB . 1.40 . I.20 . U 2= 1.00 . LtJ O.80 . e a= e.se . I - O.40 . a.as .
. N EF M 5 9 "n c Z N R Q a . CLR55 MIDP0lNTE
***CNVIFONM'NTAL SAMPLi' GTATISTICA[. DATA ***
TABLE 12 AIPdOFNC PARTICULATC G A PS' A ISOTOPIC 10-3 rCi/ cubic reter Zr-95 CONTFOL STATION SAPPLC STATISTICS (JU.'?B ER OF SAM PLCS 6.000 NI ll t'Ut' VALUC 0.466 STANDARD DCV. 0.4 54 RANOC 1.134 l M C A!i VALUC 1.053 M A X I t'UM VALUC .l.650 5 VARIANCE 0.206 CLASS WIDTil 0.12d I
***llISTOGRAM***
CLASS NO. LOWER B. U PPER II. FPCCUCNCY PCL.FRCO.S. l 2 0.460 0.580 1.0 17 g 0.580 0.700 0.0 0 5 3 0.700 0.820 1.0 17 4 0.820 0.940 0.0 0 5 0.940 1.060 2.0 33 6 1.060 1.180 0.0 0 7 1.180 1.200 0.0 0 8 1.300 1.420 0.0 0 l 9 1.420 1.540 1.0 17 5 10 1.540 1.660 1.0 17
* *
- PLOT OF 51I STOG PAM * *
- I 2.00 .
l.80 . 1.50 . 1.40 . 1.20 . Q C3 l.00 0.80 . _i e cx 0.s0 . Ls 0.40 .
~
msmse~mmem e w w w ._: _- __- ._: ._: __: E
.. CLR55 M1DPDINT5 g
* *
- ENVIRONMENTAL S AMP LC STATI STI CAL DATA ***
T AB LE 12 _ MONTl!LY P ARTICULATE COMPOSITE CAMt% I SO TOP I C 10- 3 FCi/ cubic noter Zr-95 INDICATOF STATION SAMPLE STATISTICS NUMBER OF SAMPLES 6.000 MINIFUM VALUE 0.430 ST AND APD D EV . 0.494 RANGE 1.130 MEAN VALUE 0.970 MAXItUM VALUE 1.560 VARIANCE 0.244 CLASS WIDTH 0.J20
* *
- H I STOG RA M * * *
, CL ASS NO. LOhER B. UPPER B. FFEQUEN JY RE L .F EEQ .1 1 0.400 0.520 1.0 17 2 0.520 0.640 1.0 17 3 0.640 0.760 1.0 17 4 0.760 , 0.880 0.0 0 5 0.880 1.000 0. 0 0 6 1.000 1.120 1.0 17 7 1.120 1.240 0.0 0 8 1.240 1.360 0.0 0 9 1.360 1.480 0.0 0 10 1.480 1.600 2.0 33
* *
- P LOT O F HI STOGRA M * *
- 2.00 .
l.80 . 1.50 . 1.40 . l.20 . U i.00 .
==.J LL B.80 .
E5 0.s0 . ac
? L.L 0.40 .
0.20 .
. M2 @ r- Gd E he EE IM 9 5
. CLR55 MIDPD1NTE
* * *E!!VIf 0!it'E!!'I AL SAPPLE STATISTI CAL DA 'I A * *
- I TABLE 12 l POtlTilLY P AFTICUIATE CCPPCSITE =
GAM PA ISOTOPIC 10-3 g;i / cub ic rre te r Cc- 13 7 CONTPJL STATICt. g SAMPLE STATISTICS g tiUFbER OF SAFPLES 12.000 MItJIFU F. VAL UE 0.752 ST At;E / FD DEV. 1.071 RAtJ CE 3.44E MEAN VALUE 1.833 MA XI FU b VALUE 4.200 VAFIANCE 1.148 CL A S S WI D'lli 0. 4 ;0 I
* * *III STCGR AM * *
- CL ASS 110. LOhEP B. UPPE11 B . FFEQULNCY RE L.FFLO . i 1 0.500 0.920 2.0 17 E 2 0.920 1.340 4.0 33 5 3 1.340 1.760 1.0 8 4 1.760 2.180 1.0 8 g 5 2.180 2.600 2.0 17 g 6 2.600 3.020 0.0 0 7 3.020 3.440 0.0 0 8 3.440 3.860 1.0 8 9 3.860 4.280 1. 0 8 10 4. 280 4.700 0.0 0
* *
- P LOT OF !*I STOGRA F * *
- I 4.00 3.50 3.20 ,
2.80 2.40 . t 2.00 2= w I.50 . l E5 i.20 . ca:: L 0.80 0.40 I
= w wm -
mw a w W - - - N N H H m 9 l CLR55 MIDP0lNTS I
* * *CMVIFONNENTAL S AMPLE STATI STI CAL CATA***
TABLE 12 MONTilLY P AE'IICULATE COMPCSITE GAMPA ISOTOPIC 10- 3 W i /c ub ic me te r C c- 13 7 INDICATOP STATION SAMPLE STATISTICS NrlPEER OF SAPPLES 12.000 MIN T FUM VALUE 0.300 STAND APD DEV. 1.036 RANCE 3.010 MEAN VALUE 1.598 MAXIFUM VALUE 3.310 VARIANCE 1.074 CLTSS WIDT!! 0.320
* * *llI ST OG RA M * *
- CL ASS NO. LOhER B. UPPER B. FFEQUENCY REL.FREO.E 1 0.200 0.520 34 0 25 2 0.520 0.840 0.0 0 3 0.840 1.160 2.0 17 4 1. 16 0 1.480 1.0 8 5 1.480 1.800 1.0 8 6 1.000 2.120 0.0 0 7 1.120 2.440 1.0 8 8 2.440 2.760 3.0 25 9 2.760 3.080 0.0 0 10 3.080 3.400 1. 0 8
* *
- P LOT OF III STOGRA M * *
- 3.00 .
2.70 . 2.40 . 2.10 . l.80 . U
==
l.50 La J I l.20 . a= 0.90 . k U.60 . 0.30 .
. R 8 E3 Pi 5 Efl Pd S Di FG
& a -: : --
_: rd n cd M CLR55 MIDP0lNT5
* *
- Ei.v I cot EiiTAL CA:'PLC STATISTICAL DATA ***
'i A E' L C 12 g
'10ST!!L'l FAFTICULliTC CO.?POSITC 3 G A.01 A ISOTOPIC 10-3 cCi/ cubic meter C c-14 4 CO.4 IL L ST AT I O2. S AAPL C STA'"I STICS
- .0 4fiC R O F SANPLCS 6.000 t'I N I .'109 VALUC 3.200 STAfiCAPD DEV. 7.950 R AtJGC 20.800 g
- iC A ti VALUC 8.731 M AXIt'UV VALUC 24.000 g VAitI AiiCC 63.210 CL ASS t'I DT!! 2.120
* *
- l I S'I OG R AM * *
- I CLASS !iO. LOFCP D. UPPCP 8. FPCOUCNCY PCL.PRCO.;
1 3.000 5.120 2.0 33 2 5.120 7.240 2.0 33 3 7.240 9.360 0.0 0 4 9.360 11.480 1.0 17 5 11.480 13.600 0.0 0 6 13.600 15.720 0.0 0 7 15.720 17.840 0.0 0 8 17.840 19.950 0.0 0 g 9 19.900 22.080 0.0 0 5 10 22.080 24.200 1.0 17
***PLCT OF HISTCGPAM***
2.00 . g 1.80 . 1.50 i.s0 l v 1.20 I.00 l 2: W 0.80 . w C a: 0.50 . 6 0.40 . B.20
, _ _ mmmmmaz I
Y $ did&
^
& l' Ri Fd l
. CLR55 MIDP INTS I
* *
- C o v li;Otel;C,4'1 AL G AI .F LC STATISTICAL DATA ***
TABLE 12 .iO.iT!iLY PARTICULATC COMPOSITC C A i 's! A ILOTOPIC 10-3 nCi/ cubic roter C e-14 4 IMulCATOP. STATIO.4 SA:!PLC STATISTICS tJ U:l B C R OF SAf?PLCS 6.000 idIN I.'iUta V ALUC 1.500 S T A t4 C A R D DEV. 5.283 PANGC 13.500 ACArJ VALUE 5.183 :MAXIt'U" VALUE 15.000 VAPIAuCC 27.906 CL ASS viI CTil 1.450
* *
- III STOG RA:4 * *
- CLAGS WO. LOP:C R 13. UPPCP B. F R EQU C:,C Y PCL.FRCC.
_________ ________ ________ _________ __________'A 1 1.000 2.450 3.0 50 2 2.450 3.900 0.0 0 3 3.900 5.350 1.0 17 4 5.350 6.800 0.0 0 5 6.500 8.250 1.0 17 6 8.250 9.700 0.0 0 7 9.700 11.150 0.0 0 a 11.150 12.600 0.0 0 9 12.600 14.050 0.0 0 10 14.050 15.500 1.0 17
* *
- P LOT Or' fiI STOC P A'1* *
- 3.00 2.70 -
2.40 . 2.10 . l.80 . D
==
1.50 w l.20
-a h
a= B.90 { 6 0.50 0.30 . m m m EP EIS A r-. m m U.
- r m
m Rmm e- m a M
. CLR55 MIDPOINTE
* * *Et1V IROt1 MENTAL SAMP LE STATI STI CAL D ATA* *
- TAB LE 14 E Al RB ORN E I OD INE 5 G AMMA ISOTOPIC FCi/ cubic meter I-131 It1 DICA'IOR STATION SAMPLE STATISTICS NUfB ER OF SAMPLES 9.000 MINI!UM VALUE 0.020 STANDARD DEV. O.015 R At1GE O.050 g MEAN VALUE 0.041 MAXIFU M VALUE 0.070 5 VARIANCE 0.000 CLASS KIDT!! 0.007
* * *HI STOGR AM* *
- I CLASS NO. LOWER B. U PPER B . F REQ UENCY REL.FREQ.%
1 0.010 0.017 0.0 0 2 0.017 0.024 1.0 11 3 0.024 0.031 2.0 22 4 0.031 0.038 0.0 0 5 0.038 J . 04 5 4.0 44 6 0.045 0.052 0.0 0 7 0.052 0.059 0.0 0 8 0.059 0.066 1.0 11 5 9 0.066 0.073 1.0 11 3 1J 0.073 0.080 0.0 0
* *
- PLOT OF !!I STOGR AM * *
- 4.00 .
3.50 - 3.20 . 2.80 - 2.40 . U 2.00 -
==.J Lt l.60 .
S 0: i.20 - Lt. . 0.80 . 0.40 I m = a m s===== l CLR55 MiDPD1NTS I
* *
- ENVIRONMENTAL SAMP LE STATI STICAL D ATA* *
- TAB LE 15 ENV IRON!! ENTAL TLD READINGS TOTAL DOSE lct Qtr. rRem/Qtr.
GAMMA CONTROL STATION SAMPLE STATISTICS nub 3 ER OF SAMP LES 6.000 MI NIFU M VALUE 8.000 STANDARD DEV. 1.506 R AN GC 4.000 MEAN VALUE 10.333 MAXIFU M VALUE 12.000 VARIANCE 2.267 CLASS WIDTil 0.600
*** HISTOGRAM ***
i CLASS NO. LOWER B. UPPER B . FREQUENCY REL.FREQ.% 1 7.000 7.600 0.0 0 2 7.600 8.200 1.0 17 3 8.200 8.800 0.0 0 4 8.800 9.400 0.0 0 5 9.400 10.000 0.0 0 6 10.000 10.600 3.0 50 7 10.600 11.200 0.0 0 8 11.200 11.800 0.0 0 9 11.800 12.400 2.0 33 10 12.400 13.000 0.0 0
* *
- P LOT OF !!I STOGR AM * *
- 3.00 .
2.70 . 2.40 . 2.10 . l.80 . U
==
l.50 . LJ l.20 . S a= 0.90 . i u 0.50 . 0.30 . I m m m m m !% !!9 5 5' IEE' m M e.- r-co m m M M
.. CLR55 MlDPD1NTE
* * *ENV IRONMENTAL SAMPLE STATI STICAL DATA * *
- TABLE 15 g ENV IRONMENTAL TLD READINGS E TOTAL DOSE 2nd Q t r . rRem/Qtr.
GAMMA CONTROL STATION SAMPLE STATISTICS NU M3 E R OF S AMP LES 5.000 MINIMu t! VALUE 10.000 STANDARD DEV. 0.70 7 R AN GC 2.000 5 MEAN VALUE 11.000 MAXIMUM VALUE 12.000 3 VARIANCE 0.500 CLASS WIDTl! 0.400
* * *lli STOGR AM* *
- CLASS NO. LOWER B. UPPER B . FREQUENCY REL.FREQ.%
1 9.000 9.400 0.0 0 g 2 9.400 9.800 0.0 0 g 3 9.800 10.200 1.0 20 4 10.200 10.600 0.0 0 5 10.600 11.000 0.0 0 6 11.000 11.400 3.0 60 7 11.400 11.800 0.0 0 8 11.800 12.200 1.0 20 E 9 12.200 12.600 0.0 0 5 10 12.600 13.000 0.0 0
*** PLOT OF HISTOGRAM ***
3.00 - 2.70 - 2.40 . 2.10 . 1.80 . U Z. l.50 . w I I.20 . e e.se . W b.bb . 0.30 . m m E 93 E FS E E E5f3 E Y~d m d d d d d d d
.. CLR55 MlDPD1NTS
-100-
* * *ENV ITONf' ENTAL S APP LE STATI STI CAL DATA ***
TABLE 15 ENVIF . !PENTAL TL E RE ADINGS TOTAT. JOSE 3rd Otr. rrFerr/Q t r . GAMPA
- m. CONTFOL STATION SAMPLE STATISTI CS
!;Uf 3 ER OF SAMPLES 7.000 MINIfUM VALUE 7.000 STAND AFD D EV . 1.952 RANGE 6.000 MEAN VALUE 10.143 MA XI f V M V ALUE 13.000 VAPIANCE 3.810 CL ASS WIDTH 0.800
* * *H I STOGPA M * *
- CL AS S NO . LOhER B . UPPER B. FT EQ UENCY B E L. F FEQ. %
~
1 6.000 6.800 0.0 0 2 6.800 7.600 1.0 14 3 7.600 8.400 0.0 0 4 8.400 9.200 1.0 14 5 9.200 10.000 0.0 0 6 10.000 10.800 3.0 43 _ 7 10.800 11.600 0.0 0 0 11.600 12.400 1.0 14 9 12.400 13.200 1. 0 14 10 13.200 14.000 0.0 0
* *
- P LOT OF llI STCGPAM * *
- _ 3.00 .
2.70 . _ 2.40 . 2.10 . l.80 . U
==
l.50 q l.20 . 8 a: 0.e5 . w 0.50 . 0.30 .
. 92 R ES E 8 E. N. $ $
a E. s a s s s es = e a
. CLR55 MIDPOINT 5
-101-
* * *EtiVIRON!'EllTAL SAMPLE STA'lI STICAL DATA ***
TABLE 15 ..llVIEOtlFENTAL TLD READINGS TO'.'AL EOSE 4 th O tr . rr. Ectr /O t r . G A l'MA COhTIDL STATION SAMPLE STATISTICS NUf'B ER OF SAFPLES 7.000 MINIbUM VALUE 10.000 STANDAPD DEV. 1.512 RANGE 4.000 MEAN VALUE 11.571 MAXIEUM VALUE 14.000 VABIANCE 2. 28 6 CL ASS WIDTil 0.600 I
* * *H I ETOGRAM * *
- CL ASS NO.
LOWE F B . UPPER B. F PEQUENCY REL.FFEO.% I 1 9.000 9.600 0.0 0 E 2 9.600 10.200 2.0 29 5 3 10.200 10.800 0.0 0 4 10.800 11.400 2.0 29 5 11.400 12.000 0.0 0 6 12.000 12.600 1.0 14 7 12.600 13.200 1.0 14 8 13.200 13.800 0.0 0 9 13.800 14.400 1.0 14 10 14.400 15.000 0.0 0
* *
- P LOT OF III STOGR AM * *
- I 2.00 .
l.80 . l . EiB . 1.40 . l.20 . C
==
I.00 . W, 0.80 . F-3 0.s0 . a= W 0.40 . 0.20 . I mm m mmmmmmm l s s e ==5 0 0 E E C L F155 MiDPO1NT5
-102-I
* * *ENVIFONFENTAL SAMPLE ST ATI STICAL DATA ***
TABLE 15 ENVIFONt' ENTAL TLD PEADINGS TOTAL DOSE FOP YEAR mEem/Qtr . GAMPA CONTROL STATION SAMPLE STATISTICS , NUFB ER OF SAFPLES 25.000 MINIPUF VALUE 7.000 ETANDAFD DEV. ~ 1.562 RANGE 7.000 MEAN VALUE 10.760 MAXIFUM VALUE 14.000 VAPIANCE 2.440 CLASS WID711 0.900
* * *llI STOGRAM * *
- CL ASS NO. LOhE R B . UPPER B. FFEQUENCY REL.FREO.1 1 6.000 6.900 0.0 0 2 6.900 7.800 1.0 4 3 7.800 8.700 1.0 4 4 8.700 9.600 1.0 4 5 9.600 10.500 9.0 36 6 10.500 11.400 5.0 20 7 11.400 12.300 5.0 20 8 12.300 13.200 2. 0 8 9 13.200 14.100 1.0 4 10 14. 100 15.000 0.0 0
* *
- P LOT OF !!I STOGRAM * *
- 9.00 .
8.10 . 7.20 . 5.30 . s.40 . O
==
y.s0 . H 3.60 . e a= 2.70 . L.t- l.80 . 0.90 .
~
w Y~26 & 6 d d d i
. CLR55 MIDPOINTE
-103-
* * *Et;VIRONt'EtJTAL SAFPLE STATI STICAL DATA ***
I ENVIFONFENTAL TLD FEADIt;GS TOTAL DOSE lst Otr. crem/Otr. GAMMA INDICATOF STATION SAMPLE STATISTICS ?.Uf B ER OF SAFPLES 5.000 MINIbUt' VALUE 9.000 STANDAFD DEV. 2.345 RANGE 5.000 MEAN VALUE 11.000 MA XI t<U M V ALU E 14.000 VAPIANCE 5.500 CLASS hIDT!! 0.700 I
* * *H I STOGR AM * *
- CL ASS NO. LOKER B. UPPER B. FREQU EN CY RE L . F PEO . %
1 8.000 8.700 0.0 0 2 8.700 9.400 2.0 40 3 9.400 10.100 1.0 20 4 10.100 10.800 0.0 0 3 5 10.800 11.500 6 11.500 12.200 0.0 0.0 0 0 3 7 12.200 12.900 0.0 0 8 12.900 13.600 1.0 20 9 13.600 14.300 1.0 20 10 14.300 15.000 0.0 0
* *
- P LOT OF HI STOGR AM* *
- 2.00 .
1.80 . 1.50 . 1.40 . l.20 . O
==
i.aa . q a.se . S a.sa . a: LL 0.40 . 0.20 I
- - - w w w wwww YYY& d d d d d W l
CLR55 MiDPD1NTE I
-104-
* ** ENVIRONMENTAL S ANPLE STATI STI CAL DATA ***
T AB LE 15 ENVIRONMENTAL TLD READINGS TOTAL DOSE 2nd Otr. r Rer/Q tf . GAMPA INDICATOP STATION SAMPLE STATISTICS NUfG ER OF SAMPLES 5.000 MINIf U M VALUE 11.000 STAND AFD D EV . O.548 RANGE 1.000 MEAN VALUE 11.600 MA XI FUM VAL UE 12.000 VARI AN CE 0.300 CLASS h'IDTI! 0.200
* * *III STOGRAM * *
- CL ASS NO. LOhE R B . UFFER B. F REQU EN CY REL.FFEO.t 1 10.500 10.700 0.0 0 2 10.700 10.900 0.0 0 3 10.900 11.100 2.0 40 4 11.100 11.300 0.0 0 5 11.300 11.500 0.0 0 6 11.500 11.700 0.0 0 7 11.700 11.900 0.0 0 8 11.900 12.100 3.0 60 9 12.100 12.300 0.0 0 10 12.300 12.500 0.0 0
* *
- P LOT OF III STOGRAM * *
- 3.00 .
2.70 - 2.40 . 2.10 . 1.8B . D
==
I.50 . q l.20 . E3 a.sa . w 0.50 . 0.30 . d d d d d d d d d
~
ee
.. CLR55 MiDPD1NTE
-105-
* * *ENVIFONMENTAL SAMPLE STATISTICAL CATA***
ENVIRONMEllTAL TLD READINGS TO TAL DOSE 3rd Otr. m Tem /Q t r . GAMPA INDICATOF STATICN g SAMPLE STATISTICS l NUMB ER OF SAMPLES 5.000 MINIWM VALUE 9.000 STAND APD D EV . 0.894 RANGE 2.000 MEAN VALUE 10.400 MA XI FU M V ALUE 11.000 VAEI AN CE 0.800 CL ASS WIDTII 0.300 I
* * *llI STCGR AM * *
- CL ASS NO. LOhER B . UPPER B. F TEOU ENCY R EL .F FEO . t 1 8.500 8.800 0.0 0 2 8.800 9.100 1.0 20 3 9.100 9.400 0.0 0 4 9.4 00 9.'00 0.0 0 g 5 9.700 10.)00 0.0 0 g 6 10.000 10.300 1.0 20 7 10.300 10.600 0.0 0 8 10.600 10.900 0,0 0 9 10.900 11.200 3.0 60 10 11.200 11.500 0.0 0
* *
- P LOT OF III STOGRAM * *
- I 3.00 .
2.7B . 2.4a . 2.10 . l.Ba . U 2= l.50 - q 1.20 . O a: a.sa . u- 0.5a . a.30 . m u Nu u B3 W W3 M 9 m 9 m m u m 9 m e w s
.. CLR55 MiDPO1NTS g
106-
* * *EliVIFONFEtiTAL S A!1PLE ETATI STICAL EATA***
T AB LE 15 ENVIFONFENTAL .TLD READINGS TOTAL DOSE 4th Qtr. m Fert/Q t r . GAMPA INDICATOP STATION SAPPLE STATISTICS NUFB ER OF SAFPLES 5.000 MINIbUM VALUE 10.000 STAND ARD D EV . 1. 14 0 RANGE 3.000 MEAN VALUE 11.600 MAXI FU M V AL UE 13.000 VARI AN CE 1.300 CLASS WIDTH 0.400
* * *H I STOG RA M * *
- CL ASS NO. LOWE R B . UPPER B. F FEQU EN CY REL.FFEQ.%
1 9. 500 9.900 0.0 0 2 9.900 10.300 1.0 20 3 10.300 10.700 0.0 0 4 10.700 11.100 1.0 20 5 11.100 11.500 0.0 0 6 11.500 11.900 0.0 0 7 11.900 12.300 2.0 40 8 12.300 12.700 0.0 0 9 12.700 13.100 1.0 20 10 13.100 13.500 0.0 0
* *
- P LCT OF HI STCGRAM* *
- 2.00 .
l.80 . 1.50 . 1.40 . 1.20 . U 1.00 -
==.J Lt B.90 .
e a 0.s0 . L.6 U.40 - B.20 . esa E B EM R I2S 5 5 ER R Dd & d d d d d d d CLR55
. MIDPOINT 5
-107-
* * *Et VIROtJFENTAL S AMPLL STATI STI CAL EATA***
I ENVIFONf' ENTAL TLD BEADINGS TOTAL COSE F CR YE AP mFem/O tr. GAM MA INDICATOF STATION SAMPLE STATISTICS !;UMB ER OF SAFPLES 20.000 MINIFU M VALUE 9.000 STAND AFD D EV . 1.387 RANCE 5.000 MEAN VALUE 11.150 MA XI F U F V /.L UE 14.000 VAFIANCE 1.924 CLAES WID7H 0.700 I
* * *H I Si CCR AM * *
- CL ASS NO. LChEP B. UPPER B. FREQUENCY REL.FFEC.%
1 8.000 8.700 0.0 0 2 8.700 9.400 3.0 15 3 9.400 10.100 3.0 15 4 10.100 10.800 0.0 0 5 10.800 11.500 6.0 30 6 11.500 12.200 5.0 25 7 12.200 12.900 0.0 0 8 12.900 13.600 2.0 10 9 13.600 14.300 1.0 5 10 14. 300 15.000 0.0 0
* *
- P LC 7 O F HI ST CGR AP * *
- I B.00 .
5'.40 . 4.80 . 4.20 . 3.50 . t; 3.00 . z L_1 2.40 . a: I.80 . L _. 1.20 . 0.80 . se to to W3 k2 kG W K) 'm^ is YYYd d d d d d W
. CLR55 MIDPOINTE
-108-
* * *EllVIFOtil El4'I AL S AFP LE ST ATI STI CAL EATA***
TABLE 16 CONTINGUS PADI ATION BONITOFS AVG. l'ONTHLi VALUE mr/hr GAMFA CO!1Tf0L STATION SAMPLE STATISTICS NUFB ER OF SAFPLES 12.000 MINIFUM VALUE 0.020 STAtJDAED D IV . O.006 RANGE 0.022 FIAN VALUE 0.029 MA XI b.U E V AL UE 0.04 2 VAPIANCE 0.C00 CLI SS WID'IH 0.004
* *
- H I STCG RA N * *
- CL ASS NO. LOKEP B. UPPER B. FEE 00ENCY REL.FFEO.%
1 0.010 0.014 0.0 0 2 0.014 0.018 0.0 0 3 0.018 0.022 2.0 17 4 0.022 0.026 3.0 25 5 0.026 0.030 1.0 8 6 0.030 0. 0 34 3.0 25 7 0.034 0.038 2.0 17 8 0.038 0.042 0.0 0 9 0.04 2 0.046 1.0 8 10 0.046 0.050 0.0 0
* *
- P LOT OF HI STCGR AM* *
- 3.00 .
2.70 . 2.40 . 2.10 . 1.80 - D
==
1.50 . l.20 - 8 a.se - a= L.i.- U.50 . 0.30 -
. iEi E E E E E E E E !#
& & & & & & & & & m
. CLR55 MIDPOINTE
-109-
* * *EtiV IRONNENTAL SAMP LE ST ATI STICAL DATA * *
- cot;TINOUS RADI ATION MONI f0RS AVG. mot 1TilLY VALUE mr/hr GAMPA INDICATOR STATION E SAf'PLE STATISTICS g
NUtiBER OF SAMPLES 108.000 MINIMUM VALUE 0.013 STANDARD DEV. O.009 RANGE 0.034 MEAN VALUE 00?'l MAXIEU M VALUE 0.047 VARIANCE 0.000 CLASS WIDTH 0.004
* * *ll I STO GR A N * *
- CLASS NO. LOhER B. UPPER B. FREQUENCY REL.FREQ.%
1 0.010 0.014 4.0 4 2 0.014 0.018 23.0 . 21 3 0.018 0.022 40.0 37 4 5 0.022 0.026 0.026 15.0 14 g 0.030 2.0 2 3 6 0.030 0.034 10.0 9 7 0.034 0.038 2.0 2 8 0.038 0.042 7.0 6 9 0.042 0.046 3.0 3 10 0.046 0.050 2.0 2
* *
- P LOT O F !!I STOGRA M * *
- I 40.00 .
3t5 . 00 . 32.00 . . 28.00 . 24.00 . t: 20.00 . 2= w I 15.00 . oc 12.00 . Lt B.20 - 4.00 . 3 I e e a . . m m m m = m m = m m 3
. CLR55 MIDPDlNTS g
-110-
* * *EtJVIPOt1FENTAL sal'PLE STATI STICAL DATA ***
TABLE 18 MILK GAMPA I SOTOPIC [C i /1 K-40 COf1TFOL STATIO!J SAFPLC STATISTICS I;UFB ER OF SAFPLES 7.000 MINIbUF VALUE 990.000 STANDARD DEV. 221.499 RANCE 610.000 PEAll VALUE 1284.286 MAXI MIE V ALUE 1600.000 VAFIANCE 49061. SOS CLASS lilDTI: 79.000
* * *llI STOCR AM * *
- CLASS NO. LOWE R B . UPPER B. FFEQUENCY REL.FFEQ.1 1 900.000 979.000 0.0 0 2 979.000 1058.000 1.0 14 3 1058.000 1137.000 1.0 14 4 1137.000 1216.000 2.0 29 5 1216.000 1295.000 0.0 0 6 1295.000 1374.000 0.0 0 7 1374.000 14 53.000 1.0 14 8 1453.000 1532.000 1.0 14 9 1532.000 1611.000 1.0 14 10 1611.000 1690.000 0.0 0
* *
- P LOT OF III STCGRAM * *
- 2.00 .
1.80 . l.50 . 1.40 . 1.20 . t; i.aa .
==
W, B.BB . e a: a.se . Lt- B.4B . D.20 . u ": "! ": "! "! M E u" O $ m e Q =W 2e 5
~
- m _ r a
. CLR55 MIDPOINTE
-111-
* * *Et.VIPOliFENTAL S APP LE ST ATI ST ICAL DATA ***
TABLE 18 MILK GA MMA ISOTOPIC TCi /] K-40 IhDICATOP STATION SAPPLE STATISTICS tiUfBER OF SAPPLES 28.000 MIt1If Ut* VALUE 800.000 ST AND A FD DEV. 285.858 PAriCE 1100,000 3 MEA!J VALUE 1405.000 MAXI FU f: VALUE 1900.000 3 VAEIANCE 81714.815 CL ASE WIDill 120.000
* * *H I STOGR A M * *
- CLASS !!O. LOhTR B . UPPER C. F F EOUf fiCY REL.FPEQ.1 1 750.000 870.000 1.0 4 2 870.000 990.000 3.0 11 3 990.000 1110.000 1.0 4 4 1110.000 1230.000 2.0 7 5 1230.000 1350.000 4.0 14 6 1350.000 1470.000 4.0 14 7 1470.000 1590.000 3.0 11 8 1590.000 1710.000 7.0 25 9 1710.000 1830.000 1.0 4 10 1830.000 1950.000 2. 0 7
* *
- P LOT OF HI STOGR AM * *
- 7.00 .
5.30 - 5.50 . 4.90 . 4.20 - D 3.50 .
==_J La 2.80 .
8 m 2.10 . Lt l.40 . 0.70 . m m . . . . .
. EE5 f*4 is 9 e = 0 EE e e C- e
.. CLR55 MlDPD1NTE
-112-
* * *E NV I FONf'E NTAL S AMP LE ST ATI STICAL D ATA* *
- TAB LE 18 MI LK: STATI ON #5 STRONTIU M PCi/l Sr-90 CONTROL STATION SAMPLE STATISTICS NUfGER OF SAf'PLES 7.000 MINIMUtt VALUE 3.000 STANDARD DEV. 2.040 RANGE 6.000
+ MEAN VALUE 5.886 MAXIIUM VALUE 9.000 VARIANCE 4.161 CLASS WIDTII 0.700
* * *l1I STOCR AM * *
- CLASS NO. LOWER B. UPPER B. FREQUENCY REL.FREQ.%
1 2.500 3.200 1.0 14 2 3.200 3.900 0.0 0 3 3.900 4.600 1.0 14 4 4.600 5.300 1.0 14 5 5.300 6.000 1.0 14 6 6.000 6.700 1.0 14 7 6.700 7.400 0.0 0 8 7.400 8.100 1.0 14 9 8. 100 8.800 0.0 0 10 8.800 9.500 1.0 14
* *
- P LOT O F III STOGRAM* *
- l.00 .
0.90 - 0.80 . 0.70 . 0.50 . t
==
0.s0 . LtJ B.40 . B a 0.30 . Lt 0.20 . O.10 .
. M M M M M M M M M M N M =r; :s ed us e: r: ed ed
. CLR55 MIDPOINTE
-113-
* *
- EtIV IRO?D'EtJTAL SAMP LE ST ATI STI CAL D ATA * *
- TAB LE 18 MILK STRONTIUM pC1/1 Sr-90 INDICATOE STATION SAMPLE STATISTICS NU!GER OF SAMPLES 28.000 MINIMUM VALUE 2.500 ST ANDARD DEV . 1.814 RANGE 7. 500 MEAN VALUE 5.925 MAXIEU!! VALUE 10.000 VARIANCE 3.292 CLASS WIDTil 0.850
* * *llI STOGRAM * *
- CLASS NO. LOWEF B. UPPER B. FREQUEtJCY REL.FREO.%
1 2.000 2.850 1.0 4 2 2.8 50 3.700 2.0 7 3 3.700 4.550 2.0 7 4 4.550 5.400 8.0 29 5 5.400 6.250 3.0 11 6 6.250 7.100 3.0 11 7 7.100 7.950 4.0 14 8 7.950 8.800 4.0 14 9 8.800 9.650 0.0 0 10 9.650 10.500 1.0 4
* *
- P LOT O F !!I STOGRAM* *
- 8.00 .
7.20 . 6.40 . E.50 . 4.80 . t; 4.00 . 2= LtJ 3.20 . O a: 2.40 . w 1.50 . 0.80 -
- 9
~
k 9 n-54
=-
R w EB Di 9 3-
. CLR55 MIDPOINTE
-114-
* * *EtiVIROtJFEtJTAL sat:PLE STATI STICAL DATA ***
TABLE 18 MILK GAMFA ISOTOPIC Wi/1 Cc-137 CO!JTIDL STATIO!J SAMPLE STATISTICS 1:UbE ER OF SAFPLES 7.000 MItJIbUF V ALUE 2.400 STAND A FD D EV . 1.977 RANGE 5.400 FEA?J VALUE 5.829 MA XI bU b: VALUE 7.800 VARIAtiCE 3.909 CLASS WIDTl! 0.560
* * *1!I STOGR Ah! * *
- CLASS IJO. LOhEP B. UPPER B. F FEQU EtJCY REL.FFEQ.%
1 2.200 2.780 1.0 14 2 2.780 3.360 0.0 0 3 3.360 3.940 0.0 0 4 3.940 4.520 1. 0 14 5 4.520 5.100 0.0 0 6 5.100 5.680 1.0 14 7 5.680 6. 260 0.0 0 8 6.260 6.840 2. 0 29 9 6.840 7.4 20 0.0 0 10 7.420 8.000 2.0 29
* *
- P LOT OF III STCGRAM * *
- 2.00 .
l.80 . l.50 . l.40 . 1.20 . U
==
l.00 . LA_J U.BU . w Es e.so a: La_. D.40 . 0.20 . nJ r,-i n-i e d U U i.4 W W
. CLR55 MIDPOINTE
-115-
* * *ENVIRONFENTAL SAf'PLE STATI STICAL DATA <**
TABLE 18 f4ILF GAFfM I SOTOP I C [C i'/1 Cs-137 II.DICATOF STATION SAMPLE STATISTICS NU f.'B ER OF S A FPL E S 28.000 tiltlIFU M V ALUE 3.400 ST AND AliD DEV. 7.094 RANGE 29.600 MEAN VALUE 9.936 MAXIFUF VALUE 33.000 VAEIANCE 50.327 CLASS WIC'Ill 3. 0 50
* * *11 I STCG R A N * *
- CL AS S NO . LCKER B. UPPER B. F EEOUENC Y REL.FREC.i 1 3.000 6. 0 50 9.0 32 2 6.050 9.100 6.0 21 3 9.100 12.150 8.0 29 4 12.150 15.200 1.0 4 5 15.200 18.250 2.0 7 6 18.250 21.300 0.0 0 7 21.300 24.350 0.0 0 8 24.350 27.400 0.0 0 9 27.400 30.450 1.0 4 10 30.450 33.500 1. 0 4
* *
- P LOT OF !!I STOGR A f' * *
- 9.00 .
B.IB . 7.20 . 5.30 . s.40 . O
==
q.s0 . q 3.50 . 8 a= 2.70 . L _. l.80 - D.90 I
. u m R N N 9 9 m. m. R 9 W ES O !E E2 Ri K} FO A
.. C L F155 MiDPD1NT5
-116-
* * *E NVIFOt1FE twTAL S AFP LE STATI STICAL DATA ***
TABLE 20 ME AT and PCULTFY GAFMA ISOTOPIC FCi /g (wet) K-40 II; DICA 700 STATIOtJ SAMPLE STATISTICS t;UtBER OF SAFPLES 10.000 MINIMJ t' V ALUE 1.500 STAT D AFD DEV. O.457 RANCE 1.300 ME AN VALUE 2.100 t:AXIFUF VtLUE 2.800 VA PI A!;CE 0.209 CLASS WIDTH 0.200
* * *H I STO CR A M * *
- CLASS NO. LOWE R D . UPPEP D. FF EC UENCY REL.FEEQ.1 1 1.000 1.200 0.0 0 2 1.200 1.400 0.0 0 3 1.400 1.600 1. 0 10 4 1.600 1.800 2. 0 20 5 1.800 2.000 1.0 10 6 2.000 2.2u0 2. 0 20 7 2.200 2.400 1.0 10 8 2.400 2.600 1. 0 10 9 2.600 2.800 1. 0 10 10 2.800 3.000 1. 0 10
* *
- P LOT OF HI STCGRA t.* *
- 2.00 .
1.80 . 1.50 . 1.40 . l.20 . t; i.aa .
==
q 0.80 . Em, B.sa . a: 6 0.40 . B.20 .
. E
- M 5 '
s M E M S W M
-- .: - - M M M M M
.. C L F155 MiDPD1NT5
-117-
* * *EtiVIFOtit'EllTAL SAPP LE STATI STI CAL CATA***
TABLE 20 ME AT and PCULTF Y GAPPA ISOTOPIC [C i /g (wet) Cc-137 It:DICATOP STATIC!J SAMPLE STATISTICS t:UoB EF OF SAPPLES 7.000 MINIBUF VI,LUE 0.013 STAT;DAFD D LV . O.011 R AllCE 0.027 E MEAN VALUE 0.021 MAXIEUb'V/LUE 0.040 E VAF.IAt:CE 0.000 CLt.S S WIDT!! 0.004 I
* * *III STOGR A tr * *
- CL AS S 110. LCliEP B. UPPER B. F F ECUEN CY REL.FFEQ.1 1 0.010 0.014 1.0 14 g 2 0.014 0.010 3.0 43 3 3 0.018 0.022 1.0 14 4 0.022 0.026 0.0 0 5 0.026 0. 030 0.0 0 6 0.030 0. 034 1.0 14 7 0.034 0.038 0.0 0 8 0.038 0.042 1.0 14
- 9 0.04 2 0.046 0.0 0 $
10 0.046 0.050 0.0 0
* *
- P ILT O P !!I STCG RA P * *
- 3.00 -
1 2.70 . 2.40 . 2.10 . l.80 . D
=
I.50 . La J l.20 - Eri 0.s0 . a= w 0.50 . 0.30 I
. m = = = a a = = = m
& & a & & a & & & &
f L F155 MlDPDINTE I
~ -118-
* * *E tJVIPOt;FE!;TAL S AMP LE STI TI STI CAL D ATA* *
- TABLE 20 PFODUCC GA FMA ISOTOPIC FCi/g (wet)
K-40 II; DICA'IOD STATIOtJ SAMPLE STATISTICS t.Ut'B EP OF SAMPLES 9.000 MIt!ItUP VALUE 0.E00 ST A?;D A FD DEV. 1.386 RAtJGE 4.000 MEA!1 VILUE 2.211 MAXIlUF VALUE 4.800 VAPIAtJCE 1.921 CLISS WID711 0.440 s ._ * * *!! I STOGRAM * *
- CLASS tJO. LCWE R B . UPPER B. FrECUEtJC Y REL .F TEO. It 1 0.600 1.040 2.0 22 2 1.040 1.480 1.0 11 3 1.480 1.920 2.0 22 4 1.920 2.360 1. 0 11 5 2.360 2.800 0.0 0 6 2.800 3.240 1. 0 11 7 3.240 3.680 0.0 0 8 3.680 4.120 1. 0 11 9 4.120 4.560 0.0 0 10 4. 560 5.000 1.0 11
* *
- P LOT OF !!I STCG FAM * *
- 2.00 .
i.s0 . 1.50 . 1.40 . 1.20 . U
==
l.00 . q 0.e8 . d a= 0.50 . La 0.40 . 0.20 .
. E N N E Bi E !ja g g g M
ed - -- M M M M & &
. CLR55 MIDPOINTE
-119-
9
- - - - i -is-- --- - - --
E VI. DATA Str1%RY Af1D CONCLUSIONS
-126-
VI DATA
SUMMARY
AND CONCLUSIONS The results of the 1978 Radiological Environmental Monitoring Program must be put into perspective considering the natural processes of the environment and the aggregate of past data. Several factors must be considered in the course of radiological data evaluation and inter-pretation. First, it must be recognized that our environ includes an abundant inventory of natural background radiation of primordial and daily origin which is in a constant state of flux, influenced by a myriad of phenomena, from solar activity to barometric pressure. Secondly, the detonation of man-made nuclear devices in the atmosphere has resulted in an extensive array of radioactive isotopes in the atmosphere and on the surface of the Earth from global fallout. Section VII, titled HISTORICAL DATA, contains sample statistics from previous environmental sampling. In the process of determining the impact (or lack of impact) of the plant on the environment, the scrutiny of past analytical data can be a tool by which positive (and possible negative) trends cari be discerned. The interpreation of historical data in this report was done to a limited degree. Because of the constant change in analytical sensitivities, as state-of-the-art detection capa-bilities improve, data comparisons become difficult. Minimum detection capabilities for the 1969 and 1974 analyses of c,:vironmental data would be considered anomalies by 1979 analytical standards. A. LAKE PROGRAM Tables 3 through 9 list the analytical results for the aquatic media sampled during the 1978 sampling program. Aquatic samples were obtained at a coabination of four on-site locations. The transect designations used for the on-site sampling are NMPW (01), NMPP (02), JAF (03) and NMPE (04). Due to the local unavailability of certain required sample media, samples could not be obtained consistently at each of the same on-site transects sampled for cther media. Off-site samples were collected in the vicinity of the Oswego Harbor 0FF-SITE (00).
- 1. Periphyton - Table 3 The collection and analysis of periphyton organisms was per-formed twice during 1978. The first collection was on 6/27-28/78 and the second collection'was completed on 8/23/78. The results of gamma spectral analysis of these samples is pre-rented in Table 3, section IV. Analytical results show that a significant concentration of Cc-144 (pCi/g) was present in periphyton organisms collected on 6/27-28/78. The origin of Cc-144 in the periphyton samples is not totally certain, but the majority of evidence indicates that the concentration of Cc-144 in the sample is the result of atmospheric nuclear testing, fallout and the subsequent runoff into Lake Ontario.
The first piece of evidence that indicates that the presence of Cc-144 is not plant related is the fact that a concentra-tion of 0.10 + 0.06 pCi/g (vet) was present in the control station sample. The control station is located in the Oswego Harbor, 8 miles west of the site.
-121-
Based on the meterology and limnology of the area, the control station should not be impacted by plant operation. The liquid release of Ce-144 for the second half of 1977 and the first , half of 1978 was low with a total concentration of 2.89 x 10 ~ Ci. Calculation of expected concentrations of Ce-144 in aquatic plants can be made. Using a bioaccumation factor of 11 4000 pCi/kg per pCi/1 a discharge dilution o{01 82 x 10 liters, a release concentration of 2.90 x 10 pCi of Cc-144 and a near field dilution factor of 6, the maximum concentration of Ce-144 that can be expected to be found in periphyton organisms residing in close proximity to the plant is 0.106 _ pCi/g (wet). The calculated concentration of 0.106 pCi/g (wet) is a very conservative calculation and is well below the concentration present in the July 1978 sample. If a more realistic far-field dilution factor of 9 is used a maximum expected concentration of 0.071 pCi/g (wet) can be calculated which is 15 times less than the analytical results, indicating that the Cc-144 in the periphyton must be due to a source other than the plant effluent. The recond set of periphyton samples collected showed a reduc-tion in Cc-144 activity by a factor of 10 for the indicator or on-site sample stations using the maxima for each sample period. The concentration of Cc-144 at the off-site or control location showed a slight increase in activity from 0.10 pCi/g (wet) to 0.13 pCi/g (wet) . The presence of Cc-144 in both of the off-site sampics, further reinforces the belief that its presence is due to sources other than the plant. A concentration of 0.10 1 0.01 pCi/g (wet) of Co-60 was found in the August sample at the NMPP (02) transect. The signi-ficance of this level of activity may be only that it is 10 times the control station results. The total liquid release of Co-60 for the second half of 1977 and the first half of 1978 was equal to 0.235 Ci. An integrated release of this quantity should not produce any detectable environmental impact and was we'l within the discharge limits imposed by the plant's Technical Specifications. It should also be noted that the detection of a small quantity of Co-60 in the off-site or control station may indicate the presence of Co-60 is Lake Ontario periphyton. As stated above,any samples collected from the off-site location should be outside the influence of plant operation. A dose calculation from activity found in the lake periphyton is difficult as these organisms are not in the human food chain. For the purpose of illustration a dose calculation can be made using some unrealistic assumptions. If an adult were to consume 64 kg/yr of periphyton (an amount equal to the maximum annual adult consumption of Icafy vegetables), the dose from the on-site Cc-1]4 concentration would be 0.0018 mrem /yr (whole body) and would be 0.03 mrem / yr (whole body) from Co-60 with the total dose being equal to 0.0318 mrem /yr. The significance of this greatly over estimated dose is very low with respect to natural background radiation and the changes in the natural background 1cvels due to mans activities.
-122-M - - -
An examination of past periphyton data shows a decline in activity of Cc-144 and Co-60 in the periphyton organisms in the vicinity of Nine Mile Point. Past levels of Cc-144 and Co-60 are presented in graphic form in figures VIII-6 and VIII-7 respectively.
- 2. Botton Sediment - Table 4 Bottom sedt ant sampics were collected twice during the 1978 sampling effort. Gamma spectral analysis and Sr-90 analysis results are listed in table 4. The review of bottom sediment analysis results indicated that Cs-137 was the major nuclide occuring in this media. The presence of Co-60 was also de-tected in possibly significe t concentrations with a maximum concentration of 1.5 pCi/g (dry) at the JAF (03) sample loca-tion. The presence of Cs-137 in sediment samples may be attributed to a large extent, to the detonation of nuclear devices in the atmosphere. The long radioactive half life of Cs-137 (30 years) is condusive to the accumulation of this fission product in the environment. The presence of detect-able concentrations of Cs-137 at the off-site (00) sample station is strong evidence that the Cs-137 activity is from sources other than plant effluents.
The June 1978 sediment samples showed a Co-60 concentration of 1.50 + 0.20 pCi/g (dry) at the JAF (03) on-site sample location. The presence of Co-60 in sediment off shore from the plant may be due to deposition of plant effluents. The sediment found in areas of the plant is transient by nature often stirred up the regicn winde and waves, keeping sediment in the area from becoming heavily layered. The physical makeup of the aff-shore area is predominantly bedrock. The chemical properties of the sediment may cause Icw concentrations of trace metals to become concentrated by acting as an ion exchange medium with the dissolved material in the lake water. A second consideration that should be noted is that Co-60 concentrations in the vicinity of Nine Mile Point may be the results of atmospheric detonation of nuclear devices and the widespread global fallout and concentration of isotopes from surface runoff. The fact that higher concentrations were present at the on-site locations could be related to the non-existant or slow sedimentation rate of the promontory area while the control station located at the mouth of the Oswego River, would have a very high sedimentation rate, thus masking any radionuclide build up in buried sediment layers. The total liquid release to the lake for the third and fourth quarter in 1977 and the first and second quarters of 1978 was 0.270 Ci of Co-60 and 0.0134 Ci for Cs-137. All releases were well within effluent limits contained in the plant's technical specifications.
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The dose to man cannot be directly calculated for lake bottom sediment as bottom sediment is not accessible to man and any radioactivity found in the rediment is shicided by the over lying water. In addition, lake sediment is not direcity in the food chain of man or aquatic life. Bottom feeding biota may ingest small quantities of sediment but to a very limited degree. No passage of radionuclides to the human food chain from material deposited in lake sediment is expected. To display the impact of radioactivity in sediment samples with respect to the dose to man concept, the unlikely assumption could be made that lake bottom sediment could at some future time find its way to the surface and F:come shoreline sgdi-ment. Assuming that the density of sediment is 40 kg/m- (dry) and an average residence time on the shore of 47 hr/yr for a teenager, the annual dose from a Cs-137 concentration of 2.1 pCi/g (dry) would be 0.017 mrem /yr whole body and the dose from Co-60 with a concentration of 1.5 pCi/g (dry) would be 0.048 mrem /yr whole body, resulting in a total whole body dose of 0.065 mrem /yr. This dose could be considered minimal, if not insignificant with respect to natural background levels. A review of historical data shows the levels of Cs-137 to be randomly distributed with no definable trend evident. Past levels of Cs-137 and Co-60 are depicted in Figures VIII-8 and VIII-9.
- 3. Mollusks - Table 5 The results of Mollusk sampling are presented in table S.
Sampling efforts for mollusks in the vicinity of Nine Mile Point were of limited success during the first collection, in June, 1978. The lake bottom configuration off shore from the site is mainly bedrock, with sediment of insufficient depth to sustain a mollusk population. For this reason only NMPh' (02) and the off-site (00) location yielded sufficient quantities for a meaningful analysis in the June 27 ar.d 30, 1978 sample collection. Sufficient quantities were obtained at the off-site and 2 on-site transects in the October 2, 1978 collection. During both collections no mollusks were found on the JAF (03) t ransec t. Gamma spectral analysis revealed the presence of Mn-54 and Co-60 activity in mollusk tissue. Sh-54 activity was found in both co11cetions at the NMPP (02) sample transect. A possible explanation for the existence of such a disproportionate concentration of 55-54 could be the very high bioaccumation factor of manganese for fresh water mollusk of 90,000 pCi/kg per pCi/1. Such a high bioaccumulation factor would result in a rapid accumulation of manganese activity in mollusks which are indigenous to the off-shore area of the site. The total release of Co-60 and Sh-54 via liquid effluent from the plant for the period of July 1, 1977 to June 30, 1978 was 0.235 Ci for Co-60 and 0.199 Ci for 5b-54. Discharge di this same period of time was equal to 5.89 x 10}gition flow for liters.
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The fresh water mollusks found in the vicinity of Nine Mile Point are not consumed by humans and are considered to be in the aquatic food chain to only a limited degree. Because fresh water mollusks are not considered edible, no accurate estimate of the possible dose contribution to man from their use as a food can be made. A dose estimate can be made using inflated parameters for the purpose of evaluation of possible dose contribution from the use of fresh water mollusks. Using the average individual consumption of seafood of 1.0 kg/yr for an adult the dose due to ingestion would be 0.001 mrem /yr whole body and 0.015 mrem /yr to the gastrointestinal tract from 56-54 concentrations. The dose resultirg from a Co-60 concentration of 0.22 pCi/g (wet) would be 0.001 mrem /yr whole body and 0.009 mrem /yr to the gastrointestinal tract. The maximum dose received from consuming 1 kg of fresh water mollusks in a year's time would be 0.002 mrem /yr whole body and 0.24 to the gastrointestinal tract. As illustrated above, the resulting dose is very low and in reality would probably be 0.00 because the species is inedible. The review of past data shows that Sr-89 and Sr-90 levels are declining but a limited number of data points does not provide evidence of a distinct trend. Graphs of previous mollusk samples with respect to 55-54 and Co-60 levels, are presented in figures VIII-10 and VIII-11,
- 4. Gammarus - Table 6 Gammarus samples were collected twice during 1978. The first sample collection yielded masses of 9, 12, and 38 grams at the NMPP (02), JAF (03), and off-site transects respectively. The August 1978 sampling effort yielded marginally sufficient sample volumes from JAF (03) transect with 248 grams and the off-site (00) transect with 478 grams. The NMPP (02) transect yicided only 64 grams of sample. Several attempts were made on each collection using a variety of sampling methods.
In spite of the low sample volumes, sensitivity of the gamma spectral analysis remained low. 50L values for Sr-89 analy-ses ranged from <0.07 to <0. '0 pCi/g (wet) . Insignificant 1cvels of Cs-137 and Ce-144 were detected in both the off-site sample and the on-site JAF (03) sample from the August 1978 collection. Both the Cs-137 and Cc-144 are suspected to be the result of atmospheric nulcear testing along with Sr-90 activity which was detected at all locations from the June and August collections.
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An additional detectable measurement resulting from the analysis of gammarus samples was a 0.10 + 0.10 pCi/g (wet) concentration of Mn-54 found in the August NMPP (02) sample. The associated error for the analysis is on the order of 100'. resulting in littic analytical confidence in the results. Even if this lack of confidence was resolved the significance of the possible activity present is very small from a dose to man standpoint and an environmental impact viewpoint. The presence of trace amounts of Mn-54 in aquatic organisms can be related to the large bioaccumation factor of many fresh water o rgar.i sms . The analyses of gammarus show no significant impact from plant operation. IIistorical gammarus data shows reduction of Sr-90 levels in the organism. Cs-137 levels show a similar reduc-tion in the activity levels feua-1 in gammarus in the vicinity of the site.
- 5. Fish - Tabic 7 A total of 28 fish samples were collected from Lake Ontario and were analyzed for gamma emitters, Sr-89 and Sr-90 acti-vity. Sample collections were made during May (spring season) and October (fall season) at 2 on-site locations (NMPP-02, JAF-03) and one off-site location (OFF-SITE 00) .
Analysis results indicate no detectable impact from the operation of the plant. The data does show however a number of isotopes present in fish samples which can be directly attributed to atmospheric nuclear testing. Cs-137 levels were detected in 25 of the 28 samples collected for 1978, from both on-site and off-site sample locations. In addition, Sr-90 levels were detected in 20 of the 28 samples, again at both on-site and off-site locations. Because Lake Ontario fish are in the human food chain a reasonable estimate of dose to man can be made. Assuming that the average adult fish consumption is 6.9 kg/yr and the maximum activity level of 0.20 pCi/g (wet) for Cs-137 and 0.25 pCi/g (wet) for Sr-90 as found in the sampics are used, the calculated dose to man would be 0.33 mrem /yr whole body and 1.31 mrem /yr to the bone. If the amount of fish consumed were raised to the estimated maximum of 21 kg/yr, the resulting dose would be equal to 1.28 mrem /yr whole body and 4.31 mrem to the bone. The dose resulting from atmoshperic testing via fish samples can be calculated to be many times the dose calculated for previous sampled media, which may be considered to be related to the operation of the plant. 1.istorical data shows that the level of Cs-137 in the locally sampled fish has declined. Cs-137 activity reached a mean high of 1.40 pCi/g (h'et) in 1975 (at the indicator stations) and has fallen off.to the present mean low of 0.08 pCi/g (wet). Sr-89 and Sr-90 levels have shown a parallelism to the Cs-137 trend, with a mean high in 1976 of 0.27 pCi/g (wet), a present low of 0.01 pCi/g (wet) and 0.01 pCi/g (wet) for Sr-89 and Sr-90 respectively. Cs-137 levels have been graphed and may be found in figure VIII-12.
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- 6. Lake Water - Tables 8A, 8B, 9 Lake Water samples are analyzed for gross beta, tritium, strontium 89, strontuim 90, and gamma emitters.
Gross beta, tritium and strontuim 89 and 90 analyses showed no evidence of plant related radiological impact on the environ-ment. The gross beta mean activity for 1978 was significantly lower than all previous years that analyses of lake water has been performed. This reduction in activity is most directly attributed to the improvement of analytical procedures and equipment. Lake water tritium has an indicator mean activity of 389 pCi/1 for 1978. Tritium levels in the area of Nine Mile Point have remained constant since sampled for H-3 (1974-1978). Tritium is a naturally occuring radioactive isotope of hydrogen which is produced in the upper atmosphere by cosmic radiation. The fact that Tritium is naturally occurrin may account for background levels in the lake varying slightly from year to year. Strontium-90 activity was detected in 9 of the 12 quarterly sampics. Both the on-site and off-site sample locations showed detectable levels of Sr-90, ranging from 1.10 pCi/1 to 0.40 pCi/1. As in the fish samples above, Sr-90 levels can be attributed to atmospheric nuclear testing. Overall Sr-90 levels have decreased slightly, fror 1977 to 1978. Strontium-89 was detected in 3 on-site samples during the year. All detectable Sr-89 activities were at or below the MDL level with associated errors ranging from 50 to 85 percent. The presence of these levels of Sr-89 is not considered to be significant and may be attributed to reccat atmospheric testing by the People's Republic of China. Analysis was performed on 36 monthly composites from 3 sample locations. Fluctuating backgrounds in plant counting equip-ment often resulted in background concentrations larger than the gross sample concentrations. The net sample concentrations were reported as 0.00+ accumulative error- (background error + sample error) . A number of posi.tive activities were detected for Co-60 and Mn-54. however, the larte error associated with the determination could Icad to the conclusion that no acti-vity was present in the sample and was the result of in-plant background. Because of the large associated analyses error and fluctuating counting room background, all samples after June 1978 were sent to a contractor for analysis so that lower background variations, and therefore lower statistical counting errors, would result. As indicated in table 9 (section IV) all analy-ses after June 1978 resulted in no positive detectable IcVels of activity, as would be expected, all analytical results were reported at MDL 1cvels.
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The following nuclides were detected in the control location samples but do not show up in Table 9. They were excluded from this table because they were detected only once during 1978. Month Nuclide* NMP Inlet JAF Inlet Raw City Water March Zn-65 <17.3 19.5 + 5.5 <15.3 April I-133 3.4 1 2.4 <5.2 <5.1
- Concentration in pCi/1 B. LAND PROGRAM The results of terrestrial sample analyses for the 1978 reporting period are incluc ed in Tables 10 through 20.
- 1. Air Particulates - Tables 10 and 11 Tables 10 and 11 give the air particulate gross beta results for the 6 off-site and 9 on-site stations respectively. No significant levels of gross beta activity were present on the 315 off-site samples or the 466 on-site samples analyzed during the 1978 program. The off-site air monitoring stations showed a gross beta activity slightly greater than the associ-ated on-site stations for the same sample period (off-site mean of 0.14 pCi/m 3
, on-site mean of 0.10 pCi/m3 ). Both the off-site and on-site gross beta activity are up slightly from the four previous years, but are significantly lower than the activity levels for 1969. This change in gross beta activity over the years can be attributed to several factors. In the early 1960's, atmospheric detonation of nuclear devices was proliferous. With the adoption of nuclear test ban treaties by most 6f the world's countries, the atmosphere had purged itself of most of the contaminates from this testing. The decrease in gross beta activity since the 1960's has been a world wide, and nationally observed trend. In the last several years, the majority of activity found on air parti-culate filters, analyzed for gross activity, is the result of naturally occurring activity in the form of uranium and thorium daughter products. The concentration of the naturally occurring isotopes in the biosphere is based on location and is affected by time related processes such as wind direction and snow cover. The fluxuation of natural background concen-trations and the fact that the People's Republic of China conducted two nuclear atmospheric detonations during 1978 can be considered the major reason for the slight increase in gross beta activity in the 1978 samples at both the off-site and on-site sample locations. Figure VIII-15 is a graph of air particulato gross beta activity from 1974 through 197S.
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- 2. Monthly Particulate Composites - Table 13 On a monthly schedule, air particulate filters are composited by location (off-site /on-site).
Positive activities were detected at both the off-site and on-site sample of the following isotopes: Co-60, 55-54, Co-58, Nb-95, Zr-95, Cs-137, Cc-144, Ba La-140 and I-131. The presence ,f activity in air particulate samples prior to July 1978 are likely the result of in-plant background fluxuations affecti g sample counting equipment. The March sample analysis shows tne presence of I-131 in both the off-site and on-site composites. The concentrations were 2.50 x 10-3 pCi/m 3 for the on-site and 4.60 x 10-3 pCi/m 3 for the off-site sample. The MDL's for I-131 on composite samples ranged from 9.28 x 10-5 to 2.51 x 10-4 pCi/m3 . These I-131 activities can be directly attributed to a nuclear atmospheric test conducted by the People's Republic of China, on March 14, 1978. Using the off-site concentrations on a nuclide basis as control, the Febuary Co-60 activity of 1.53 x 10-2 pCi/m 3 in the on-site composite may be considered of possible significance, using two times the control station value as a screening level. As discussed above, this activity is likely a result of a counting environment background from the plant. Two nuclides were identified in the December composite but were not included in the second half of Table 12. The nuclides were Cc-144 and Ru-103 with concentrations of 2.8 + 1.9 x 10-4 - and 4.5 + 2.4 x 104 pCi/m3 respectively.
- 3. Airborn I-131 - Tables 13 and 14.
The results of the I-131 (charcoal cartridge) analysis for the six off-site and nine on-site monitoring stations are presented in Tables 13 and 14. The March 27-28 sample results showed detectable I-131 con-centrations at 4 of the 6 off-site sample locations and 5 of the 9 on-site sample locations. The off-site activity ranged from 0.03 + 0.01 to 0.04 + 0.01 p'Ci/m3 , while the corresponding on-site sample results rar.ged f rom 0.03 + 0.01 to 0 06 + 0.01 pCi/m3 . The source of the I-131 can be attributed to an atmospheric nuclear test conduct >d by the People's Republic of China, on March 14, 1978. The widespread occurance of detectable I-131, also evident in the monthly air particulate composite results, support the fact that the concentrations of 1-131 were due to the test conducted by the Chinese, and not plant operation. 9 4
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During 1978, three single on-site samples showed detectable IcVels of I-131 activity. The 9/25 sample from the I on-site station showed an I-231 concentration of 0.02 + 0.01 pCi/M .3 The 6/27 sample at the H on-site station showed a detectable concentration of 0.07 + 0.01 pCi/m3 and the G on-site station 3 showed an activity of 0.04 + 0.01 pCi/m on 10/16. The activity reported in these samples is very low in concentra-tion and in each case close to the MDL level of 0.01 to 0.08 pCi/m3 (range). These measurements were recorded in the second half of the year and are not considered to be related to atmospheric fallout. Plant releases during the second half of 1978 were higher than the first and second quarter of 1978. The higher release rates for the second half of 1978 may be correlated to refueling outage maintenance. The concentrations detected during the second half of 1978 were analogous to the levels detected from atmospheric testing recorded earlier in the year. A dose calculated using the maximum detected coacentration of 0.07 pCi/m3 , and based on NRC staff assumptions in Rcgulatory Guide 1.109, would be equal to 0.83 mrem /yr to the thyroid and 0.001 mrem /yr to the whole body. This annual dose calculation is made using an inhalation rate of 8000 m 3/yr for the average adult and a dose factor of 1.49 x 10-3 mrem /pCi inhaled and 2.56 x 10-6 mrem /pCi inhaled for the thyroid and whole body dose respectively. The dose resulting frem the detected I-131 levels calculated above assumes that the level of I-131 con-centration in air remains constant for an entire year. A review of the data table shows that no I-131 concentration was detected for longer than one sample period which would be a maximum time period of 7 days. If the dose calculation is adjusted to reflect the real temporal distribution of the sample results, the dose calculation can be reduced by a factor of 52. The recalculated doses would then be 0.016 mrem /yr to the thyroid and 0.00003 mrem /yr (300 x 10-5 mrem /yr) whole body dose. Although trace amounts of I-131 were detected in 3 samples during 1978, this represents only six tenths of one percent (0.6 %) of the on-site samples collected during the year and only four tenths of one percent (0.4 %) of the total airborne iodine samples collected. It should be noted that minute traces of I-131 have and can be detected by our air monitoring system. A review of the data indicates that radioiodine releases are not routinely detected in the environs of the site as confirmed by the few actual detectable I-131 concentrations recorded during the 1978 operating period.
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- 4. TLD'S (Environmental Dosimetery) - Table 15 TLD results for the first and second quarters are reported as an average of 5 individual LiF chips. The third and fourth quarter TLD's are Ca(SO4 ) (Tm). Each reported value is the average of 4 independent readings (2 readings /TLD - 2 TLD's/
location). This is due to a contractor change starting in April of 1978. The TLD's are broken down into 3 groups for reporting purposes. The groups are on-sites, off-sites, and si - boundary (see sampic summary). The net dose at the site boundary (site boundary average - off-site average) for each quarter were 1, 1, 0, 0, respectively (mrem). The total site boundary dose (mrem) for 1978 was 2. Badges 31, 32, 39, and 40 are located within the NMP-1 fenced area near the Radwaste Building and are being influenced by waste trucks being loaded in the building or parked nearby. Badges 27 through 30 are located within the JAF restricted area and are being affected by waste trucks being loaded in or parked near the JAF Radwaste Building.
- 5. Radiation Monitors - Table 16 Radiation monitors are located in 10 of the 15 air monitoring stations. Each of the on-site air monitoring stations contains a radiation monitor and the C off-site station contains a similar radiation monitor. The radiation monitors consist of a GM detector with an associated power supply, chart recorder and trip unit. The monitor has an operating and recording range of 0.01 to 100 mrem /hr. Each radiation monitor has a small radioactive source mounted on the detector to produce an on-scale reading. The design intent of the monitors is to detect possible dose rates resulting from plume releases from the plant. The radiation monitors are not considered capab :
of detecting minute fluxuations in levels of background radiation. Therefore, no comparison can be made between the radiation monitor reading with those of environmental TLD's. ,
- 6. Milk - Table 17 and 18 Milk samples were collected monthly from each of 5 farms and analy:cd for I-131. Twice per month milk was collected from the same 5 farms. The two monthly samples were composited by location and were analyzed for gamma emitters and Sr-90.
Tables 17 and 18 shows milk sample results for I-131, gamma emitters, and Sr-90 respectively.
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As noted earlier there were two Chinese nuclear tests con-ducted in the atmosphere in 1978. The first test was in mid-March and the second in mid-December. Milk samples were not collected during the period that fallout occurred in the Northeastern United States because cattle were not on open pasture due to snow cover. By the time cattle were on spring pasture feeding any expected I-131 fallout had decayed. Cs-137, a significant nuclear test byproduct would remain abun-dant and detectable for a much longer period of time. Due to the long half life of Cs-137 (30.2 years), the concentration has a tendancy to build up in the environment and thus was detected in every milk sampic (including the control samples) collected during 1978. The concentrations of Cs-137 varied during the 1978 grazing season due primarily to local weather patterns and precipitation trends. Cs-137 levels have shown a decreasing trend since 1976 in the vicinity of the site. Graphic levels of Cs-137 are shown on Figure VIII-16. Iodine IcVels in the 1978 milk samples were at or below the MDL level. One positive radiciodine concentration was de-tected during the year with a positive value of 0.19 + 0.07 pCi/1. This concentration is below the normal FDL 1cvel and - was due to long counting time, resulting in very high sensi-tivity. The dose estimate of a teen drinking 200 liters of milk per year, based on 0.19 pCi/1 of I-131 would be 0.05 mrem /yr based on a six month grazing season. The comparison of 1978 milk I-131 data shows a significant decrease in I-131 levels in milk _ from previous years sampled. It should be noted that previous data is biased by I-131 resulting from the detonation of nuclear devices in the atmosphere, while such results are not part of the 1977 and 1978 data. (See Figure VIII-17) . Sr-90 1cycls detected in 1978 milk samples are a remnant of past atmospheric testing. Detected levels of Sr-90 range from 2.5 pCi/1 to 10.0 pCi/1 and were recorded in both off-site and on-site samples. Past data review (1974-1978) shows a consis-tant level of Sr-90 in the milk samples since 1974. A peak concentration was recorded in the 1976 samples and levels have been on a general decrease to date. Figure VIII-18 represents a graph of Sr-90 levels from 1974 through 1978.
- 7. Milch Animal Census - Table 19 and Figure 5 The number of milch animals located within a ten mile radius of the plant is estimated to be 712 cows and 18 goats for the spring census; which shows a decrease of 223 cows and an increase of 15 goats from the 1977 spring census. The 1978 summer census showed a total of 643 cows and 17 goats which represents a decrease in the number of cows by 259 animals and an increase in the number of goats by 15 over the 1977 summer census.
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------i--immii i ' ' ' ' =
- 8. Iluman Food Products - Table 20 The result of analyses performed on meat, poultry, eggs and food crops are shown on Table 20. Iluman food crop analyses for I-131 resulted in minimum detectable activities ranging from <3 to <10 pCi/kg (wet). All analyses were performed within one half-life.
Sight traces of Cs-137 were found in the meat, poulty, and egg samples as was to be expected. One positive detection of a trace amount of Mn-54 in a pear sample was recorded, which was suspect, due to the high associated counting error. The location was resampled and resulted in no detectable Mn-54.
'\
e
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C. CONCLUSIONS The Radiological Environmental Monitoring Program is conducted each year to determine the radiological impact of the James A. Fit:- Patrick Nuclear Power Plant on the local environment. As demon-strated by the analytical results of the 1978 program, the major radiological impact on the environment was the result of fallout from atmospheric nuclear testing. The 1cvels of natural background and the associated fluxuation in intensity are much more significant in terms of dose to man (normal background in the vicinity of the site is equal to 60 mrem /yr) than radiation levels in the environment associated with the operation of the plant. It is therefore concluded that no appreciable radiological environ-mental impact has resulted from the operation of the James A. Fit: Patrick Nuclear Power Plant.
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D. REFERENCES
- 1. U.S. Nuclear Regulatorf Commission Regulatory Guide 1.109,
" Calculation of Annual Doses to blan from Routine Releases of Reactor Effluent for the Purpose of Evaluating Compliance with 10 CFR Part 50, Appendix I", h! arch 1976.
- 2. U.S. Nuclear Regulatory Commission Regulatory Guide 1.109,
" Calculation of Annual Doses to h!an from Routine Releases of Reactor Effluent for the Purpose of Evaluating Compliance with 10 CFR Part 50, Appendix I", October 1977.
- 3. Eichhol , G. Environmental Aspects of Nuclear Power, First Edition, 1976, Ann Arbor Science Publishers, Inc., Ann Arbor, blichigan.
- 4. National Council on Radiation Protection and htcasurements (NCRP), Environmental Radiation hicasurements, NCRP Report No.
50, 1976.
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e mumm-mm-mm VII. HISTORICALDATA
-136-m--- mmm--m -
VII. SAMPLE STATISTICS FROM PREVIOUS ENVIRONMENTAL SAMPLING The mean, standard deviation, minimum value, maximum value, and range, were calculated for selected sample mediums and isotopes. Special Considerations
- 1) Sample data listed as 1969 was taken from the NINE MILE POINT, PRE-OPERATIONAL SURVEY, 1969 and ENVIR-ONMENTAL MONITORING REPORT FOR NIAGARA MOHAE POWER CORPGRATION NINE MILE P0lNT NUCLEAR STATION, NOVEMBER 1970.
- 2) Sample data listed as 1974 is taken from the NINE MILE POINT NUCLEAR STATION, ENVIRONMENTAL OPERATING RtPORT.
The 1974 data is pre-operational to the James A. Fit: Patrick Nuclear Power Plant, which started commercial operation in November 1974.
- 3) Sample data listed as 1975, 1976, and 1977 is taken from the respective Environmental operating reports for the Nine Mile Point Nuclear Station and James A.
Fit: Patrick Nuclear Power Plant.
- 4) Only measured values were used for statistical calculations.
-137-
BNIROWB1TAL SMPLE STATISTICS PERIPilYTON Cs-137 pC1/g (wet) [*M CONTROL STD.DW. M. V21. ME 1978 0.04 0.03 0.063 0.023 0.04 1977 <xto 1976 5.00 ONLY ONE DATA POINT 1975 oot. _ _ _ _ 1974 0.10 0.02 0.12 0.09 0.30 1969 N0 oATA - _ _ (Pre-Operationai) PERIPilYTON Cs-137 pCi/g (wet) INDICATOR VM SE. DW, VM. f11N. ME 1978 0.11 0.06 0.19 0.05 0.14 1977 0.42 0.56 1.40 0.09 1.31 1976 2.60 1.38 4.10 1.40 2.70 1975 22.25 14.34 36.00 4.00 32.00 1974 5.18 3.73 8.44 1.72 6.72 lggg NO DATA - _ _ _ (Pre-Opera t io nal)
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I BNIRONMENTAL SATLE STATISTICS BOfTOM SEDIMENT Sr-90 pCi/g (dry) jgj gg, gg, [,E FilN. NGE CONTROL 1978 0.05 0.01 0.04 0.061 0.02 1977 0.0s ONLY ONE DATA POINT 1976 < ret - - - - 1975 I
<MDL - - - -
' M" - - - -
19711 I 1969 30 aira _ _ _ _ (Pre-Operational) BOTTOM SEDIMENT Sr-90 pCi/g (dry) INDICATOR MFM1 STI). DEV. FAX. MIN. RANGE 1978 0.015 ONLY ONE , DATA POINT 1977 < >o t - - - - 1976 0.04 0.00 0.04 0.04 0.00 1975 0.29 0.27 0.65 0.03 0.62 I lg7/j <MDL - - - - I 0.08 ONLY ONE DATA POINT (Pre-Operational)
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BNIR0ffEfTAL SAMPLE STATISTICS BOTTOM SEDIMENT FMI ' Cs-137 pCi/g (dry) STD. D W. MAX. Mlil. PANGE CONTROL 1978 0.61 0.15 0.71 0.50 0.21 1977 0.68 0.08 0.73 0.62 0.11 1976 omt. _ _ _ _ 1975 0.40 0.10 0.50 0.30 0.20 1974 0.11 ONLY ONE DATA POINT 1%9 no oira _ _ _ _ (Pre-Operational) BOTTOM SEDIMENT Cs-137 pC1/g (dry) INDICATOR FMI E. DW, PE t<111 ME 1978 0.99 0.80 2.10 0.24 1.86 1977 2.27 1.90 4.10 0.31 3.79 1976 2.45 0.64 2.90 2.00 0.90 1975 0.83 0.86 3.50 0.20 3.30
.4 0.26 0.58 0.21 0.37 1974 lggg 0.38 0.09 0.44 0.31 0.13 (Pre-Operational)
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MOLLUSKS BNIR0tPERAL SN'PLE STATISTICS l Sr-89 pCi/g (wet) fM SID dbl. VAX. MIil. RANGE CONTROL 1978 0.02 ONLY ONE DATA POINT 1977 <MDt - - - - 1976 NO DATA - - - - 1975 NO DATA - - - - I 1974 NO DATA 1969 no oira _ _ _ _ (Pre-Operational) MOLLUSKS Sr-89 pCi/g (wet) INDICATOR VEAN STD. DEV. VAX. MIN. PANGE 1978 0.05 0.03 0.07 , o.03 0.04 1977 <MDt - - - - 1976 0.42 ONLY ONE DATA POINT
<MDL - - - -
1975
#MD' - -
19/4 1%9 NO DATA - - - - (Pre-Operational)
-141-
BNIR0tPERAL SATl.E STATISTICS MOLLUSKS Sr-90, pCi/g (wet) IM STD.DEV. MAX. Mlil. RANGE CONTROL 1978 0.14 0.02 0.15 0.12 0.03 1977 <MDL - - - - 1976 NO DATA - - - - 1975 NO DATA - - - - 1974 NO DATA - - - - bb NO DATA - - - - (Pre-Operational) MOLLUSKS Sr-90, pCi/g(wet) INDICATOR VM STD. DW, VM. MIN. ME 1978 0.14 0.03 0.18 0.10 0.08 1977 0.10 0.02 0.11 0.07 0.04 1976 0.51 ONLY ONE DATA POINT 1975 0.17 0.04 0.19 0.14 0.05 1974 0.32 ONLY ONE DATA POINT 106g 0.12 0.17 0.24 0.01 0.24 (Pre-operational)
-142-
I BNIR0tPBfTAL SMPLE STATISTICS MOLLUSKS I Cs-137, pCi/g (wet) FFR1 STD. DEV. 1%X. Mlil. PNEE CONTROL 1978 <xDL - - - - I 1977 <xDL - - - - 1976 NO DATA - - - - I NO DATA - - - - 1975 1974 NO DATA - - - - I 1%9 NO DATA - - - - (Pre-Operational) MOLLUSKS Cs-137, pCi/g (wet) INDICA M FFR1 STD. DEV. PAX. MIN. RANGE 1978 o 99 0.80 2.10 0.24 1.86 1977 <xDL - - - - 1976 0.18 ONLY ONE DATA POINT 1975 <xDL - - - -
}g74 0.26 ONLY ONE DATA POINT I
1%9 08 ONLY (Pre-Operational) ONE DATA POINT
-113-
BNIR0tPERAL SMPE STATISTICS GA>DIERUS Sr-89, pCi/g (wet) PER1 STD.DEV. PAX. MIN. PR1GE C0!TfROL 1978 < 3gt _ _ _ _ 1977 <MDL - - - - 1976 NO DATA - - - - 1975 NO DATA - - - - 1974 < >m L - - - - 1969 (Pre-Operational) NO DATA - - - _ GA>DIERUS Sr-89, pCi/g (vet) INDICATOR VERI STD.DEV. VAX. MIN. PAEE 1978 < >m t - - - - 1977 <30t _ 1976 NO DATA - - - - NO DATA - - - - 1974 <>m t - - - - 1%9 NO DATA - - (Pre-Ope ra t ional)
~ -
-114-
I EINIR0ttBRAL SWPLE STATISTICS G,UtiERUS l Sr-90, pCi/g (wet) EAN STD.DEV. MAX. MIN. PREE CONTROL 1978 0.14 0.01 0.14 0.13 0.01 1977 0.32 ONtv ONe DATA r01Nr 1976 NO DATA - - - - 1975 No D^T^ - - - - I Jg74 4DL - - - -
~ ~ ~ ~
(Pre- ational) G,VDIERU S ![~!cir0f[""""' D EAN SlD. DEV. MAX. MIN. PNEE g 1978 0.14 0.04 0.21 0.13 0.08 1977 0.40 0.46 0.73 0.08 0.65 1976 NO DATA - - - - 1975 NO DATA - - - - 4S' - - - - I 1974 NO DATA - - - I (Pre-Operational) l
-145-
EINIROWETAL SAMPE STATISTICS Cs-1 pCi/g (wet) CONTROL 1978 0.028 0xty OxE DATA point 1977 <sL - - - - 1976 W DATA - - - - 1975 no n,,13 _ _ _ _ 1974 30 DArA _ _ _ _ 1 1969 NO DATA - - - - (Pre-Operational) GA>DIERU S Cs-137 pCi/g (wet) im CATOR EM STD.DEV. PA'< . MIN. RANGE 1978 e , 0.00 0.05 o.os o.oo 1977 <mL - - - - 1976 E DATA - - - - 1975 W DATA - - - - 1974 0.21 ONLY ONE DATA POINT 1%9 NO DATA - - - - (Pre-Operationa1)
-116-
I suunma ser swisucs F1 Sit SAMPLES p i/g (wet) I Sr-89, CONTROL fH1 STD. DEY. t%X. Mlil. PAIGE lg73 <MDL - - - - 1g77 0.04 0.01 0.05 0.03 0.02 1976 0.24 0.08 0.33 0.19 0.14 I 1975 I
< MDi. - - - -
I 1974 <>mt. - - - - g 1969 NO DATA - - - - (Pre-Operational) FISil SAMPLES I! ATo MEM STD. DEV. f%X. MIN. RANGE g 1g73 0.01 0.001 0.015 0.014 0.001 1g77 0.07 0.05 0.24 0.03 0.21 1976 0.27 0.is 0.41 0.12 0.29
<MDL - - - -
I 1975 I 1974 < 301. - I 1%9 NO DATA - - - - (Pre-operational)
-147-
BNIR0 tie 1TAL SMPLE STATISTICS FISil SAMPLES Sr-90, pCi/g (wet) i STD. DEV. MAX. Mlil. fWiGE CONTROL 0.01 0.004 0.015 0.004 0.01 1977 0.07 0.03 0.14 0.02 0.12 1976 0.25 0.27 0.81 0.05 0.76 19 5 0.07 0.06 0.10 0.04 0.06 0.07 0.02 0.09 0.04 0.05 1%9 so oxrA - - _ _ (Pre-Operational) FISil SAMPLES Sr-90, pCi/g (wet) INDICATOR VMI SE. DW. VM. Miti. EE 1978 0 013 0.006 0.025 0.004 0.021 1977 0.07 0.05 0.24 0.03 0.21 1976 0.28 0.48 2.20 0.05 2.15 1975 0.08 0.03 0.13 0.02 0. u 0.23 0.69 2.30 0.01 0.29 1069 0.23 0.17 0.51 0.30 0.48 (P re-Ope ra t io n.11)
-148-g .___ .
I I BNIPMBITAL S/FPLE STATISTICS g 5$3f"$cE)n(wet) IM STD.DEV. t'AX. Mlil. PAffaE com0t. l 1978 g,g9 g,g30 g,200 g,g;g g ,17, I
. 3 m NE DATA POINT 1977
. 2 OM ONE DATA POINT 1976 1975 <xm. - - - -
I 1974 0.43 0.37 0.94 0.09 0.85 I 1%9 (Pre-Operational) NO DATA - - - - FISil SAMPI.ES
$~O7g'""("")
u MENi STD. EEV. fMX. f11N. PANGE g
<> . a .2 (.300 0. 30 0.07 1978 g
.29 0.21 3. 7 () 0.1 0. %
1977 1.4 .67 3 . <> 0 0.50 3.40 1976 1.38 .22 1.70 1.10 0.60 1975 l 1974 0.57 0.82 4.40 0.08 4.32 0.06 0.04 0.13 0.01 0.12 I
}ggg (Pre-Operational)
-149-
Bt/lR0t0EITAL SMPE STATISTICS LAKE WATER GROSS BETA Pci/1 EAl STD.DEV. PAX. Filil. PA4GE CONTROL 1978 3.55 1.58 6.10 0.50 5.60 1977 10.9 14.5 49.3 2.50 46.8 1976 42.48 50.62 189.00 4.90 184,10 1975 45.33 52.79 160.00 1.00 159.00 1974 4.85 0.07 1 4.90 4.80 0.10 1969 ^ ~ ~ (Pre-Operational)
~ -
LAKE WATER GROSS BETA pC1/1 NDICA M gg) g}g,g{y, ygg, p,jjpg, pggg{ 1978 4 53 2.62 11.10 0.60 10.50 1977 15.80 21.00 87.00 1.00 86.00 1976 41.76 55.23 192.00 1.10 190.90 1975 18.24 17.08 80.00 0.60 79.40 1974 31.71 20.22 60.00 6.30 53.70 1969 NO DATA - _ _ _ (Pre-Operational)
-119a-
I BNIROBEHAL Stl'PE STATISTICS pci/1 STD. DEV, MFAl PRX. Mlil. P/!!GE CONTROL
}g/8 <MDL - - - -
1977 <*' - - - - 1976 <*' - - - - 1975 <xoi, _ - - _ 1974 I NO DATA - - - - 1969 NO DAT' - - - - I (Pre-operational) IAKE WATER Sr-89, pC1/1 INDICATOR f*g'~ fj gg, gg, gy, [.j{[j, pp,\(( I 1978 o 70 0 10 0 80 o.co 0.29 1977 <*' - - - - 1976 <*1 - - - - 1975 0.30 ONLY ONE DATA POINT I 1974 NO DATA - - - - I 1969 NO DATA - - - - I (Pre-Ope ra tional)
-150-
BNIROTEUL SfFPE STATISTICS LAKE WATER Sr-90 pCi/1 IBJ1 STD. DEV. FAX. MI 1. PA'GE CONTROL 1978 0.90 0.10 1.00 0.80 0.20 1977 1.00 ONLY ONE DATA POINT 1976 <st - - - - 1975 <gt _ _ _ _ M0 DATA - yg7q 1b69 NO DATA - - _ _ (Pre-Operational)
~
LAKE WATER Sr-90, pC1/1 INDICATOR FD11 SE.DW. i"AL Iilfl. PM 1978 0.80 0.30 1.10 0.40 0.70 1977 1.00 ONLY ONE DATA POINT 1976 <MDL - - - - 1975 <mL - - - - NO DATA - - - - 1%9 NO DATA - - (Pre-operational)
-151-
I anmum swat swisucs LAKE WATER TRITIU51 FFAI STD. DD/. FM. Mlil. PAIGE co:naot g 1978 303.75 127.51 490.00 215.00 275.00 1977 407.5 97.4 530.0 300.0 230.0 1976 651.7 251.0 929.0 440.0 489.0 I I 1975 362.5 72.8 414.0 311.0 103.0 I 197/1 ogt _ _ _ _ 1969 tio DATA - - - - (Pre-Operational) -cu TRITIUS1 R I nmIcAToR MFM1 STD. DD/. I'M. fllti. PANGE 1978 389.38 119.94 560.00 253.00 307.00 1977 450.0 67.2 530.0 380.0 150.0 I 5 1976 513.0 250.3 889.0 297.0 592.0 1975 334.8 132.5 482.0 124.0 358.0 I yg77 440.0 84.9 500.0 380.0 120.0 I I 1%9 rio DATA - - - - (Pre-Oper.itional)
-152-
EWIR0ffEITAL SfFPLE STATISTICS AIR PARTICULATE GROSS BETA j,*M'l pCi/m STD. B . VM. FW1 M'lGE CONTROL 1978 0.14 0.13 0.66 0.01 0.65 1977 0.126 0.080 0.484 0.001 0.483 1976 0.051 0.031 0.240 0.004 0.236 1975 0.085 0.060 0.294 0.008 0.286 lg7q 0.121 0.104 0.808 0.001 0.807 1959 0.334 0.097 0.540 0.13C 0.410 (Pre-Operational) AIR PARTICULATE GROSS BETA pCi/m3 FEA11 STD. DW, VM, fllti. EtGE INDICATOR 1978 0.10 0.09 0.34 0.01 0.33 1977 0.070 0.034 0.140 0.016 0.124 1976 0.047 0.032 0.191 0.002 0.189 1975 0.067 0.055 0.456 0.001 0.455 lg7q 0.111 0.114 0.855 0.003 0.854 1%9 0 0.090 (Pre-operational) . l 0.520 0.130 0.390
-153-
I eumma smat susucs ENVIRONME!4[AL TLD's: g QUARTERLY READING FOR Tile YEAR, mrem j,M1 STD.DE FE PE PK E g 0FF-SITE g 1973 10.76 1.56 14.00 7.00 7.00 1977 15.63 4.00 24.00 11.00 13.00 1976 15.42 3.51 21.50 9.60 11.90 6.u .95 21.40 13.50 7.90 1975 16.00 6.04 26.70 7.20 19.50 I yg7q I 1969 ALL DATA REPORTED AS <10 (Pre-Operational) ENVIR0!.31 ENTAL TLD's QUARTERLY READINGS FOR THE YEAR, mrem VENI STD. DD/. VAX. [11N. RANGE a SITE - BOUNDRY g 1978 11.15 1.39 14.00 9.00 5.00 1977 14.90 5.13 28.00 10.00 18.00 1976 15.61 3.26 21.50 11.30 10.20 16.52 4.14 24.40 12.20 12.20 I 1975 1g7/4 16.91 6.35 28.30 8.40 19.90 ALL DATA REPORTED AS <10. I 1%9 (Pre-Operational)
-154-
BNIR000B1TAL SATE STATISTICS
~
MILK SAMPLES Sr-90, pCi/t IM STD.DEV. MAX. MIil. RANGE CONTROL 1978 5.88 2.04 9.00 3.00 6.00 1bN NO DATA - - - 1976 N0 0373 _ _ _ 1975 no DATA - - 1974 NO DATA - - - 1969 (Pre-Operationat) NO DATA - - - MILK SAMPLES Sr-90, pC1/1 INDICATOR MEAN STD DEV. MAX. MIN. RANGE 1978 5.93 1.81 10.00 2.50 7.50 6.07 3.50 15.00 2.00 13.JO ygg 7.16 3.41 14.80 1.50 13.30 ygg 6.31 3.11 13.80 2.30 11.50 1975 1974 5.66 2.89 14.00 1.00 13.00 1%9 (Pre-Operational) NO DATA - _ _
-155-
I EINIRO FBITAL SN'PLE STATISTICS I MILK SAMPLES Iodine - 131 pC1/1 j,M1 SE. DB/, PM. Fil:1. ME CONTROL
}g7g <MDL - - - -
}g77 NO DATA - - -
lg76 NO DATA - - - 1975 NO DATA - - I 19711 NO DATA I 1969 NO DATA - - - (Pre-Operational) MILK SAMPLES Iodine - 131 pCi/1 INDICATOR VFRl STD. DD/. PM. fitti. RANGE g lO7Q 0.19 ONLY ONE DATA POINT 1977 0.20 0.14 0.22 -0.40 0.62 1976 3.20 7.81 45.00 0.02 44.98 1975 0.37 0.60 2.99 0.01 2.98 I
}g7/4 1.23 0.44 2.00 0.70 1.30 I
I 1b9 NO DATA - - (Pre-Operational)
-156-
BNIRotPBITAL S/FPLE STATISTICS MEAT Cs-137, pCL/g (wet) FM1 STD.DW. PAX. FilN. PREE 1978 0.021 0.011 0.040 0.013 0.027 1977 <MDL - - - - 1976 <MDL - - - - 1975 o,10 0,00 0,10 0,30 0,00 19711 no oir3 _ _ _ _ 1969 NO DATA - - - - (Pre-Operational) - EGGS Cs-137, pCi/g (wet) MEN 1 STD.DEV. VAX, filtl. P#EE 1978 <MDL - - - - 1977 <MDL - - - - 1976 <MDL - - - - 1975 <MDL- - - - - yg7q NO DATA - - - - 1%9 NO DATA - - - - (Pre-operational)
-157-
I BNIROWBITAL SAPLE STATISTICS HUMAN FOOD CROPS Cs_137 FFAl STD.DEV. MAX. MI:1. P#1GE pCi/g (wet) 1978 0.01 ONLY ONE DATA POINT 1977 <not - - _ _ 1976 < nut - _ _ _ 1975 <m' - - - 1974 0.142 0.09 0.34 0.04 0.30 I
^^ ~ ~ -
(Pre- ational) HUMAN FOOD CROPS Iodine - 131 pCi/g (wet) BFE1 STD.DEV. VAX. MIN. P#!GE 1978 <not _ _ 1977 <nDt - _ _ _ I
'""' ~ - - -
1976 1975 <not- - _ _ _ I 1974 W DATA - - - -
* "^'^ - - - -
1969 (Pre-Operational)
-158-
BNIR0tFB1TAL SfFPLE STATISTICS SOIL SA!IPLES Cs-137, pCi/g (dry) IM STD.DEV. MAX. M!il. RNIGE CONTROL 1978 NO SAMPLES REQUIRED IN 1978 1977 1.17 0.48 2.00 0.70 1.30 1976 NO DATA - - - _ 1975 1.07 0.21 1.30 0.90 0.40 1974 NO DATA - - - - 1969 (Pre-Operational) 0 DATA - - - - SOIL SAMPLES Cs-137, pC1/g (dry) INDICATOR M1 E . DEV. VAX. MIN. RANGE 9 NO SA>1PLES IN 1978 REQUIRED l 19 1.03 0.62 2.00 0.30 1.70 1976 no nari _ _ _ _ NO DATA - - - - 1974 1.03 1.18 2.80 0.40 2.40
}ggg NO DATA - - - -
(Pre-operational)
-159-
I BNIR0tPB1TAL SNPLE STATISTICS g SOIL SAMPLES Sr-90 pCi/g (dry) I'NI bEs bb.
- MIN. RANGE CONTROL 1978 NO SAMPLES REQUIRED IN 1978 1977 0.21 0.07 0.29 0.13 0.16 1976 NO DATA - - - -
I 1975 0 13 o.1o 0.26 0.04 0.22 I 1974 NO DATA - - - - (Pre- ational)
'^ ~ ~ ~ ~
i SOIL SAMPLES I
"" (" ')
![~$ ATE'R MEAN SE. DEV. MAX. MIN. RANGE g 1978 NO SAMPLES REQUIRED, IN 1978 1977 .O.40 0.18 o.6s o.17 0.48
~
1976 NO DATA - - - - I I
}g3 NO DATA - - - -
I 1974 0.27 0.06 o.34 0.23 0.11 I 1969 NO DATA - - - - (Pre-Operational)
-160-
VII1. FIGURESANDMAPS a
-161-
VIII. FIGURES AND MAPS
- 1. DATA GRAPilS This section includes graphic representation of selected sample results.
For Graphic Representation results less than the MDL were considered to be at the MDL Icvel of activity.
- 2. SAMPLE LOCATION Sample locations referenced as numbers on analysis results tables are plotted on maps.
-162-
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-163-
FIGURE 1A i ..- *' 0FF-SITE MONITORING i. ./
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-164-
FIGURE 2
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*-TLD's Letters - Stations
-165-
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d.R.FITZPRTRICK N.P.P-1978 FIGURE B
-- - - - - = C \ l \
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d.R.FITZPRTRICK N.P.P-IB78 FIGURE 7 B__ ER Y ~~ \ - - - - - = CONTROL MERN ( =1NDIGTOR MERN 1 PCl/E (WET) 9 Gi 6-r 3 E
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d.R.FITZPRTRICK N.P.P-1978 FIEURE B
~~
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d.R.FITZPRTRICK N.P.P-1978 FIGURE 9 v g-- ) v
----- = CONTROL 3-~ - ~'
\
=lNDICRTOR MERN MERN 3-~
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1974 197E 197E 1977 1978 aus mas sem amm num amm sem aus sem num men mim amm som - aus num nas mas
JR. FITZPRTRICK N.P.P:lB78 FIGURE 10 4-
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__ b(b --- -- = CONTROL MERN V y _. { Lj =lNDIGTOR MERN
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v g . C - t--
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d.R.FITZPRTRICK N.P.P-1978 FIEURE 11
- - - - - = CONTROL MERN V
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d.R.FITZPRTRICK N.P.P-1978 FIGURE 12 7 v J 5 5. _ 75 -----
= C .\ ~~ 7 _
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d.R.FITZPRTRICK N.P.P-1978 FIGURE 13 B- - 5 5 V] _ E 5 -- - - = C \~7 .
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J.R.FITZPRTRICK N.P.P-1978 FIGURE 14 (5
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JR . F I TZPflTR I CK N . P . P- 1978 FIEURE lE 9] l ~~ ( _ ~~5 - - - - - = CONTROL MERN
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d.R.FITZPRTRICK N.P.P-1978 FIGURE 15 V _( ._ 5 VJ EE ----- = CONTROL MERN
=INDIGTOR MERN 90- -
CE 27
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$ TRKEN PRIOR TD 1978 M
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d.R.FITZPRTRICK N.P.P-1978 FIGURE 17 v VJ
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m
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. NOTE: NO CONTROL SRMPLES TRKEN PRIOR TO 1978 CONTROL M9L
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d.R.FITZPRTRICK N.P.P-1978 FIEURE IB V / F- V ._1 TE __ N J __1 B-- =lNDIGTOR MERN g q __ c 7
, Q PCl/L
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H~~ - CONTRDL MDL NDTE: ND CONTRDL SRMPLES TRKEN PRIDR TD 1978 l l 1 ! ! 1974 197E 1975 1977 1978
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