ML20238A305
| ML20238A305 | |
| Person / Time | |
|---|---|
| Site: | Peach Bottom  |
| Issue date: | 12/31/1977 |
| From: | INTEREX CORP. |
| To: | |
| References | |
| 35, NUDOCS 8708310016 | |
| Download: ML20238A305 (148) | |
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(PEACHBOTT ATOMIC POWER STATION ENVIRDIMDIATION MONITORING PROGRAM January 1, 1977 through December 31, 1977
' REPORT NO. 35 for The Philadelphia Electric Company June 1978 INTEREX CORPORATION 3 Strathmore Road Natick. Mass. 01760 8708310016 771231 PDR ADOCK 05000171 R PDR
PEACil 130TTOM ATOMIC POWER STATION ENVIRONS RADIATION MONITORING PROGRAM January 1, 1977 through December 31, 1977 l
REPORT NO. 35 for The Philadelphia. Electric Company June 1978 INTEREX CORPORATION 3 Nrathmore lined y, N a tic k, M an. 01760
TABLE OF C0fTTENTS Page I. INTRODUCTION 1 II. PROGRAM DESCRIPTION 3 A. Environmental fionitoring Stations 3 and Media Collected B. Sampling and Analysis Program 3 III. PROC E DURES 22 IV. DISCUSSION OF RESULTS 26 A. Air Particulate 26 B. Precipitation 28
. C. Sur f ace Water and Discharge ila ter 29 D. Well k'a ter 30 E. Soil 31 F. Silt 32 C. Fi sh 33
!!. Shellfish 34 I. Vegetation )
J. Milk 36 1: . Rabbits 37 L. External Gamna Radiation 38 Y. SI"15tARY 39
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LIST g _ TABLES 7 m.s l' 11.1) Environmental Monitoring Stations
/ January through December 1977 II.2 Environmental Radiation Monitoring Program Period January through December 1977 11.3 Summary of Analyses performed on Samples Collected January 1, 1977 chrough December 31, 1977
.m III.1 Typical Analytical sensitivities)
IV.l.1 Analytical Data for Air-Particulate Samples Concentration of Gross Beta Radioactivity (pCi/m 3)
Group I - Peach Bottom Site IV.l.2 Analytical Data for Air-Particulate Samples Concentration of Gross Beta Radioactivity (pCi/m )
Group II - Intermediate Distance locations .
IV.I.3 Analytical Data for Air-Particulate Samples Concentration, of Gross Beta Radioactivity (pC1/m3 )
Group III - Distant Locations l
IV.I.4 Monthly Mean Values of Weekly Air-Particulate Samgles Concentrations of Gross Beta Radioactivity (pCi/m )
IV.1.5 Analytical Data for Air-Particulate Samples '
Concentration of Gross Beta Radioactivity (pCi/m )
Comparative FPA Data - Harrisburg, Pa. . .
IV.l.6 Analytical Dnts for Monthly Composite Air-Particulate gamples Camma Spectrum Analysis - Nuclide Concentration (pCi/m )
IV.2.1 Analytical Data for Precipitation Samples Concentration (pCi/1) '
IV.2.2 Analytical thta for Prgeipitation Samples Surf ace Density (pCi/m ) ,
, IV.2.3 Mean Radioactivity Concentration in Precipitation (pCi/1) 1 Mean Radioactivity Surf ace Density in Precipitation (pC1/m )2 .
IV.2.4 Analytical Data for Precipitation Samples Comparative EPA Da ta - Harrisburg, Pa . - N IV.3.1 Analytical Ihta for Surf ace Water Grab Samples .
Concentrations in (pC1/ liter)
IV.3.2 Analytical Data for Discharge Water Grab Samples Concentrations in (pC1/ liter) -
LIST _0JF TABII.S IV.3.3 Analytical Da ta for Surface Wa ter Composite Samples Concentrations in (pCi/ liter)
IV.3.4 1977 Annual Mean Radioactivity Concentration in Surfcce Water IV.3.5 1977 Annual Mean Radioactivity Concentration in Discharge Water IV.3.6 Mean Radioactivity Concentration in Surf ace Water and Discharge Water Samples by Date IV.4.1 Analytical Ihta for Well Water Samples Concentration (pC1/1)
IV.4.2 1977 Annual Mean Radioactivity Concentration in Well Water Mean Radioactivity Concentration in Well Water by Quarter IV.5.1 Analytical Data for Soil Samples Concentration (pC1/g dry)
IV.S.2 1977 Annual. Mean Radioactivity Concentration in Soil (pCi/g dry) 5 Mean Radioactivity Concentration in Soil by Date (pC1/g dry)
IV.6.1 Analytical Data for Silt Samples Concentration (pCi/g dry)
IV.6.2 Analytical Data for Silt Camma Spectrum Analysis IV.6.3 1977 Annual Mean Radioactivity Concentration in Silt IV.7.1 Analytical Data for Fish Samples Concentration (pC1/g ash)
IV.7.2 Analytical Data for Fish Samples Concentration (pC1/g original sample)
IV.7.3 Analytical Data for Fish Camma Spectrum Analysis IV.7.4 Mean Radioactivity Concentration in Shad and White Sucker (pCi/ gram ash)
IV.7.5 Mean Radioactivity Concentration in Shad and White Sucker (pCi/ gram original sample)
IV.7.6 1977 Annual Mean Radioactivity Concentrations in Fish Samples (pC1/ gram ash)
IV.7.7 1977 Annual Mean Radioactivity Concentrations in Fish Samples (pCi/ gram original sample)
IV.8.1 Analytical Data for Shellfish - Sof t Tissue Samples Concentration (pCi/g ash) i
LIST OF, TABLES IV.8.2 Analytical Data for Shellfish - Sof t Tissue Samples Concentration (pCi/ gram original sample)
IV.8.3 Analytical Data for Shellfish - Shell Samples Concentration (pC1/g ash) h IV.8.4 Analytical Data for Shellfish - Shell Samples Concentration (pCi/ gram original sample)
IV.8.5 Analytical Data for Shellfish Samples Camma Spectrum Analysis - Sof t Tissue Concentration (pCi/ gram original sample)
IV.9.1 Analytical Data for Vegetation Samples p
g Concentration (pCi/g ash) l IV.9 2 Analytical Data for Vegetation Samples l
Concentration (pCi/ gram original sample) l IV.9.3 1977 Annual Mean Radioactivity Concentrations in Vegetation f
Concentration (pCi/g ash) L --
IV.9.4 1977 Annual Mean Radioactivity Concentration in Vegetation Concentrations (pCi/ gram original sample) [__
IV.10.1 Analytical Data for Milk Samples Concentration (pCi/1)
IV.10.2 1977 Annual Radioactivity Concentration in Milk Samples (pCi/1)
IV.11.1 Analytical Data for Rabbit Samples Collected from Peach Bottom Site - Station 1 Concentration (pci/g ash)
IV.11.2 Analytical Data for Rabbit Samples Concentrations (pC1/ gram original sample)
IV.11.3 1977 Annual Mean Radioactivity Concentrations in Rabbit Samples Concentration (pC1/g ash)
IV.11.4 1977 Annual Mean Radioactivity Concentration in Rabbit Samples Concentration (pCi/g original sample)
IV.12.1 Gamma Radiation Monitoring Readings (mR/hr)
LIST OF FIGl[R_ES 11.1 Environmental Sampling Stations on or near Peach Bottom Site II.2 Environmental Sampling Stations at Intermediate Distances from Peach Bottom Site II.3 Environmental Sampling Stations at Remote Distances from Peach Bottom Site IV.l.1 Gross Beta Radioactivity in Air Particulate Samples for Group I - Stations IA, iB and 2 and Group III - Stations 12A and 12D IV.I.2 Gross Beta Radioactivity in Air Particulate Samples for Group II - Stations 3A, 4A, 4B, 5, 6B, 14, 15, 17, 31, 32, 33A and 38 and Group III - Stations 12A and 12D IV.l.3 Gross Beta Radioactivity in Air Particulate Samples for Group I - Stations 1A, 1B and 2 and Harrisburg, Pa.
I V. l . 4 Gross Beta Radioactivity in Air Particulate Sampleo for Group II - Stations 3A, 4A, 4B, 5, 6B, 14, 15, 17, l 31, 32, 33A and 38 and Harrisburg, Pa.
l IV.I.5 Cross Beta Radioactivity in Air Particulate Samples for Group III - Stations 12A and 12D and Harrisburg, Pa.
l IV.2.1 Monthly Mean Concentration of Gross Beta Radioactivity in Precipitation Samples IV.2.2 Monthly Mean Surface Density of Gross Beta Radioactivity in Precipitation Samples IV.2.3 Annual Mean Concentration of Gross Beta Radioactivity in Precipitation Samples IV.2.4 Annual Fkan Surf ace Density of Gross Beta Radioactivity in Precipitation Samples IV.2.5 Surf ace Density of Sr-90 in Precipitation Samples IV.2.6 Surf ace Density of Cs-137 in Precipitation Samples IV.3.1 Monthly Mean Concentration of Gross Beta Radioactivity in Unit 1 Intake and Discharge Water Samples -
Soluble Fraction
LIST Ol[ FIGURES IV.3.2 Monthly Mean Concentration of Gross Beta Radioactivity in Unit 1 Intake and Discharge Water Samples -
Insoluble Fraction q IV.3 3 Monthly Mean Concentration of Gross Beta Radioactivity i
in Units 2 and 3 Int.ahe and Discharge Water Samples-Soluble Fraction IV.3.4 Monthly Mean Concentration of Cross Beta Radioactivity in Units 2 and 3 Intake and Discharge Water Samples-Insoluble Fraction IV.3.5 Monthly Mean Concentration of Cross Beta Radioactivity in Surf ace Water Samples - Foluble Fractiote IV.3 6 Monthly Mean Concentration of Cross Beta Radioactivity in Surface Water Samples - Insoluble Fraction IV.3.7 Monthly Mean Concentration of Cross Beta Radioactivity in Composite Surface Water Samples - Conowingo Dam Station 4L and Holtwood Dam Station 61 - Soluble Fraction IV.3.8 Monthly Mean Concentration of Gross Beta Radioactivity in Composite Surface Water Samples - Conowingo Dam Station 4L and Holtwood Dam Station 61 - Insoluble Fraction IV.3.9 Annual Mean Concentration of Gross Beta Radioactivity in Surf ace Water Samples - Soluble Fraction IV.3.10 Annual Mean concentration of Gross Beta Radioactivity in Surface Water Samples - Insoluble Fraction IV.5.1 Quarterly Mean Gross Alpha Concentration in Soil Samples IV.5.2 Quarterly Net Beta Concentration in Soil Samples IV.5.3 Semi-Annual Mean Sr-90 Concentration in Soil Samples IV.5.4 Semi-Annual Mean Sr-89 Concentration in Soil Samples IV.S.5 Semi-Annual Mean Cs-137 Concentration in Soil Samples IV.6.1 Semi-Annual Sr-90 Radioactivity Concentration in Silt Samples IV.6.2 Semi-Annual Cs-137 Radioactivity Concentration in Silt Samples
1,IST OF, FIGURES l
IV.6.3 Sr-90 Radioactivity Concentration in Silt Samples i IV.6.4 Semi-Annual Cs-137 Radioactivity Concentration in Silt Samples l
IV.7.1 Quarterly Mean concentration of Sr-90 Radioactivity
, in Fish Samples IV.7.2 Quarterly Mean Concentration of Cs-137 Radioactivity in Fish Samples IV.7.3 Quarterly Mean Concentration of Sr-90 Radioactivity in Fish Samples IV.7.4 Quarterly Mean Concentration of Cs-137 Radioactivity in Fish Samples IV.8.1 Concentration of Net Beta Radioactivity in Shellfish Tissue Samples IV.8.2 Semi-Annual Concentration of Sr-90 Radioactivity in Shellfish Shell Samples IV.9.1 Annual Mean Concentration of Sr-90 Radioactivity in Vegetation Samples IV.9.2 Annual Mean Concentration of Cs-137 Radioactivity in Vegetation Samples IV.10.1 Mean Concentration of Sr-90 Radioactivity in Milk Samples IV.10.2 Mean Concentration of Cs-137 Radioactivity in Milk Samples IV.10.3 Mean Concentration of I-131 Radioactivity in Milk Samples IV.11.1 Semi-Annual Mean Concentration of Net Beta Radioactivity in Rabbit Muscle Samples IV.11.2 Semi-Annual Mean Concentration of Sr-90 Radioactivity in Rabbit Bone Samples
I. INTRODUCTION l
L A pre-operational environmental radioactivity survey, initiated in March 1960, was conducted by Nuclear Science & Engineering Corporation for the
, Philadelphia Electric Company in connection with Peach Bottom Atomic Power Station located in Peach Bottom Township, York County, Pennsylvania. The initial loading of fuel into Unit 1, a 40 MWe (net) high temperature, gas-cooled reactor, was started on February 5,1966, and initial criticality was achieved on Ma rch 3, 1966. Shutdown of Pe ach Bottom Unit I for decommissioning was on October 31, 1974. For the purposes of this monitoring program, the beginning of the operational period for Unit 1 is February 5, 1966. A summary of the Unit 1 pre-operational monitoring program is presented in a previous report. (1)
Peach Bottom Units 2 and 3 are boiling water reactors each with a power output of 1050 MWe (net) . First fuel was loaded into Peach Bottom Unit 2 on August 9, 1973, criticality was achieved on September 16, 1973, and full power was first reached on June 16, 1974. The first fuel was leaded into Peach Bottom Unit 3 on July 5,1974, criticality was achieved on August 7,1974, and full power was first reached on December 21, 1974. A pre-operational summary report (2) for Units 2 and 3 has been issued previously and summarize s the results of all analyses performed on samples collected from February 5, 1966 through August 8, 1973. De tailed program description, station designations, reporting units, abbreviations, etc., are given in that report reflecting the program status at that time. Where changes had been made from the original program, they are indicated in the appropriate sections of that report. In general, any such changes have been made to increase the scope and specificity of the program to fulfill the program objective.
In 1967, site preparation for Units 2 and 3 at the Peach Bottom site was und e r t ake n. This has resulted in certain physical changes which required moving some of the original sampling stations. Also, beginning in 1971, several sampling stations of significance to Units 2 and 3 were added to the program. In 1973, some additions and changes were made in the analytical requirements to reflect the latest recommendatier.s of various government agencies. These changes are detailed in a previous report (2).
Ttt1 1s_ report summarized the results of analyses performed by Interex on samp1ea e011ected dur aug7he_ perlod January _l~Stough December _.3I~, .1Yl{f nl_the "
Int-erex porri5iGf tli6'overall Peach Bottom program.
The responsibility for pe r fo rmanc e_ of the environmental radiation monitoring program has been modified several times since the Peach Bottom Unit 1 pre-operational program was first undertaken in 1960. From the start of the program until the first quarter of 1969, a single laboratory located in Pi t t sb ur gh , Pa . , wa s used . This was initially called Nuclear Science and Engineering Co rpo ra tion and later b ecame Nuclear Sciente Division, International Chemical and Nuclear Corporation as the result of a change of ownership. During the first quarter of 1969, the program was transferred to ICN/Tracerlab, also part of Interni .onal Chemical and Nuclear Corporation and was pe r fo rmed by ICN in the Walt:am, Mass., laboratory until the end of the first quarter of 1972. At this time the program was transferred to Interex
I. INTRODUCTION Page 2 Co rpo ra tion laboratories in Waltham. The Interex Corporation laboratory, which is presently carrying out sample collection, analysis and report pr epa ra tion, was moved to Natick, Mass. in May 1974. During the various change-overs and moves, extreme care was taken to insure that continuity in all aspects of the overall program was maintained. For example, samples were collected by the same individual throughout the entire period.
The objective of this program is to acquire quantitative d a ta fo r the concentrations of radioactivity in environmental media in the vicinity of the reactor site prior to and during operation of the reactor plant. These data are then examined to determine the extent of the impact of the plant or plants on the environment as reflected by any changes in the radioactivity levels from those observed during the pre-operational survey. Generally, this is done by comparing the observed levels at those sampling stations which would be expect ed from various considerations to show mam'. mum ef fects of plant operation to levels at stations remote from the aste. When possible, comparison is also made to data obtained by various government agencies.
Since there are both natural and man-made radioactivity present in the environment which are not related to plant operation, it is important to understand and adequately measure these contributions.
A number of radioactive elements occur in nature. The most important of these are uranium and thorium, along with their respective radioactive decay products, and potassium-40 ( K-4 0) . The concentrations of natural radioactivity vary with geographical location and with time and are primarily dependent on the concentration of the respective elements in the constituents of the lithosphere. Therefore, environmental radioactivity measurements must be pe rfo rmed at a number of l ocations representative of the general geographical area of interest.
Other radionuclides have been introduced into the biosphere as a result of the detonation of n uclear d evice s in the atmosphere. A significant fraction of these nuclides is generally disseminated throughout the upper atmosphere with the fine particulate debris from the detonation. Varying fractions of the nuclear debris eventually are deposited at g rotmd level, principally in conj unction with precipitation. After their arrival at ground level, the radionuclides enter soil or bodies of water, and varying f rac tions may enter drinking water supplies or be assimilated by edible plants or animals and thus enter the human food chcin. Na tural radioac tivities are also introduced into the human diet by analogous ecological processes.
The deposition patterns of nuclear debris depend on many factors, including latitude, p roximity to detonation sites, ant.ual accumulation of precipitation, and the frequency, magnitude, location, and altitude of the detonations. In the absence of detonations, seasonal variations have been noted for several years, including maximum deposition rates 17 the spring and summer months and minimum rates in the late fall or early winter. Di stinc t variations have also been noted in individual precipitations. These latter variations have been attributed to variations of meteorological conditions prevailing during the respective precipitation events.
Since significant geographical and temporal variations are expected in the concentrations of both natural and man-made radioactivity in environmental media, it is necessary to acquire experimental values for their concentrations
I. INTRO WCTION Page 3 over a period of several years to achieve statistically-significant data.
Such an approach also provides data for seasonal or annual trends in the t empo r al behavior of these concentrations and permits correlations of these trends with meteorological or climatological factors or with known injections of man-made radionuclides into the atmosphere.
II. PROGRAM DESCRIPTION
)
The program as it existed at the end of the report period is desc ribed below. Since its inception, several changes have been made which expanded the program to better accomplish the program goals.
A. Environmental Monitoring Stations and Media Collected The environmental monitoring stations are described in Table 11.1 and are shown in Figures II.1 through II.3. In general, stations have not been moved significantly since the start of the program.
B. Sampling and Analysis Program The types of analyses performed,the frequency of sampling and analysis, the locations of samples, and the number of samples per station scheduled for each location as of the end of the report period, are given in Table II.2.
A summary of the analyses perfo rmed on samples representing January 1.1977 through December 31,1977 is given in Table II.3.
The program was not changed during 1977.
It was not possible to obtain all of the scheduled samples in 1977. Only one set of shellfish samples was taken during the year. The Chesapeake Bay Institute which normally does this sampling did not have a boat in the area during the quarters in which no samples were obtained. In some cases samples were not obtained due to equipment malfunction or availability of the sampl e medium. The reasons for the missing samples are noted on the respective data tables. The samples that were not obtainable amounted to a small fraction of the overall program and do not affect any interpretation of the data.
An extra set of milk sampics was taken in June at four farms for I-13:
a n al ys is because the samples collected in May were delayed in shipment resulting in an unacceptable decay time for I-131 C. Program changes f or 1978 A number of program changes were made starting with samples taken in 1978. These changes are based on the analysis of previous data, dif ferences in environmental conditions f rom when the program was first designed and other considerations g iv en b el ow. They do not reduce the ef festiveness of the program in monitoring the environment for radionuclides from PBAPS.
Sampling and analysis of shellfish was discontinued. Shellfish have been s am p.l ed from Chesapeake Bay since 1960 as part of the Peach Bottom Unit I moni toring program. The sampling locations are from 40 to 50 miles downstream
II. PROGRAM DESCRIPTION Page 4 of Peach Bottom and are now potentially affected by another nuclear power facility. They are poor indicators of Peach Bottom releases. The Appendix 1 dose model described in the USNRC Regulatory Guide 1.109 model indicates that the fish pathway is a more sensitive dose pathway to man for Peach Bottom releases, assuming that fish and shellfish are at the same location. Since fish are extensively monitored in Conowingo Pond, there is no technical reason for maintaining shellfish analyses.
The sampling and analysis of fish from Peters and Pequea Creeks has been te rminated . At the recommendation of the U.S. Fish and Wildlife Service the US AEC requested that fish be monitored in the tributaries to Holtwood and Conowingo Ponds. Philadelphia Electric Company stated that sampling in the tributary creeks would be implemented, and if af ter three years of operation of Peach Bottom Unite 2 and 3 no significant effects were detected, the sampling would be discontinued. The data collected through 1977 indicate no positive Peach Bottom effect on fish radioactivity concentrations at these locations. This is to be expected aince the hydraulic flow pattern from the creeks to the ponds would prevent this.
Surface water Station IP and discharge water Station 1R are no longer sampled. No further releases are possible from Unit 1 because it has been de c omissio ned . The liquid radwaste discharge pipe has been rem oved .
Therefore, there is no need to monitor the intake and discharge of Unit 1.
Well water from Station 8 is no longer sampled. Regula to ry Guide 4.8 re c ommend s g:ound water be sampled at the most likely sources. The Branch Technical Position (5) recommends ground water sampling only if sources are likely to be af fected. At Peach Bottom no wells are likely to be af fected due to the nature of ground wa ter flow. Ho wev e r , ground wa ter sampling has continued because of the presence of the visitor center in proximity to the plant. Since on-site sampling has continued, a distant well is desirable for comparison. Stations 7 and 8 are essentially equivalent for background purpose. However, Station 8 has an accesa problem, so it was selected as the location to be discontinued.
Cross alpha analysis of fish and vegetation was discontinued since it is of no value for monitoring the environmental ef fects of PBAPS. There are no significant concentrations of alpha emitters in Peach Bottom's releases.
Therefore, gross alpha analyses are measuring the concentration of naturally occurring and weapons fallout alpha emitters in the m ed ia . No applicable guidelines recommend these gross alpha analyses.
Sampling of surf ace and discharge water at Un it s 2 and 3 intake and discharge canal exit is being done by continuous composite samples in addition to monthly grab samples. The first samples were obtained for the period beginning February 4, 1978. Such sampling is recommended in Regulatory Guide 4.8 and other applicable litere.ture, and has been instituted to increase the representativeness of the samples collected.
Cesium isotopes in milk samples are being measured by using Ge ll spe c trome tr y on the radiochemically separated cesium fraction. The previous procedure (low level beta counting) cannot differentiate b etwe en Cs-137 and Cs-134. Therefore, all cesium activity measured has been assumed to be Cs-137 which is present in the environment from atmospheric nuc lear testing. Both
II. PROGRAM DESCRIPTION Page 5 .
Cs-134 and Cs-137 are produced in nuclear reactors while only Co-137 is l l produced by fission. Since cesium is routinely measurable in milk, it is
) important to determine what fraction of it, if any, is Cs-134 if one is to determine if there is any Peach Bottom ef fect. I l
Page 6 TAB 12 II.]
ENVIRONMENTAL MONITORING STATIONS January through December 1977 Station Station location, Direction and Environmental No. Station Name Distance from Peach Bottom Site Media Collected 1 Peach Bottom located in Site Area Vegetation, Small Game Site Area lA Peach Bottom - On Site at Weather Station 1, Ambient Radiation, Weather Station 1 0.1 Miles ESE of Unit 1 Air Particulate, Precipitation IB Peach Bottom - On Site at Weather Station 2, Ambient Radiation, Weather Station 2 0.6 miles NNW of Unit 1 Air Particulate, Precipitation IM Peach Bottom - On Site at Canal Discharge D1scharge Water Canal Discharge 0.9 miles SE of Unit 1 IP Peach Bottom - On Site at Unit 1 Intake, Surface Water Unit 1 Intake 1350' ENE of Unit 1 IQ Peach Bottom Unit 2 On Site at Unit 2 Intake, Surface Water
, Intake 1500' NNE of Unit 1 1R Peach Bottom Unit 1 Unit i Screen Well from Discharge Water Discharge which discharge pipe exits, about 350' ENE of Unit 1 IT Peach Bottom Dis- On Site in the Station Dis- Discharge Water (1) charge Canal - charge Canni, 0.4 miles SE 2200' of Unit 1, 2200' from Unit 1 Intake and upflow f rom the Units 2 and 3 rad-waste discharge IU Peach Bottom Site - Well at Plant Site, 450' SW Well Water Utility Building of Unit 1 IV Peach Bottom Site - Well at Plant Site, 450' SE Well Water Information Center of Unit 1 I
~ ~ - - - ' TABLE 11.1 P e /
Station Station location, Direction and Environmental No. Station Name Distance from Peach Bottom Site Media Collected IX Peach Bottom Site - About 1100' ENE of Unit 1 Silt and Fish (2)
Cooling Tower Pond (Channel Catfish l B-1 and White Crappie)
I 1AA Peach Bottom - Located ebout 1400' SE of Soil t
Di scharge Canal Bank Unit 1 on the Discharge Canal Bank 1BB Peach Bottom - On Site in the Station Silt (1)
Discharge Canal Discharge Canal, 2250' SE of Unit I LEE Peach Bottom - In the Discharge Canal anywhere Fish (Channel Catfish Discharge Canal between the Peach Bottom Unit and White Crappie) 2 and 3 Liquid Radwaste Dis-charge and Canal Exit (between 2200 and 4600' SE of Unit 1) 2 Peach Bottom Site - On Site, 0.7 miles SE of Air Particulate 130 Sector Hill Unit 1 Soil 3A De l t a , Pa . - 3.6 miles SW of Unit 1 Air Particulate, substation 0.5 miles N of Maryland Vegetation, Soil border 4A Conowingo Dam - 8.4 miles SE of Unit 1 Air Particulate Powerhouse Roof on Powerhouse roof in Cecil County, Md.
4R Conowingo Dam - 8.4 miles SE of Unit 1 Air Particulate Powerhouse Roof on Powerhouse roof in Cecil County, Md.
4C Conowingo Pond, 1,000' downstream f rom Silt Pa. the Peach Bottom Station Discharge 4D Conowingo Pond, 500' downstream from the Silt Pa . Peach Bottom Station Discharge 4F Conowingo Dam - In the conowingo Hydro-Elec- Surface Water El . 33' MSL Grab tric Station about 8.4 miles SE of Unit 1. Water is sampled from a header which continuously draws pond water from about elevation 33' MS L.
TABIE ,II.1 Page 8 Station Station location, Direction and Environmental No. Station Name Distance from Peach Bottom Site Media Collected 4H Conowingo Dam - Tailrace on west side of Fish (American Shad)
Tailrac e river 8.5 miles SE of Unit 1 4I Conowingo Pond - Located in Conowingo Pond Fish (Channel Catfish Net Trap 8 about 1450' E of Unit 1 and White Crappie) 4J Conowingo Pond - Located in Conowingo Pond Fish (Channel Catfish Net Trap 15 about 6400' SE of Unit 1 and White Crappie) 4L Conowingo Dam - Continuous sampler in the Surface Water El. 33 (Ft.) Conowingo Hydro-Electric Composite Station, about 8.4 miles SE of Unit 1. Water is continuously sampled from a header which draws pond water from about elevation 33' MSL.
4M Conowingo Dam - West bank downstream of Precipitation Downs tre am Conowingo Hydro-Electric El. 40 (Ft.) MSL Station 8.5 miles SE of Unit 1 4N Conowingo Dam - Environmental Monitoring Sta- Vegetation, Soil Environmental tion on west shore upstream Station of Conowingo Hydro-Electric Station about 8.4 miles SE of Unit 1 4T Conowingo Pond - Near middle of Conowingo Pord, Silt Near conowingo Dam about 8 miles SE of Unit 1 5 Wakefield, Pa. 4.5 miles E of Unit 1 Air Particulate, Soil and Vegetation 6A Holtwood Dam - 5.9 miles NW of Unit 1 Surface Water Hydro-Electric (through Hydro Station Plant) 6B Holtvood Dam - 5.9 miles NW of Unit 1 Air Particulate Hyd ro-Elec t ric (Hydro Powerhouse Station Roof) 6D Holtwood, Pa. 6.0 miles NW of Unit i Vegetation near Holtwood Dam in Lancaster County
TAB LE_ II.1 Page 9 Station Station location, Direction and Environmental No. Station Name Distance from Peach Bottom Site Media Collected 6F Holtwood Dam - 5 9 miles NW of Unit 1 Silt (above dam)
Ea s t Shore Upstream in 14ncaster County l
)
6G Holtwood, Pa. 6.0 miles NW of Unit 1 Soil near Holtwood Dam in lancaster County 6H Holtwood Pond - Incated in Holtwood Pond about Fish 6.6 miles NW of Unit 1 61 Holtwood Dam - Continuous sampler at Holtwood Surface Water Hydro-Electric Hydro-Electric Station intake Station - composite about 5.9 miles NW of Unit 1.
Water is continuously sampled and collected in a 175 gallon tank.
6J Holtwood Pond - Incated in Holtwood Pond Fish near the east bank about 10.7 miles NNW of Unit 1 7 Darlington, 9 4 miles SSE of Unit 1 Well Water Maryland Area in Hartford County 8 Colora, 9 9 miles ESE of Unit 1 Well Water Ma ryland in Cecil County Vegetation 9 Tolchester, 38 miles south of Unit 1 Shellfish Ma ryland on the east side of the (Oysters)
Chesapeake Bay 10 Hacke tts Point. 56 miles S of Unit 1 on Shellfish Ma ryland the west side of the (Oysters)
Chesapeake Bay 11 Swan Point Bar, 44 miles S of Unit 1 on Shellfish Maryland the east side of the (Oysters)
Chesapeake Bay 12A Philadelphia, Pa. 63 miles ENE of Unit 1 on Air Particulate 900 Sansom St. the roof of 900 Sansom Street 12D Philadelphia, Pa. 62 miles ENE of Unit 1 on Air Particulate 2301 Ma rke t St . the roof of 2301 Market Street
TABLE 11.1 Page 10 Station Station location, Direction and Environmental No. Station Name Distance from Peach _ Bottom Site Media Collected 13A Chester Water On the east shore of Conowingo Surface Water Intake Pond Pond at Chester Water Authority l Intake, 2.8 miles SE of Unit 1 13B Chester Water Intake At Chester Water Authority Surface Water Pump Discharge intake 2.8 miles SE of Unit 1 14 Peters Creek 2.3 miles E of Unit 1 Air Particulate 15 Silver Spring Road 3.8 miles N of Unit 1 Air Particulate 17 Riverview Road 4.4 miles ESE.of Unit 1 Air Particulate 23 Peach Bottom Of f-site, hill 0 9 miles Vegetation 150*[8o[9 Sector Hill SSE of Unit 1 25A Pequea Creek In Pequea Creek,10.8 miles Fish (White Sucker)
NNW of Unit I near PP&L recreational aren 25B Pequea Creek In Pequea Creek, 12.4 miles Fish (White Sucker)
N of Unit I near Creek and School Roads 25C Pequea Creek In Pequea Creek, 12.2 miles Fish (White Sucker)
N of Unit I nest Byerland Church Road 25D Pequea Creek In Pequea Creek, 13.3 miles Fish (White Sucker)
N of Unit I near Radcliff Rd.
25E Pequea Creek In Pequea Creek, 10.5 miles Fish (White Sucker)
NNW of Unit 1 30A Peters Creek In Peters Creek, 2.7 miles Fish (White Sucker)
ENE of Unit 1 30B Peters Creek In Peters Creek about 2.2 miles Fish (White Sucker)
ENE of Unit 1 30C Peters Creek In Peters Creek about 2.5 miles Fish (White Sucker)
ENE of Unit 1
TABLE I1.1 Page 11 Station Station location, Direction and Environmental No. Station Name Distance from Peach Bottom Site Media Collected 31 Pilot town Road 4.8 miles SE of Unit 1 Air Particulate near Pilottown Road 32 Slate Hill Road 2.8 miles NE of Unit 1 Air Particulate near Slate Hill Road
! 33A Fulton Weather Fulton Main Weather Station Air Particulate Station 1.8 miles ENE of Unit 1 38 Peach Bottom Road 2.9 miles E of Unit I near Air Particulate Peach Bottom Road 40 Peach Bottom Site Well in Site Area about Well Water 1.2 miles SW of Unit 1 Peach Bottom Nearby Regional Farms sur- Milk Regional Farms rounding the Peach Bottom site on tha west side of Conowingo Pond are de.signated G, H, and J. Intermediate distance farms on the east side of the pond are desig-nated D, L, M, and N.
Distant regional f arms on the west side of Conowingo Pond are designated A, B, and C, and a distant farm on the east side is desig-nated Farm E. (3)
- 1. These stations were exposed to Unit I discharge water after 12/6/72. Prior to this date only surface water was present.
- 2. These stations were exposed to Unit I discharge water until 12/6/72.
- 3. The precise farms involved in the program have changed in some cases due to circumstances beyond control of the program, The replacement farms are in the same general locations distributed so as to encircle the site close to and further away from the Peach Bottom site.
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Page 26 IV. DISCUSSION OJ[ RESULTS The results obtained from the program are presented in the data tables and figures following this section and are discussed below according to sample type. In this report, results of analyses which are perfo rmed on ashed samples are repo rted in units of pCi/g original sample in addition to pCi/g ash. This is done to enable one to more easily estimate doses to man by re po rting concentrations of radioactivity in food products, as determined by the radiation monitoring program, in terms of the sample state which is eaten by man. The results repo rted in these units, howeve r , offer poorer comparisons of data because biological variables, such as wa ter content, grectly affect the results. Results reported ap . radioactivity concentrations in terms of the ashed weights eliminate these variables and put the data on a more uniform basis for comparison. For this reason, the graphs in this report which are intended to show comparisons of conc en trations of radioactivity be twe en locations and time periods illustrate data reported in terms of the s ashed weight, not the original sample weight.
All results are given wi th an error corresponding to two standard dev ia tio ns in the net count rate except for K-40 which is generally 10% when significantly above the detection limit. Results which are less than the cal cula ted error are reported as less than (<) the value corresponding to the error.
l l In calculating averages, results reported as "less than" a value are included as that vnlue. The average of a series of numbers which contains at least one real number is given as a real number. If all of the numbers in a series to be averaged are "less than" numbers, the average value is given as a "less than" value. The deviation listed with means is equal to two standard deviations of the data comprising the mean.
In the discussion of data , general trends in the data are stressed as are compa risons of results from stations which would most likely be affected by Peach Bottom Atomic Power Station (PBAPS) operation, with data from those which are more remote from the site. Because of the presence of generally lower 1cvels of radioactivity in the environment compared to earlier periods of maj or atmospheric nuclear testing, precise trends tend to become obscured in the normal variability of data.
Some of the data reflect the continued deposition of fallout from a test by the Peoples Republic of China in September, 1976. This is most readily seen in air particulate and precipitation samples. Another atmospheric test also by the Peoples Republic of China on September 17, 1977 was seen in samples ta ke n from PBAPS environs about two weeks later. While the rad io nuc lid e c onc en tra tions we re less than found af ter the 1976 test, their presence was definitely detectable by using the techniques normally used in the PB APS program.
A. AIR PARTICULATE l The values of the concentrations of gross beta radioactivity observed in air pa r t ic ula t e samples are listed in Tables IV.1.1 through IV.1.4 and are
IV. DISCUSSION Oj[ RESULTS Page 27 presented graphically in Figures IV.1.1 through IV.I.S. Comparative available EPA data are given in Table IV.l.5. Camma spectral analyses are given in Tables IV.I.6 and IV.1.7.
For comparative purposes, stations have been divided into three groups.
Group I, which is on the Peach Bottom site and closest to the plant release points, consists of Stations 1A, 1B, and 2. Group II rings the site at further distances and consists of Stations 3A, 4A, 4B, 5, 6B, 14, 15, 17, 31, 32, 33A, and 38. Group III, which is in Philadelphia, Pennsylvania serves as a reference group and consists of Stations 12A and 12D.
Cross beta radioactivity concentrations exhibited the trend typical of those seen prior to 1976 1.e. there was an increase in concentration through late May or early June and then a gradual decline for the rest of the year, interrupted in late September and October by the arrival of debris from tge September 1977 test. The late spring maximum was about 0.4 - 0.5 pCi/m ,
approximately an order of magnitude higher than the 1976 samples taken before October of that year.
The September 17, 1977 tegt caused values at all stations to increase generally to about 0.8 pC1/m for 5he period ending October 1. A few values were measured somewhat above 1 pCi/m . By early November the concentrations a p pe a red to be down to pre-test levels and generally declined gradually for the rest of the year.
As can be seen from Figures IV. l.1 and IV.l.2, there was no significant dif ference b etwe en the values obtained for the three groups of stations indicating no ef fects due to PBAPS operations.
For comparison, data from the Environmental Protection Agency (EPA) (4) are presented in Table IV.1 5 and shown on the long term plots in Figures IV. l . 3, IV. l . 4, and IV. l . 5. The values observed in the Peach Bottom program are somewh a t higher than those seen at the EPA station in Harrisburg, Pennsylvania. The dif ference in results is apparently due to differences in laboratory techniques and is not attributable to PBAPS operation because it exists for all three groups. The EPA data also exhibit the same trend as the PBAPS data. The EPA values listed in Table IV.1.5 are based on laboratory measurements in contrast to the less sensitive field estimates available for some periods before 1974.
Figurce IV.I.3 through IV.1.5 show comparable trends and values over the period 1966-1977 for all three groups of stations even though the composition of the groups has been changed by adding more sampling stations. This would indicate that the distribution of activity over the entire area is relatively unifo rm and is not af fec ted by PB APS.
Camma spectrum measurements are made on monthly c ompo site samples from each station. These samples generally consist of all weekly samples for the month from the given station taken together. Results of these analyses are ;
g iv en in Tabler, IV.1.6 and IV.I.7. Other than Zr-95 and Nb-95 from nuclear I test fallout and naturally-occurring Be-7 and K-40 no nuclides were detected by Na I gamma spectrometry. The observed values tended to follow the same trend as was found for gross beta radioactivity concentrations. Ikasurable values were similar at all locations.
IV. DISCUSS 10N OF RESULTS Page 28 No contribution from the operation of PBAPS is indicated.
B. PRECIPITATION The concentrations and surface densities of gross beta, Sr-89, Sr-90, and Cs-137 radioactivity in precipitation samples collected at Stations IA, 1B, and 4M are presented in Tables IV.2.1, IV.2.2, and IV.2.3 and plotted in Figures IV.2.1 through IV.2.6. Results from the EPA station in Harrisburg are given in Table IV.2.4 and are plotted in Figures IV.2.1 and IV.2.2.
Most of the radioactivity in precipitation samples is in the fo rm of pa rt icula tes which are washed out of the air by rainfall and collected in the sample containers. Since most of the particulate material is waghed out in the initial part of a rainfall, the surface density, i.e., pC1/m , is imed in addition to concentration (pC1/1), because it tends to minimized the effect of sample volume. Lack of complete correlation with air particulate values comes about because rainfall generally does not occur at frequent intervals. The depe nd ence of the activity levels on the precise conditions occurring at the start of each rainfall can cause wide variability between samples even when taken over limited geographical areas.
The values for gross beta radioactivity monthly concentrations observed in samples collected at Stations 1A and IB show an increase reaching maxima during the summer at values of several tens of a pCi/1. The gurface densities values were generally a few hundred to a few thousand pCi/m . There did not appear to be any discernable difference between l ocations. The values ob se rv ed were similar to those seen in earlier years and are in the range of preoperational data.
The values of monthly gross beta radioactivity concentrations observed in the precipitation samples collected at Station 4M are similar. to those from samples from Stations 1A and IB except that they are generally slightly lower.
This has been the case since 1974 and was seen in several years during the preoperational period.
There was no obvious change in results caused by the September atmospheric nuclear test.
EPA data from Harrisburg, Pa. presented in Table IV.2.4 and in Figures IV.2.1 and IV.2.2 show concentrations and surface densities of gross beta radioactivity. The values are generally lower than the values seen in this p r og r am . Prio r to July 1973, the published EPA values were the result of field measurements. Since then, laboratory measurements have been reported.
This chang eov er had the effect of decreasing the general level of reported monthly mean values due to an increased analytical sensitivity. The reason for the difference between data from this program and the EPA's is probably due to a dif ference in analytical procedure.
Sr-89 was found in all samples analyzed during the year re flec ting the presence of ' nuclear test fallout. September samples from Stations 1A and IB appear to contain radioactivity from the September 1977 test as evidencei by the high Sr-89 res ults. Station 4M did not show this same behavior possib, y due to dif ferences in rain pattern as evidenced by the variability in rain volume between the stations. Concentration values ranged from 5 to 30 pCi/1.
IV. DISCUSSION OF RESULTS Page 29 Corresponding surface densities were b etwe en approximately 150 and 1600 pCi/m l Sr-90 radioactivity concentrations were generally measured to be between I a fey tenths and 2 pCi/1. Surface densities ranged from tens to about 100 pC1/m . These levels are comparable to what has been observed in previous i
periods.
Cs-137 radioactivity concentrations and surface densities at Stations IA, IB, and 4M as given in Tables IV.2.1 and IV.2.2 are generally less than 2 pCi/l or 100 pCi/m . Station 4M tends to be somewhat lower than Statione lA and IB.
The presence of relatively high levels of Sr-89 in fresh fallout wi thout c orres po nd ing levels of Sr-90 and Cs-137 is what would be anticipated from fission-yield and half-life considerations.- All three nuclides have similar fission yields (atoms per fission) . The longer half-lives of 'Sr-90 and Cs-137 cause much lower specific activities.
The long term plots which are continued in this repo rt show generally scattered data which is common with this type of sample.
The observed radioactivity concentrations at Station.1A, IB, and 4M show the ex treme variability typical of precipitation and collectively do not indicate any contribution from the operation of PBAPS.
C. SURFACE WATER AND DISCHARGE WATER The concentrations of gross alpha and gross beta radioac tivity in the solubic and insoluble fractions of surf ace water and discharge water grab samples are given in Tables IV.3 1 and IV.3.2. Similar values for the compo si te samples from Stations 4L and 61 are given in Table IV.3 3 Mean radioactivity concentrations are given in Tables IV.3.4 through IV.3.6.
Comparative monthly and annual values are presented in Figures IV.3.1 through IV.3.10.
No measurable alpha radioactivity was found in the soluble fraction in any of the samples. The groe$ alpha radioactivity concentrations in the insoluble fraction were generally'a few tenths of a pCi/1 with one value as high as 4 pCi/1. The latter value was associated with a sample which had a large amount of suspended material.
Gross beta radioactivity concentration for Stations IP and IR are shown in Figures IV.3.1 and IV.3 2. The majority of the values for the soluble f raction were below the detection limit. A higher value was obtained at location IP in February. A high value was also obtained at Station IT which is located f urther down the discharge canal. These higher values were due to the t em po rary routing of the radwaste line into the upper discharge canal.
The results obtained for the insoluble fractions ranged from undetectable to a few pCi/1 and were similar at both locations. l Da ta for gross beta radioactivity concentration in samples f rom Unit s 2 l and 3 intake and discharge are shown in Figures IV.3.3 and IV.3.4. Similar to results from other stations most of the soluble fraction values were at or
IV. DISCUSSION Cg[ RESULTS Page 30 slightly above the detection limits. The annual mean value for the insoluble f raction for Station 1M was somewhat higher than that for Station IQ but was well within the generally observed range of values for all locations.
Figures IV.3.5 and IV.3 6 compare the gross beta r radioactivity concentration in grab samples taken at Station 6A which is upstream from PBAPS with those from Station 4F which is downstream. Soluble fractions generally had results which were below or equal to the detection limit. Except for one sample from Station 4F most values for the insoluble fractions were a few pCi/1. The July sample from Station 4F had a result of approximately 30 pCi/1. Ihis was associated with a very large amount of suspended material and is most likely due to naturally-occurring radionuclides associated with soil and sediment.
Composite water samples f rom Stations 4L and 61 are shown in Figures IV.3.7 and IV.3.8. The gross beta radioactivity concentrations for these locations are similar to each other and to the other locations sampled. There was generally no apparent difference between the composite samples and the grab samples taken near the same location. The higher value for the insoluble fraction found in the July grab sample from Station 4F was not reflected in l
the composite sample. This can be explained by the large amount of sediment in the grab sample as compared to the composite sample.
Annual mean gross beta radioactivity concentrations in surface water samples from Stations 6A, 4F, and 13A are given in Figures IV.3 9 and IV.310.
As has been the case in the past, these stations have relatively unifo rm concentrations. The slightly higher values in the insoluble fraction at Station 4F are attributable to a greater amount of sed iment in the sample because it is a deep sampling point.
The similarity of results among stations shows no indication of any me as ur able radioactivity in receiving water bodies due to the operation of PBAPS during the period of this report.
l D. WELL WATER Results of the analysis of well water samples for gross alpha, gross beta, Sr-89, Sr-90, and Cs-137 radioactivity and uranium are given in Tables IV. 4.1 and IV. 4. 2.
Radioactivity in well water samples generally arises from the leaching of na tur ally-oc cur ring nuclid es from the rocks and soil past which the water f l ows . As levels of the water table changes, variations can be encountered in the flow pattern followed by the water in a given well. This can cause changes in the radioactivity content of the water since the teachability of the radioactivity varies as the permeability of the soil and rock encountered by the water dif fers. An additional factor which can change radioac tivity concentration is the well usage. A well which is used at a constant rate tends to maintain a more constant radioactivity lev el . Lack of usage can cause buildup of radioactivity concentration if conditions very close to the l well are amenable to leaching, or it can cause concentrations to decrease if f water from the major sources of the radioactivity does not reach the well when samples are taken.
- _ - _ _ - - - - _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ l
IV. DISCUSSION g RESULTS Page 31 Gross alpha radioactivity concentrations were found to be below the d e tec t ion limit of several tenths of a pC1/1. This is consistent with data i f rom the Units 2 and 3 preoperational period.
All gross beta values were below the detection limit of approximately 2 pCi/1. ,
I Uranium was also detected in most samples from on-site and off-site locations. The levels are similar to those seen in previous periods. Uranium is naturally occurring in most roc k and .is not of plant origin.
No Sr-89, Sr-90 or Cs-137 radioactivity was de tec ted in any of the i samples except for Cs-137 in one sample from Station 7, a remote site.
f f Mean values as given in Table IV.4.2 show no significant differences between wells close to or on site and those at distant locations indicating no )
measured radioactivity from the operation of PBAPS.
E. SOIL The results obtained for concentrations of ac id-leachable gross alpha, ]
gross beta, K-40, net beta, Sr-90, Sr-89, and Cs-137- radioactivity in soil i samples are given in Tables IV.5.1 and IV.5.2. Mean values for gross alpha, net beta, Sr-90, Sr-89, and Cs-137 are plotted in Figures IV.5.1 through l
IV.5.5.
Alpha and beta radioactivity are found in soil samples because of the presence of naturally-occurring nuclides in the uranitra and thorium series and K-40, and f rom nuclides present in fallout from nuclear testing. Specific analysis fo r Sr-89, Sr-90, and Cs-137 which are normally present in fallout are done to measure these nuclides in the presence of the larger quantities of na turally-occurring radioactivity.
The gross alpha radioactivity concentration was generally a few pCi/g dry we ig ht , with the maj ority of the values below 2 pC1/g dry weight. The ,
observed dif ferences are most of ten the result of different soil composition i at the various locations.
Fet beta radioactivity, which was detectable in the majority of samples, 1 was between I and 6 pC1/g dry weight. These values are within the range of normal variability. 1 The maj ority of the Sr-90 concentrations were grouped in a f airly narrow range of a few tenths of a pC1/g dry weight. All of the values are consistent wi th previous annual averages.
As a result of atmospheric nuclear testing Sr-89 was found in the maj ori t y of samples analyzed. Values were generally a few hundredths of a pC1/g dry weight and were not significantly dif ferent between locations.
The concentration of Cs-137 generally was several tenths of a pCi/g dry weight and measurable in all samples. All values were within the range of preope rational data.
IV. DISCUSSION OF RESULTS Page 32 Values obtained from sr.mpl e s taken at the Pe ach Bottom site are c om pa rable to or lower than the average values from the surrounding sampling stations indicating no measurable radioactivity in soil from PBAPS operation.
F. SI l.T Tables IV.6.1 and IV.6 3 give the analytical results and annual means for c onc ent ra tions of ac id-leac habl e gross alpha, gross beta, Sr-89, Sr-90 and Cs-137 rad ioactivity for sil t samples. Gell gamma spectrum analysis results are given in Table IV.6.2 Gross beta and specific nuclide activities observed at several stations are presented in Figures IV.6.1 through IV.6.4.
Silt samples are expected to contain naturally-occurring rad ioac t ivi t y ,
as discussed above fo r soil samples, in addition to any other activity introduced into the aquatic environment which would settle onto or be absorbed by the silt. As can be seen by comparison of the data in Tables IV.6.1 and IV.S.1, the activity levels in silt generally are similar to those fo und in soil, al tho ugh soit may tend to be somewhat higher due to the presence of fallout from previous atmospheric nuclear testing.
The concentrations of gross alpha radioactivity at all sampling stations ra nged from not detectable to a few pCi/g dry weight and are well within the range of variability observed in PBAPS Units 2 and 3 preoperational data.
Cross beta radioactivity concentration was similar to gross alpha concentration. The results and variations between stations are consistent with the PBAPS Units 2 and 3 preoperational period.
Sr-90 concentrations occur red within the approximate range of 0.01 to 0.1 pCi/g. All res ul t s are wi thin the range of variability observed during the PRAPS Units 2 and 3 preoperational period. Sr-89 was measured in a few of the samples, most probably due to the atmospheric nuclear testing by the Peoples Republic of China.
All samples analyzed showed Cs-137 generally at low levels of a several hund r ed t h s to several tenths of a pCi/g dry weight which is well within the range of PBAPS preoperational data. Any apparent discrepancy b et we en the radiochemistry values and gamma spectrum values most probably occurs because of the gamma spectrum values given in Table IV.6.2 are more representative of the who le sample, which is inhomogenious, rather than only the aliquot analyzed. The dif ferences between stations are discussed below under ganma spectrum analysis.
Figures IV.6.1 and IV.6.2 compare Stations 4D, 4C, and 4T which are at increasing distances from the PBAPS discharge. There does not appear to be any correlation of the observed levels with particular locations when normal variability is taken into account. The preoperational data show approximately the same spread in values and values of similar magnitude to those seen during 1977.
A comparison of Stations IBB, in the discharge canal down-flow the liquii rad-waste discharge, and Station 6F, above Holtwood Dam, in Figures IV.6. 3 and ;
IV.6 4 indicates no positive addition of radioactivity by PBAPS operation, when no rm al variability is taken into account, except for cesium as is i
IV. DISCUSSION OF RESUUTS Page 33 discussed below.
Gross beta values measured during this period are within the approxima te range of 1-15 pCi/g dry weight observed during the preoperational period.
Sr-90 and Cs-137 concentrations were also similar to the preoperational data indicating no addition to the radioactivity concentration of silt due to the
- ope ration of PBAPS.
Gamma spectrum analysis showed primarily the presence of K-40 a.id the U,Th series, all of which are naturally-occurring and Cs-137. Cs-134 was found in some samples from Stations 1BB and 1X and is most likely from PBAPS ope ra tion because it is a reactor-generated product. These concentrations occurred within the PBAPS discharge water system. No Cs-134 was detected in silt in the outside aquatic environment, indicating that the Cs-137 measured silt from Conowingo Pond is a result of fallout. Zr-95 a t trib uted to atmospheric nuclear testing was found in several samples.
The overall similarity of results between locations and with the pr eope ra tional data indicates no addition of radicac tivity due to the operation of PBAPS except for very small concentrations of Cs-134 in the plant discharge water system.
- c. FIS3 The results of the analysis of fish samples for concentrations of gross alpha, gross be ta , K-4 0, net beta , Sr-89, Sr-90 and Cs-137 radioactivity are given in Tables IV. 7.1 and IV. 7.2. Gamma spectrum . data are presented in Table IV.7.3. Mean values are presented in Tables IV.7 4 through IV.7.7. Sr-90 and Cs-137 concentrations are plotted in Figures IV.7.1 through IV.7.4.
No gross alpha radioactivity was detected in any of the samples analyzed.
Net beta radioactivity generally ranged from <10 to 40 pCi/g ash. A few slightly higher results were obtained from the October sampling from Station 4J. The values were well within the range of PBAPS preoperational data.
Cs-137 and Sr-90 values in these same samples were similar to results from the remainder of the samples.
Sr-89 was detected in a few fish. This is most likely due to atmospheric nuclear test fallout.
Sr-90 radioactivity concentration as determined in samples from all locations was generally about 1 pCi/g ash corresponding to several hundredths of a pC1/g original sample. A high value of about 9 pCi/g ash was found in a first quarter sample from Station 6J which is above Holtwood Dam from PBAPS and therefore cannot be af fected by plant operation.
The concentration of Cs-137 radioactivity measured in samples from all stations was b e twe en approximately 0.1 and 6 pCi/g ash with the majority of values several tenths of a pC1/g ash. Corresponding values for the original samples were .004 to 0.3 pCi/g with the majority of values a few hundredths of a pC1/g.
YV. DISCUSSION OF RESULTS Page 34 Quarterly mean concentration of Sr-90 radioactivity as shown in Figure IV.7.1 indica tes that 1977 values at Pe ters Creek and Pequea Creek were similar to each other, although the results from analysis of Peters Creek fish
> are slightly higher than those from Pequea Creek as was the case during the preoperational period. The observed concentrations are well within the range of PBAPS preoperational data.
Cs-137 radioactivity quarterly mean concentrations at Peters Creek and requea Creek are also similar as can be seen in Figure IV.7.2.
Stations IEE and 4J, as a group of stations which could be affected by PBAPS o pe ra tion, and Station 6J, which is above Holtwood Dam and therefore l unaf fected, are compared in Figures IV.7 3 and IV.7.4. There is essentially l no dif fe rence in the range of concentrations for Sr-90 radioactivity in fish l from the two groups of locations as can be seen from Figure IV.7.3. As was l the case in 1976, the quarterly mean Cs-137 concentrations tended to be higher at Stations 1EE and 4J. The levels found in catfish, which are bottom l feeders, were again higher than those' fo und in white crappie. A dose calculation using the USNRC Regulatory Guide '1.109 model results in a calculated dose of 0.28 mrem to an adult total body f rom catfish caught in the discharge canal. This calculation assumes that all fish eaten during the year are from the discharge c anal , all cesium is from PBAPS, and the cesium is one-half Cs-134 and one-half Cs-137.
Camma spectrum analyses as shown in Table IV.7 3 generally indicate the presence of only naturally-occurring K-40 and Cs-137 from nuclear test fallout. Cs-134 was detected however in a few samples from Station IEE and 1X which are in the plant water discharge system. No Cs-134 was found in fish caught at any off-site location.
Examination of the data for fish indicates no apparent difference in radioactivity concentration betwe en species or station except for cesima concentrations. The species mean values given in Tables IV.7.6 and IV.7.7 indicate a generally higher concentration of Cs-137 in catfish.
Examination of data from all stations in Tables IV.7.1, IV.7.2, and IV./.3 indicates essentially no difference other than normal variability be tween of f-site stetions. There is a small amount of Cs-134 in a few samples from the onsite environment prob 6bly due to the operation of PBAPS.
H. S HE LLFISH The results of the measurement of concentrations of gross beta, Sr-89, Sr-90, and Cs-137 radiosetivity in oyster shells and sof t tissue, and K-40, net beta and gross gamma in sof t tiosue are given in Tables IV.8.1 through .
IV.8.4 for Stations 9, 10, and 11. Results of gamma spectrum analysis of I t i esue samples are presented in Table IV.8.5. Net beta radioactivity concentration in shellfish tissue samples are plotted in Figure IV.8.1. Sr-90 radioactivity concentrations in shellfish shell samples are presented in -
Figure IV.8. 2. No samples other than the first quarter samples were available ;
since the Chesapeake Bay Institute, which normally collects these samples did )
not have a boat in the area during the quarters in which no samples were obtained.
m IV. DISCUSSION OF RESUUIS Page 35 The net beta radioactivity c concentrations in oyster soft tissue as presented in Table IV.8.1 and plotted in Figure IV.8.1 were below the detection limit. Corresponding values in units of pCi/g of original sample were ab out a factor of 100 lower. These results are similar to values seen l previously during the PBAPS Units 2 and 3 preoperational period. l The concentrations of Sr-89, Sr-90 and Cs-137 radioactivities for soft tiss ue are also given in Tables IV.8.1 and IV.8.2. Sr-90 was found in one f sample at a level consistent with preoperational data. No Sr-89 was f o und .
Cs-137 was also not detectable. ,
1 Cross beta radioactivity concentrations in shells were below the i detection limit of about 7 pCi/g ash. Corresponding values were slightly !
lower in units of pCi/g of original sample indicating a small weight loss in ashing the samples.
Sr-90 radioactivity was detected in only one shellfish shell sample at a l ev el somewha t lower than seen in 1976. Because Sr-90 would tend to concentrate in the shell due to its chemical similarity to calcium and the ready availability of large quantities of shell, this analysis should detect j any significant changes in radioactivity level which would be below the level detectable in tissae. Sr-89 radioactivity was not detected in any samples.
There were no nuclides except uraniun and thorium detectable in shellfish soft tissue by gamma spectrum analysis.
I. VEGETATIOy The concentrations of gross alpha, gross beta, net beta, K-40, Sr-89, Sr-90, and Cs-137 radioac tivity are given in Tables IV.9.1 and IV.9 2 for vegetation samples. Mean values are in Tables IV.9 3 and IV.9.4. Figures IV.9.1 and IV.9.2 show annual mean values for Sr-90 and Cs-137 radioactivity c o ncentr ations .
The concentrations of gross alpha radioactivity were generally undetectable or barely detectable at several pCi/g ash. Corres ponding concentrations in pCi/g original samples were generally between several hund r ed ths and a few tenths of a pCi/g. The raw weight to ashed weight ratio varies markedly between samples as would be expected from the different water c ont en t of various types of vegetables and vegetation.
The concentrations of net beta radioactivity are similar for all stations and appear to have approximately the same spread. Measurable values ranged from about 30 to 400 pC1/g ash with the majority of values nearer the low end of the range. The higher values occurred in samples taken on October 1 which is the time of arrival of debris from the September atmospheric nuclear test.
All resul ts prior to the October values are in range measured during the PB APS Units 2 and 3 preoperational period. Corresponding values were in the general range of a few tenths to about 5 pCi/g original sample.
Sr-90 radioactivity concentrations had a range from a few tenths to approximately 40 pCi/g ash. These concentrations are well within the range of PB APS pr operational data. The corresponding values in terms of pC1/g l original sample showed a similar range from a few hundredths to a few tenths i
l
IV. DISCUSSION N RESULTS Page 36 of a pC1/g. As can be seen from the annual mean values shown in Figure IV.9.1 there is no significant difference between station groups.
Sr-89 from atmospheric nuclear testing fallout was found in most of the samples. 'Ihe highest values obtained were in the October 1 samples corresponding to the arrival of new test fallout as well as the accumulation of earlier f allout during the growing season. As indicated in Table IV.9.3, the annual mean values are comparable for both groups of stations.
Cs-137 radioactivity was measured at concentrations from a few tenths to W gtation again tended ,to have._ values _well pb_ove the o
a few pCi/g ash. Th @e overall average. corresponding average value wa s about 0.02 pC17g orig'liml sample. The annual mean values shown in Figure IV.9.2 indicate similar results at both groups of sample stations.
There is no indication of a contribution to the rad ioac tivity in vegetation from the operation of PBAPS as can readily be seen in Tables IV.9.3 and IV.9.4 and Figures IV.9.1 and IV.9.2 comparing potentially affected stations with unaffected stations. Wide variability is to be expected between sample types because of differences in growing season and conditions.
J. MIII The concentrations of gross beta, K-40, net beta, Sr-89, Sr-90, Cs-137, and I-131 radioactivity are given in Table IV.10.1. Mean values are presented in Table IV.10.2. Mean concentrations of Sr-90, Cs-137, and I-131 are plotted in Figures IV.10.1 through IV.10.T.
For purposes of data compar13on, farms have been divided into three groups: one containir.g Partms C, H, and J, which are regional farms near the Peach Bottom site; a second consisting of Farms A, B, C, and E, which encircle the Peach Bottom site at remote distances; and a third consisting of Farms D, U;f, and N, which are at intermediate distances from the Peach Bottom site.
The concentration of net beta radioactivity generally ranges from undetectable to a few hundred pCi/1 as has been the case during and since the preoperational period. The major beta activity in milk is due to the presence of na tur ally-oc cur ring K-40 at concentrations of approximately 1100 pCi/1.
The residual net beta values are most probably the result of the difference between two types of measurements and are not real. The gross beta radioactivity is measured directly on milk ash while the K-40 value is cal cula ted from chemical measurement of potassium on dissolved ash. From the known metabolic process of cows, it is unlikely that any radioactive nuclides from a nuclear power plant other than those of Strontium, Cesium, Barium-lanthanum, Hydrogen, or Iodine would be present in milk.
The Sr-90 radioactivity concentration prior to the October 11 samples for all f a rms was in the range of about 1 to 13 pCi/1. This range is similar to j or slightly lower than the ranges for 1975 and 1976. These concentrations are l well within the range of PBAPS preoperational data.
1 The quarterly mean values of Sr-90 for each farm group prior to October as shown in Figure IV.10.1 generally lie between 4 and 8 pC1/1 and do not show any consistent dif ference between groups. The overall values are similar to
IV. DISCUSSION OF RESULTS Page 37 those obtained during the PBAPS Units 2 and 3 preoperational period.
Sr-89 was found in most of the samples analyzed at levels up to about 10 pC1/1. The results obtained from the October 31 samples generally tended to be higher than those from earlier samples due to the arrival of fallout from the September 1977 atmospheric nuclear test.
Values for Cs-137 radioactivity concentration range from about 2 to 12 pCi/1, a somewha t lowe r range than was seen in 1976. No significant dif ference was observed among the three farm groups as can be seen from Figure IV.10 2. The results are similar to those measured during Units 2 and 3 preoperational periods. Little if any increase in Cs-137 was seen in the October samples.
I-131 radioactivity concentration results, corrected for decay to date of sampling, are presented in Table IV.10.1. Analysis on a special set of samples from June did not indicate the presence of I-131 at any of the four f arms from which samples were obtained. No I-131 was detectable in any of the regularly scheduled samples until the fourth quarter af ter the arrival of the debris fr om the September test. The maximum concentration measured was 6.6 pCi/l about a factor of 20 below the maximum found in 1976 as a result of the test in September of that year.
None of the samples contained radioactivity which can be at trib uted to the operation of PBAPS.
K. RABBITS Tables IV.11.1 through IV.11.4 present the analytical data and mean values obtained from the analysis for gross beta, K-40, and net beta radioactivity concentrations in rabbit bone, soft tissue, at.d muscle, and Sr-89 and Sr-90 in bone. Iodine-131 concentrations in rubbit thyroids are also given. Quarterly mean values for net beta and Sr-90 radioactivity concent rations are shown in Figures IV.11.1 and IV.11.2.
Measurable net beta radioactivity concentration in muscle and sof t tissue ranged from 10 to 140 pCi/g ash indicating again that the majority of the ac tivity is due to K-40. Corresponding values are about a factor of 100 lower as pCi/g original sample. For bone, values ranged f rom about 10 to 30 pCi/g ash decreasing by a factor of 3-4 as pCi/g original sample. These values are censistent with the values seen during the PBAPS Units 2 and 3 preoperational period.
Sr-90 radioactivity values in bone ranged from about 3 to 16 pC1/g anh. 1 The pCi/g original sample values art a f ac tor of 2-5 lower.
In contrast to earlier periods, Sr-89 was detected in several of the rabbit bones analyzed. Values were a few pC1/g ash. ;
i No I-131 was measurable in the thyroids analyzed. t There is no indication of radioactivity in rabbits which can be at tributed to operation of PBAPS.
I IV. DISCUSSION OF, RESULTS Page 38 t
L. EXTERNA L cat 9fA R_A_DIATION The deat rate readings and ranges from: the Nuclear Measurement Co rporation gemma radiation monitors at Stations 1A and IB are given in Table 3
IV.12.1. The tenges for a period are obtained by scanning the entire chart for that period at a later time.
The difference in the readings and ranges between Stations 1A and IB are due to dif ference in individual instruments at these locations.
The dose rate reading ar.d ranges agree with preoperational data and show no addition to the ambient gaena levels at these locations due to operation of PBAPS.
It should ha noted that these monitors are not desfigned to measure g amma radiation at environmental dose rates. Changes in instrument response occur at times of calibration because the instrument is adj ected to respond correctly to el evated gamma dose rates (0.05 - 1 0 mr/hr) . The response to normal environmental doce rates is affected by photomultiplier tube condition (dark current) and other non-linearities present at the bottom end of the instrument scale. As s. result the values obtained are generally ab ove the true env ironmental dose rate. Plant releases which could result in a significant environmental impact would be detected.
, i 1
1 1
1
- ' l I
_ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ l
IV. DISCUSSION Ol[ RESULTS Page 39 V.
SUMMARY
Except for Cs-134 in a few silt samples from the discharge canal and a few fish samples from the same locations, there was no measurable environmental radioactivity which could be at t ributed to the operation of PBAPS.
Certain nuclides such as Sr-89, Zr-95 and Nb-95 which were generally not present in recent years were found throughout 1977 as a result of atmospheric nuclear tests by the Peoples Republic of China in September and November, 1976. A test in September of this year was seen primarily in air particulate, milk, and vegetation samples. As a result of the 1976 tests, air particulate, and to some extent, precipitation samples showed the spring rise which was typical of years before 1975.
Samples such as soil, fish, etc. showed gross and/or net activities which are consistent with the known presence of naturally occurring nuclides or which are most probably a tt rib utable to fallout from earlier nuclear testing and therefore did not result from PBAPS operation.
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, % \ >
! \ t 1, Pre-operational,2nvirons ~F-tdim{ .)tivity Survey Summary Fevert, March, i, 1960 '
Rhrough January, 1966. (Septseber d"( Ti .,
'-',2 .- Peach esttom Atomic Power Station Environs Radiation Monitoring t'togram N Pt'e-operaticdal Summary Repepp}t if dts * .and 3, February 5,1966 through Asgust
! O<, 8, 1973. Lhnuary 1974) 3 1 ~* '
(. , ,
.,N , L !, i
.3. Peach Bottom Atomic Fower Statan Regional Envir9:is I Radiation Monitoring Program. January 1,1975 throubS December 31, 1975. '(July 1976)
- 4. Envirom /nr.a(b 11a[(oh . Iit;a , U. S. Environmental Protection Agency s s 3 .s i <
,, , '3
- 5. USNRC Regulatc ry C nidei 4.&, Branch Technical Position,< March 1978
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TABLE IV.l.1 A N ALY TLC AL D AT A FOR AIR-P ARTICULATE S AMPLES 3
CONCEN TR ATI0JS OF G ROSS D ET A BADI0 ACTIVITY (PCI/M ) -
GROUP I - PEACH BOTTOR SITE COLLECTION STATION PERIOD 1A 18 2 I 77 01/02-01/09 .089 i .007 .083 i .007 .081 2 .007 01/09-01/16 .008 t .008 .003 t .008 .089 t . 008 01/16-01/22 . 05 t .01 .062 i .009 .073 1 .009 f 01/22-01/30 .044 * .006 .0u) 2 .007 .040 t .007 j'
01/30-02/05 .046 * .008 .046 t .008 .045 t .008 02/05-02/12 .04b i .007 .014 * .009 .053 * .008 02/12-32/19 .051 t .007 .011 A . 00 7 .054 2 .008 02/19-02/26 048 2 .006 .007 1 .006 .053 2 .006
)
02/26-03/05 .055 * .007 .048 2 .007 .054 1 .008 03/05-03/12 .074 t .007 .068 i .008 .074 * .008 03/12-03/20 .086 * .007 .092 t .007 .089 i .007 03/20-03/27 .061 i .007 .071 2 .008 .071 2 .007 03/27-04/02 .149 t .009 .15 i .01 .20 t .01 04/02-04/09 . 098 t .008 .101 i .009 (a) 04/09-04/17 .203 e .008 .222 t .009 (a) 04/17-04/J3 .26 2 .01 .27 t .01 .33 i .01 04/23-04/30 .21 i .01 .22 i .01 .176 t .009.
04/30-05/08 . 33 e .01 .36 * .01 .24 * .01 05/08-05/14 .053 * .009 .30 t .01 .29 1 .01 05/*4-05/21 .395 i .009 44 2 .01 43 t .01 05/21-05/29 . 42 i .01 48 t .01 .46 t .01
) .37 t 05/29-06/05 .J2 t .01 .01 .35 * .01 06/05-06/11 .42 t .01 .44 * .01 .43 1 .01 06/11-06/18 . 25 t .01 .27 i .01 .27 1 . 01 06/10-06/25 . 32 t .01 .34 t .01 .35 * .01 j 06/25-07/03 .30 t .01 .32 1 .01 .J2 2 .01 07/03-07/10 .24 i .01 .24 t .01 .24 t .01 07/10-07/16 . 25 2 .01 .30 t .01 .28 t .01 07/;6-07/24 .249 2 .009 .28 2 .01 .28 * .01 07/24-07/30 . 24 2 .01 .26 t .01 .26 * .01 07/30-08/07 .214 t .009 .22 .01 .218 t .009 08/07-06/13 . 11 i .01 .12 i .01 .12 i .01 08/13-08/21 .197 1 .008 .193 * .009 .198 2 .009 08/21-08/28 . 26 * .01 .27 t .01 .27 * .01 06/28-09/04 .175 t .009 .176 t .009 .182 i .009 09/04-09/11 .156 i .009 .142 * .009 .150 t .009 09/11-09/18 .140 t .009 .148 * .009 .14 * .01 09/18-09/25 .075 t .008 .082 2 .008 .080 t .008 09/25-10/01 . 84 t .02 .82 2 .02 .86 2 .02 10/01-10/09 42 2 .01 .48 2 .01 .44 2 .01 10/09-10/16 .162 i .009 .193 t .009 .158 i .009 10/16-10/23 .21 2 .01 .22 i .01 .25 * .01 10/23-10/29 .20 t .01 .20 t .01 .20 t .01 10/29-11/06 .145 t .008 .151 e .008 .140 t .008 11/06-11/12 .124 t .009 .128 i .009 .105 i .009 11/12-11/20 .146 A .008 .163 2 .008 .160 t .008 11/20-11/26 .107 i .009 .094 i .009 .10 t .01 11/26-12/03 .083 i .007 .084 t .006 .087 i .008 12/03-12/10 . 084 i .008 .088 i .008 .087 1 .008 12/10-12/17 .099 1 .006 .098 i .008 .095 t .008 12/17-12/23 . 0b 1 * .003 .058 t .008 .061 * .008 12/23-12/31 129 2 .007 .136 t .008 .124 2 .008 ANNUAL MEAN .1842.285 .1982.305 .1982.302 (a) No sample due to power failure.
l l
TABLE IV.1.2 AN ALYTIC A L D ATA FOR AIB-P AFTICUL ATE S AMPLES CONCENTRATIONS OF GROSS BETA BADI0 ACTIVITY (PCI/M3)
GROUP II - INTERM EDI ATE DISTA NCE LOC ATICN3 C OL L ECTI ON FERIOD 3A 4A 48 5 6B 14 77 01/02-01/09 .090 t .006 .085 t .007 .086 k . 006 .082 i .007 .086 2 .006 .088 i .007 01/09-01/16 .080 t .006 .080 t .008 .083 t .009 .083 2 .008 .083 i .008 .089 i .008 01/16-01/22 .058 i .009 .062 e .00 9 .07 2 .01 .064 i .009 .065 2 .009 .089 t .009 01/22-01/30 .043 e .007 .032 i .006 .0J4 * .007 .04 4 * .006 .040 t .007 .043 A .000 01/30-02/05 .043 t .009 .043 i .008 .037 i .009 .048 t .009 .039 i .009 .046 A .009 f 02/05-02/12 .046 t .006 .048 i .007 .044 * .008 .040 t .007 .050 t .008 .050 * .007
) 02/12-02/19 .046 t .007 .051 t .008 . 06 6 t .008 02/12-02/20 .049 i .006 .054 i .007 .053 i .007 02/19-02/26 .045 t .006 .050 t .006 .053 2 .007 02/20-02/26 .059 1 .007 .053 e .006 .057 t .007 02/26-03/05 .057 t .006 .060 i .008 .057 t .008 .048 2 .007 .049 i .008 .052 i .007 03/05-03/12 .068 1 .007 .067 t .008 .075 t .008 .076 t . 008 .094 A .006 .014 2 .006 03/12-03/19 .070 t .007 .087 A .006 .083 i .006 03/12-03/20 .082 i .007 .094 t .007 .078 t .007 03/19-03//7 .057 1 .006 .079 2 .007 .066 * .006 01/20-03/27 .058 i .007 .079 t .008 .066 k .007 03//7-04/02 . 16 i .01 .15 1 .01 . 16 i .01 .147 1 .009 .16 * .01 .17 1 .01 04/02-04/09 .090 t .006 .094 t .008 .095 t .008 .096 t .008 .100 t .009 .092 i .008 04/09-04/17 .199 i .009 .208 2 .009 .220 t .009 .227 1 .009 .226 t .009 .221 2 .009 04/17-04/23 .28 t .01 .28 t .01 .28 i .01 .26 : .01 . 28 i .01 .26 i .01 04/23-04/30 .203 t .009 .21 2 .01 .22 1 .01 .197 i .009 .22 i .01 .198 1 .009 04/30-05/06 . 33 1 .01 .30 t .01 .2d t .01 .35 t .01 .J9 2 .01 .J5 i .01 05/08-05/14 .2d 1 .01 .31 i .01 .29 1 .01 .31 i .01 .32 2 .01 .29 t .01 f 05/14-05/21 . 39 9 t ' .009 .40 t .01 .37 i .01 .42 i .01 .40 t .01 42 i .01 1 05/21-05/29 44 t .01 .45 i .01 .46 2 .01 45 * .01 .50 t .01 .44 1 .01 05/29-06/05 . 31 t .01 .34 2 .01 .42 t .01 .34 i .01 .37 i .01 .33 t .01 06/05-06/11 .42 t .01 44 t .01 44 t .01 .45 t .01 .47 2 .01 .42 1 .01 0o/11-06/18 .25 t .01 .29 i .01 .26 1 .01 .25 1 .01 .28 1 .01 .25 2 .01 06/18-06/25 .31 1 .01 .32 t .01 .32 2 .01 .34 t .01 .44 i .01 .35 i .01 l
06/25-07/02 .24 2 .01 .2d 1 .01 .Jb i .01 06/25-07/03 .28 t .01< .30 t .01 .31 1 .01
, 07/02-07/10 .27 2 .01 . 29 i .01 .267 i .009 07/03-07/10 .20 t .01 .26 t .01 .27 t .01 07/10-07/16 .24 2 .01 .25 t .01 .27 i .01 . 27 i .01 . 30 t .01 .27 i .01 07/16-07/24 .257 t .009 .27 1 .01 .27 * .01 .259 t .009 .28 k .01 .248 1 .009 07/24-07/30 .23 t .01 .25 t .01 . 24 i .01 07/24-07/31 .24 k .01 .27 i .01 .24 A .01 07/30-08/07 .214 t .009 .232 i .009 .23 i .01 07/31-08/07 .21 t .01 .23 t .01 .210 t .009 08/07-08/13 11 t .01 .10 t .01 . 12 't .01 .10 t .01 .12 i .01 .109 2 .009 08/13-0d/21 .17 b i .00J .188 i .009 .186 i .009 .169 i .008 .201 : .009 .183 i .004 0 8/21- 08 /2 d . 25 t .01 .2d i .01 .27 * .01 .26 2 .01 . 26 i .01 .26 2 .01 Ou/2N-09/04 170 t .009 .16 i .01 . 19 i .01 186 1 .009 .478 i .009 .170 t .009 09/04-09/11 133 t .008 .14. t .009 ' 14
. s .01 .132 i .006 .146 i .009 .14 0 :t .008 09/11-09/16 .14 d t .009 .13 t .01 .15 t .01 .135 2 .009 .137 i .009 .1J8 t .009 09/10-09/25 .074 t .007 .079 A .000 4) .078 t .006 .081 i .006 .074 t .008 09/25-10/01 .63 .02 .90 t .02 g) .83 i .02 . 84 t .02 .d4 i .02 10/01-10/09 .53 i .01 .38 i .01 .31 e . 01 .40 t .01 .56 i .01 .42 i .01 10/09-10/16 . 16 8 i .008 .157 t .008 .164 t .009 .162 i .009 .156 1 .009 .171 k .009 10/16-10/23 .237 .009 .24 * . 01. .265 i .009 .25 t .01 .22 i .01 .21 * .01 10/23-10/29 .200 t 009 .15 i .01 .100 t .009 .20 t .01 .16 1 .01 .24 i .01 10/2 9- 11/ Ob .157 i .007 .146 t .006 .158 2 .007 .159 i .008 .159 i .008 ,161 i .008 11/06-11/12 .099 2 .008 .114 t .009 .120 t .008 .092 i .008 .109 i .009 .119 i .009 11/12-11/20 . 15 5 i .007 .159 t .008 .168 1 .007 .184 2 .008 .176 i .009 .166 t .008 11/20-11/zb . 087 2 .000 .085 t .009 .096 2 .008 .09 1 .01 .10 t .01 .11 i .01 11/2b-12/03 .085 t .007 .078 t .007 .082 t .006 .082 i . 006 .082 i .006 .087 i .008 12/03-12/10 . 082 t .007 .006 i .008 .087 e .007 .086 2 . 008 .079 2 .008 .082 * .008 12/10-12/17 .089 1 .007 .080 t .007 .089 2 .007 .091 t .008 .101 4 .008 .091 i .008 12/17-12/23 . US b t .007 .058 i .008- .059 i .007 .055 t . 008 .053 * .009 .063 i .009 12/21-12/31 .126 t .007 .2 k .1 .119 e .006 .128 t . 008 .124 2 .000 .132 i .00H ANNUAL MEAN .1881.293 .1932.301 .1822.226 .1912.292 206t.322 .1932.287 (a) No sampl6 due to power failure.
TABLE IV.1.2 (cont.)
ANALYTICAL DATA PO R AIP-PARTICULATE S AM PLES f C3NCENTRATIONS OF GROSS DETA RADI0 ACTIVITY (?CI/M )
I GROOP II - INTERMEDI ATE DISTANCE LOC ATIONS
/
COLLECTION STATION PERIOD 15 17 J1 J2 33A 38 77 01/02-01/09 .083 t .008 .088 t .007 .084 1 .007 .083 * .007 .092 t .006 .083 t .007
. 01/09-01/16 . 083 t .008 .085 t .006 .083 1 .008 .072 1 .008 (a) .090 t .008 01/09-01/22 .070 t .005 01/16-01/22 .060 t .009 .060 t .009 .062 i .009 .048 2 .008 .055 i .009 l 01/22-01/30 .042 t .007 .043 i .006 .041 .007 .040 t .006 .044 1 .007 .045 t .007 1
01/30-02/05 .041 t .009 .042 t .009 .039 i .009 .042 2 . 008 .044 1 .009 .044 * .009 02/05-02/12 .059 i .003 .056 i .008 .060 t .008 .054 i .007 .055 t .006 .046 t .000 02/12-02/20 .053 t .007 .048 t .007 .049 2 .007 .C'6 t .006 .051 i .007 .052 t .007
)
02/20-02/26 .046 t .008 .052 1 .007 .058 t .008 .000 t .007 .024 t .007 .054 i .008 02/26-03/05 .058 t .008 .050 t .008 .022 t .007 .044 i .007 .054 .008
) 02/28-03/05 . 05 i .01 03/05-03/12 .080 t .008 .070 t .008 .072 2 .007 .076 * .008 .025 i .007 03/09-03/12 .12 1 . 02 03/12-03/19 .084 * .008 .078 1 .008 .083 i .008 .080 t .007 .087 * .008 03/12-03/21 (b) 03/19-03/27 .070 t .007 .062 1 .006 .061 * .007 .081 1 .00' .072 2 .007 03/21-03/27 .067 1 .008 03/27-04/02 . 16 2 .01 .14 t .01 .13 t .01 .133 i .009 .15 i .01 .155 1 .009 04/02-04/09 .082 i .006 .089 t .008 .079 2 . 008 .092 i .008 .069 t .006 .095 t .008 04/09-04/17 .229 t .009 .229 t .009 .198 2 .009 .226 2 .009 .239 2 .009 .226 2 .009 04/17-04/23 .23 i .01 .22 i .01 .25 1 .01 .24 i .01 .26 * .01 .26 * .01 04/23-04/30 .22 i .01 .194 i .009 .20 t .01 .199 i .009 .21 * .01 .198 i .009
) 04/30-05/08 . 37 i .01 .33 t .01 .35 t .01 .33 * .01 . 35 i .01 .33 * .01
, 05/08-05/14 . 30 t .01 .28 t .01 .23 1 .01 .30 t .01 .32 1 .01 .28 i .01 05/14-05/21 41 1 .01 .40 .01 .38 t .01 .364 1 .009 41 * .01 .403 i .009 05/21-05/29 .46 t .01 .45 t .01 .40 t .01 .46 t .01 47 1 .01 .46 t .01 05/20-06/05 . 33 * .01 .34 * .01 .31 i .01 . 34 1 .01 43
- 01 .32 2 .01 06/05-06/11 .41 * .01 42 t .01 .38 i .01 .40 t .01 44 i .01 .42 i .01 l 06/11-06/16 . 26 t .01 .25 t .01 .25 t .01 .24 i .01 .25 i .01 .25 * .01 06/18-06/25 . 33 * .01 .34 1 .01 .32 t .01 .32 t .01 .34 * .01 .33 1 .01 06/25-07/02 .26 t .01 .26 2 .01 .27 i .01 .27 * .01 . 26 t .01 .26 t .01 07/02-07/10 .27 t .01 .235 t 009 .27 t .01 .226 2 .009 .25 t .01 .249 .009 07/10-07/16 . 28 i .01 .26 i .01 .25 * .01 .24 i .01 .28 i 91 .23 i .01 07/16-07/24 .28 t .01 .258 t .009 .27 1 .01 .23b t .009 .26 t .01 .237 i .009 07/24-07/31 .25 t .01 .23 * .01 .24 t .01 .22 i .01 .25 t .01 .22 1 .01 07/31-08/07 .22 t .01 .22 i .01 .22 1 .01 .20 t .01 .21 i .01 .218 2 .009 08/07-08/13 .10 t .01 .10 t .01 .11 .01 .10 t .01 .11 t .01 .10 t .01 08/11-08/21 .206 t .009 .192 i .008 .199 t .009 .188 i .008 .209 i .009 .194 i .008 08/21-08/28 . 2b t .01 .26 i .01 .26 s .01 .24 2 .01 .26 2 .01 .25 1 .01 Ou/2d-09/04 . 166 t .009 .177 A .009 .19 t .01 .162 i .009 .172 1 .009 .166 * .006 <
09/04-09/11 .142 i .009 .131 t .008 .152 * .009 .140 t .008 .129 i .008 .137 i .006 09/11-09/18 .138 i .009 .132 i .008 .133 1 .009 .121 i .009 . 134 i .009 .129 i .008 09/18-09/25 .000 t .008 .071 t.008 .081 * .008 .081 * .008 .081 i .000 .062 i .007 09/25-10/01 . 81 t .02 .89 t .02 1.08 1 .02 .70 t .02 .96 i .02 .72 t .02 10/01-10/09 .41 i .01 .40 t .01 .50 t .01 .46 t .01 .42 i .01 .45 * .01 10/09-10/16 .157 i .009 .187 t .009 .175 t .008 196 i .009 178 1 .009 .177 1 .009 '
10/16-10/23 .25 t .01 .23 1 .01 .260 t .009 .24 1 .01 .24 i .01 .21 i .01 10/23-10/29 .18 t .01 .18 i .01 .21 t .01 .16 2 .01 . 19 .01 .21 i .01 10/29-11/06 .167 2 .008 .134 i .004 .167 t .003 130 t . 008 .149 1 .008 .168 t .008 11/06-11/12 .112 t .009 .105 t 008 .115 t .008 .104 i .009 .097 i .009 .110 t .009 11/12-11/20- .152 i .003 .170 t .008 166 i .008 .169 1 .008 .161 t .006 .180 t .008 11/20-11/26 .10 t .01 .09 2 .01 .092 i .009 .090 t .009 .09 t .01 . 10 t .01 11/26-12/03 .082 t .008 .083 * .007 .087 1 .007 .084 i .008 .002 A .008 .087 i .008 12/03-12/10 .084 i .008 .064 2 .007 .097 t .007 .085 t .0G8 .084 1 .008 .002 1 .008 12/10-12/17 .089 t .006 .082 1 .007 .093 1 .007 .092 1 . 008 .085 t 2006 .094 i .008 j 12/17-12/23 . 054 t .008 .064 i .008 .062 2 .008 .054 i .008 .057 i .00u .062 2 .009 12/23-12/31 .126 t .008 .121 t .007 .110 t .006 .132 1 .008 .122 * .000 .126 t .008 l
ANNUAL HEAN .1922.286 .1881.297 1942.333 .182 .266 .1992.323 .1882.272 (a) No sample due to frozen locks.
(b) No sample due to pump failure.
1
TABLE IV.1.3 -
ANALYTICAL DATA FOR AIR-P AR TICULA TE S A MPLES CO NC ENTL ATIO NS OF G BOSS DET A E AD10 ACTIVITY (PCI/M )
CROU P III - DISTANT LOCATIONS COLLECTION STATION PEBIOD 12A 12D 77 12/30-01/07 .061 i .006
}
12/30-01/10 .054 t .004 1 01/07-01/14 .077 t .007 I 01/10-01/14 . 09 i .01 01/14-01/24 . 054 * .005 .061 i .005 01/24-01/28 . 06 * .01 .06 i .01
! 01/28-02/04 .046 * .007 .0 51 i .008 j 02/04-02/14 .042 t .005 .045 2 .005 02/14-02/18 . 06 i .01 .06 * .01 02/18-02/25 .056 i .00b .057 i .006 02/25-03/04 . 031 i .008 .076 t .008 03/04-03/12 .081 t .007 .084 1 .007 03/12-03/19 .087 i .006 .080 t .000 03/19-03/25 . 08 t .31 .07 2 .01 03/25-04/01 .156 e .009 .153 t .009 04/01-04/07 .12 i .01 11 i .01 04/07-04/18 .185 1 .007 .172 i .007 04/18-04/22 .31 t .02 (a) 04/22-04/29 .21 i .01 .20 * .01
- 04/29-05/06 .29 t .01 .36 * .01 05/06-05/13 . J2 i .01 05/06-05/16 .392 * .009 05/13-05/20 .49 i .01 05/16-05/20 59 i .02 I
05/20-05/27 43 t .01 46 t .01 l 05/27-06/03 . 34 1 .01 .37 1 .01 06/03-06/10 .50 t .01 .54 2 01 06/10-00/20 .310 t .006 .340 t .008 06/20-06/2d . 31 1 .01 32 * .01 06/26-07/06 .38 i .01 43 i 01 07/06-07/11 .21 i .01 .24 i .01 07/11-07/1b .33 i .01 .35 1 .01 07/16-07/20 .269 t .008(b) .282 i . 009 07/26-08/02 . 16 i .02 .27 .01 08/02-08/08 . 19 i .01 .20 t .01 06/06-08/15 .120 t .009 .12 i .01 08/15-08/23 .248 i .009 .27 i 01 08/23-08/29 . 24 i .01 27 2 .01 08/29-09/06 .15 9 A .009 .169 i .009 09/06-09/12 . 14 t .01 .28 i .01 09/12-09/19 .130 t .009 .14 t .01 09/19-09/2b .059 i .007 .063 2 .008 09/26-10/03 . 66 * .02 1.27 i .02 10/03-10/12 .260 t .009 .319 1 .009 10/12-10/17 . 22 i .01 .19 t .01 10/17-10/24 . 25 i .01 .26 i .01 10/24-10/31 .17 0 t .009 .193 i .009 10/31-11/06 .130 t .008 .131 1 .008 11/08-11/14 .118 1 .009 .113 t .009 11/14-11/22 .177 * .003 .174 i .008 11/22-11/28 . 11 i .01 .10 i .01 11/28-12/05 .080 t .006 .084 i .008 12/05-12/12 .086 1 .008 090 i .008 12/12 12/19 .083 t .008 .080 t .008 12/19-12/27 .091 t .007 .083 i .007 12/27-01/03 .121 i .009 .125 t .008 ANNUAL MEAN .1952.300 .2172.405 (a) No sample due to pump failure.
(b) Small volume.
T 006000000975 0 S x 965144387172 7 a 001355422311 2 IM . . . . . . . . . . . .
I 1 1 I
- P .
Un Oi 420000009000 547191625788 000123110100 2
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TABLE IV.1.5 ANALYTICAL DATA FOR AIR PARTICULATE SAMPLES l
Concentration of Gross Beta Radioactivity (pC1/m 3) l Comparative EPA DATA
! Harrisburg, PA.
l Period Min. Max. Mean January .02 .05 .03 February .02 .04 .03 March .02 .10 .04 April .03 .17 .11 May .08 .31 .19 l
Junc .14 .24 .18 t
- July .07 .22 .14 August .06 .18 .12 September .03 .72 .18 October .02 .63 .21 November .01 .12 .07 December .02 .07 .04
\
l l
7 111111 11111111111 1 111111 1111111 1 1
- B e
+7TIII+T7TI7I77+}2 223222 222222222 2
+1.2I2222+IIT _ 2122212 1
+[+ 7 7 2T 2T T T 1
- 5 9
4 0
0 4
0 0
3 o
o, b 33333+ 333333333 43 3+333434 3434344 t3 S N 000004 000000000 00 040000000000000 40
- E L r 00000.00 00000000000
. . . . . . . 0. 000000000000000. c,o0 P Z M
A S
- 0 9 9 9 E 6 0111 11 11 11110 11 10 11 11111 1 1111 11111
- T -
0000 00 00 00000 0000 00 00000 00000 00000 A o <<<<
L C << << <<<<< << << << <<<<< <<<<< <<<<<
U C
I
- T 1 R ) 5 A 3 -
P m r 1111 1111 11111 11 11 11 11111 11111 11111 S/ C . . . . . . . . . . . . . . . . . . . . . . . . . . .
RIi <<<< <<<< <<<<< << << << <<<<< < <<<< <<<<<
ISC AYp L( 0 9999 9 EA 4 99 99998 99 8 9 999 9 9 9 9 99 TNN - 03 00 0100 00000 0010 01 00010 1 0101 01100
- s . . . . . . . . . . . . . . . . . . . . . . . . .
_ IAO K << << <<<< <<<<< << <<
_ S I << <<<<< <<<<< <CC C C OMT PUA 9
- 6. M R R 9 9 0111 1111 11110 9
11 10 9
11 11111
_ 1OTT -
1 1111 11111
.CCN o . . . . . . . . . .
V EE M <0<< <<<< <<<<< <<<< << <<<<< <<<<< <<<<<
IYPC LSN EH O 0
- LTAC 4 1111 111 1 11111 11 11 BNM 1 11 11111 11111 11111 AOME - 0000 0000 00000 00 00 00 00000 00000 00000 a . . . . . . . . . . . . . . . . . . . . .
TMAD <<<< <<<< <<<<<
GI B .
R L O C F U 1 N 3 1111 1111 11111 11 11 11 11111 11111 11111 A 1 0000 0000 00000 0000 00 .00000 00000 00000 T . . . . . . . . . . . . . . . . . . . . .
A I <<<< <<<< <<<<< << << << <<<<< <<<<< <<<<<
D L 7 A 3 1111 111 1 11111 11 11 C 1 0000 0000 00000 11 11111 1 1111 11111 I - 0000 00 .00000 00000 00000 T s . . . . . . . . . . . . . .. . . . . . . . .
Y C <<<< <<<< <<<<< <<<< << <<<<< <<<<< <<<<<
L A
N A n o
i A AD A AD t AB A AB B 45712 3822 AB AAB B4571 ?3822 a 1123 445611133 3311 11 23445 61113 ' 3311 t
S 7 7 7 7 7 7 7 7 / / /
n / 8 6 5 o 0 2 2 2 i d 3 / / /
/ 1 2 2 t o 1 ci er -
l e lP 0 0 8 o 2 3 3 2
/ / /
C 1
/
2 1 1 1
- !l iljil
- 7 88888888888989 00000000000000.1 88 00 111 9
- 0. 1 1 1 1 1 1 1 1 1 1 0.1 9
1 e +TTTI7IT71+1+1 11
. . .+7........ 1 .
B 48882040222806140 22223323333133222
+7T2+TITITT1+14 5635556646653545 4 11 23333323333323333 3333433333333333 4 5 00000000000000000 0000000000000000 0 9 00000000000000000 00000000000000000 b
+ T T T 7 TI T T 3 + 1+1111
+ T TI 7 T T 7IT T 1+ 11118 0060100980087101 S N 48668668887688566 2212222112211222 1 E - 00000000000000000 00000000000000000 L r 00000000000000000 . . . .
P Z . . . . .
- M A
- S 0
E 6 88888888888989 88 9 T - 00000000000000100 1110111111111111 1 A o 00000000000000000 00000000000000000 L C .
U <<<<<<<<<<<<<<<<<
C I
T 1 R ) 5 89999989999 8 99 A 3 - 00000000000101100 11111111111111111 . . . . . . . . . .
P r . . . . . . ...
)
S/
m C
RIi D ISC AYp T L( 0 77877877787878977 9998 999999 9989 N EA 4 00000000000000000 . 00001000000100001 .
O TNN - . . . . . . . . .
(C IAO S I K <<<<<<<<<<<<<<<<<
OMT 6PUA 9 9 9
.MRR 9 88888888888989 88 1OTT - 00000000000000100 11101111111111011. . .
o . . . . . .
.CCN . . . . . .
V EE M <<<<<<<<<<<<<<<<< <<<<<<<<<<<<<<<<<
IYPC LSN EH O 0 LTAC 4 9 9 9 9 BNM 1 01101101111101111 11111111111111111 AOME - 00000000000000000 00000000000000000 . .
TMAD a . . . .
GI B <<<<<<<<<<<<<<<<< <<<<<<<<<<<<<<<<<
R L O C F U 1 9 N 3 01111111111111111 11111111111111111 A 1 00000000000000000 00000000000000000 . . .
T - . .
A I D _
L 7 99 9 9 9 9 9 99 A 3 001 01101010101100 11111111111111111 C 1 00000000000000000 00000000000000000 . .
I - . . . . . . . . .
T s <<<<<<<<<<<<<<<<< <<<<<<<<<<<<<<<<<
Y C -
L A
N A n o
AD i A A0 A t AB AABWB457123822 AB AABWB457123822 _
a 112344S6111333311 112344S6111333311 .
t _
S _
7 n 7 7 7 7
o 7 7 7
/
i d / / /
t o 2 1 0 9 c i / / 3 2 -
/
e r 4 4 /
4 l e 4 l P - -
o - -
C 6 5 2 2 1 2 /
/ / /
2 2 4 4 lllll1ll -
9 9 999 999
- 7 e
0 11 1..+!
0
.1111 000
. . .1 000
. . 11 0000000000000000 111+++3+3+{++}+11 B 2 +I647II4294282. +II! +I{ 11 667788886866676 55 8822468610482646 0 55554 45635445455 6
- 5 333333333333333 33 000000000000000 00 000000000000000 00 333233333333 3 { 32 3 000000000000000 00 000000000000000 00 9 . . . . . . . . . . . . . . . . . .
- b 1+ II 7 III 7 IIIII[ 11 + 1+11+1+1+1+1 434203391360662 70 11 S N 7994 2388273964 8 4 4
- E -
333444444443343 33 333333332333333 34 L r 00000000000000000 000000000000000 00 P Z M
_ A
_ S
- 0 9 9 8 88898 88888 88887 8 E 6 111 1111 10111 110 1 1 0 00000 00000 00000 0 T -
000 0000 00000 000 0 0 0 00000 00000 00000 0 A o . . . . . . . . . . . . . . . . . . . .
L C <<< <<<< <<<<< <<<< < < < <<<< <<<<< <<<<< <
U C
I T 1 9 998 9 99999 99 88 9 R ) 5 111 1111 11111 111 1 1 0 00010 00000 10 0 00 A 3 -
P m r S/ C
) RI1 8 DISC .
T AYp L( 0 999 9999 98999 99 0. 9 9 7 77788 77777 87876 7 NEA 000 0000 00000 0 0 00000 00000 00000 0 OTNN 4
. . . . . . . . 0 0. 910 CIAO K <<< <<<< <<<<< <<0 < < < <<<<< <<<<< <<<<< <
( S I OMT 6PUA 9 9 9 8 88898 88888 88887 8
.MRR 9 111 1111 10111 110 1 1 0 00000 00000 00000 0 1OTT -
.CCN o <<< <<<< <<<<< <<< < < < <<<<< <<<<< <<<<< <
V EE M ITPC LSN EH O 0 9 99 LTAC 4 111 1111 11111 111 1 1 1 11011 11111 11100 1 BNM 1 000 0000 00000 0000 0 0 00000 00000 00000 0 AOME -
TMAD a < <<<<< <<<<< <<<<<
G1 B <<< <<<< <<<<< <<< < <
R L O C F D 1 111 1111 11111 111 1 1 1 1111 111111 11110 1 W 3 000 0000 00000 000 0 0 0 00000 00000 00000 0 A 1 T -
<<< <<<< <<<<< <<< < < < <<<<< <<<<< C<<<<
A I D
7 9 999 9 98 L 111 1111 11111 111 1 1 0 0001 111011 11100 0 A 3 000 0000 00000 000 0 0 0 0000 000000 00000 0 C 1 I -
T s <<< <( << <<<<< <<< < < < <<<< <<<<<< <<<<< <
Y C L
A N
A n o
i A A D A t AB AAB B4571 2382 2 A B AA B B45 7 123822 a 112 3445 61113 3331 1 1 1234 45611 1333311 t
S 7 7 7 7 7 7 n / / 7 7 o 9 7 /
i d /
t o 2 2 3 2 ci / / / /
er 5 5 7 7 l e l P - - - -
o 0 9 9 9 C 3 2 2 2
/ / / /
4 4 5 5
_ 7 00 11
, 1111 9
0 9990909 2 0001010 1 1 ....... .1 9
- 0. 1 1 9
0
.1111 . 1 9
0 9
0 111 9
0 11 e +T7 t, . .
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TABLE IV. 2.4 ANALYTICAL DATA FOR PRECIPITATION SAMPLES Comparative EPA DATA Harrisburg, PA.
Period Gross Beta Gross Beta pC1/1 pC1/m 2 January 3 40 February 11 270 March 13.6 1260 April 6.6 560 May 7.5 120 June 21.8 1530 July 12 840 August 5.8 150 September 30.1 1620 October 17.8 1120 November 5.8 350 December 13 840 l
_ - - _ _ - _ _ _ _ _ _ _ _ - _ _ _ _ _ - - h
TABLE IV.3.1 A N A LYTI C A L DATA FOR SORF ACE bar Eb GRAD LAMPLES CON CESTP ATIO N ( PC/ L)
ST ATION CO LLLCTIO N G. AL P G.ALF G.UETA G.dETA DATE SOLUBLE INSOLUDLE SOLUDLE INSOLOBLE 1r 77 01/09 < .5 < .1 < 2 < .6 02/05 < J < .2 2b t 2 3. 4 t .6
!. 03/05 < .4 1.6 i .6 < 2 3.d t .8
< .2 .8 i.4 < 2 3. 3 i .6
( 04/ 02 04/30 < .8 < .2 < 2 .5 t 4 06/05 < .7 .4 1 .2 < 2 2.1 i .6 l 07/10 < .d < .2 < 2 < .5 08/07 < .6 .2 1 .2 < 1 < .4 09/04 < .6 .3 * .2 < 2 < .5 10/01 < 1 .5 t .3 < e 2.6 2 .5 11/06 < .5 .5 * .2 ( 2 1. 5 *.5 12/03 < .3 .6 1 .3 < 2 2. 2 1 .5 Ig 77 01/09 < .4 < .07 < 2 < .6 02/05 < 1 < .1 < 2 < .5 03/05 < .6 .8 i 4 < i 2. 6 2 .7 04/02 < .4 .9 2 4 < 2 2.0 t .6 04/30 <.6 < .2 < 2 .9 t .4 06/05 < .9 .3 2 .2 < 2 1. b t .6 07/ 10 < .6 .2 i.2 J t 2 < .5 08/07 < .7 < 1 < 2 < .4 09/04 < .6 .3 i.2 2 t 2 < .5 10/01 < 1 .6 1 .3 < 2 2. 8 2 .$
11/06 ~<.6 .2 1 .2 < 2 .5 t .4 12/03 <.3 .8 t .3 2 12 1. 6 * .5 4F 77 01/09 <.4 < .07 2 22 < .5 02/05 < 1 < .2 < 2 < .5 03/05 < .4 .8 i.4 < 2 2. 6 * .7 04 / 02 < .4 .8 .3 < 2 1. 4 t .6 04/ 30 < .6 < .4 < 2 2. 2 i.4 06/05 < 1 .4 1 .2 < 2 1. d t .6 07/10 < .6 4 t 2 < 2 32 1 2 06/07 < .7 .2 1 .2 < 2 2.1 * .6 09/04 < .9 2. J t .7 < 2 4. 8 i .7 10/01 < 2 .8 i.4 2 1 2 4. 4 * .6 11/ 06 < .5 .5 t .2 < 2 1. 6 .5 12/03 < .3 .5 t .2 < 2 1. 4 t .5 bA 77 01/09 < .6 .12 * .09 < 2 < .5 02/05 < 1 < .1 < 2 < .5 03/05 < .3 1.5 t .7 < 2 5. 6 t .9 04/02 < .4 1.3 t .5 < 2 2. 9 t .6 04/30 < .7 < .2 < 2 .7 t .4 06/05 < .6 .2 t .2 < 2 .6 1 .5 07/10 < .8 < .2 < 2 < .5 08/07 < .9 < .1 < 2 < .4 09/04 < .5 .2 t .1 < 2 < .5 10/01 < 1 .5 t.3 < 2 3. 2 * .5 11/ 06 < . t> .3 1 .2 < 2 .7 1 .4 12/03 < .3 .8 2 .3 < 2.0 2. 0 t .5 13A 77 01/09 (a) (a) (a) (a) 02/05 <.d < .2 < 2 < .5 03/0'5 <.5 .9 t ,4 3 t 2 2. 3 t .7 04/02 < .4 2.2 t .6 < 2 3.8 t .6 04/30 < 2 < .2 < 3 .6 i 4 06/05 < .5 1. 0 t.4 < 2 3. 9 2 .6 07/10 < .6 < .1 < 2 < .4 08/07 < .a < .2 < 2 <.4 09/04 < .o .2 t.2 < 2 < .5 10/01 < 1 1.4 i.6 < 2 5.5 t .6 11/00 < .5 .2 1 1 < 2 .8 t 4 12/03 < .3 .2 1 .1 < 2 .6 t .5 1
1 (a) No sample due to frozen pond.
l 1
_ _ _ _ _ _ _ _ _ _ . i
TABLE IV.3.3 AN AL YTIC AL D&T& 'FOR DISCH& BGE W ATER GE&B S ARPLES CONCENTRATION (pCi/1)
ST&f10N CO LL ECT IO N G. ALP G. ALP G. BETA G. BET &
DATE SOLUBLE INSOLU BLE SOLUBLE INSOLUBLE f 1M 77 01/09 <.8 < .09 < 2 < .6~
02/05 < 1 < .1 < 2 .9 i .6 03/05 <.4 1.8 t .6 <. 2 4. 0 t .8 04/02 <.4 .6 2 .3 < 2 6.4 1 .7 04/30 <.6 .6 1.4 < 2 1. 2 i .4 i 4 2 i 2 7. 4 i .7 06/05 <.8 .5 t .3 j 07/ 10 <.6 .6 A .3 < 2 5. 4 i .6 l'
<.7 i .2 < 2 < .4 08/07 .2
< .5 09/04 <.6 .6 i.2 < 2 10/01 < 1 .6 2 .3 < 2 3.1 i.5 11/06 <.6 .3 i.2 < 2 1. 0 t .5 12/03 <.3 .3 A .2 < 2 1. 3 t .5 18 77 01/09 <.7 < .1 < 2 < .5 02/05 < 1 < .1 < 2 4.5 t .7 !
03/05 <.4 1.2 A.6 < 2 4. 4 i .8 04/02 <.3 .6 A.3 < 2 3.1 i .6 04/30 <.5 < .2 < 2 .9 i .4 1 06/05 <.8 .3 2 .2 < 2 1. 4 i .5 07/10 <.7 .2 t .2 < 2 3. 2 1 .5 08/ 07 < .9 .2 t .2 < 2 < .4 3 09/04 <.7 .4 i.2 3 2 2 < .5 j 10/ 01 < 2 .7 t .3 < 2 2. 5 i .5 '
l 11/06 <.6 .4 1 .2 < 2 1. 2 t .5 12/03 <.3 .5 t.2 < 2 2.2 i .5 II 77 01/09 <.6 < .2 < 2 3. 2 i .7 02/ 05 < 2 < .1 10 't 2 4.1 i .6 03/05 <.4 .7 t.5 < 2 3.9 i .8 04 / 02 <.3 1. 2 t.4 < 2 4. 2 i .6 04/ 30 < 1 < .3 < 2 .9 2 .4 06/05 <.7 .4 i.2 < 2 2. 0 t .6 07/10 <.7 .4 *.2 < 2 3. 5 t .5
< .2 1 .2 < 2 < .4 08/ 07 1 09/04 <.7 .3 i.2 < 2 < .5 10/01 < 2 .7 i .3 < 2 3. 2 i .5 11/06 <.6 .2 i.2 2 1 2 .9 i .5 12/03 <.2 .7 i.3 < 2 1. 8 1 .5
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TA8LE IV.7.6 1977 ANNUAL MEAN RADIOACTIVITY CONCENTRATIONS IN FISH SAMPLES (pCi/g Ash)
White Crapple
)
( Environmental Station No. C. ALPHA C. BETA K-40 N.8TTA SR-89 SR-90 CS-137 l
IEE (a) <3.0 31t10 3524 (10 <.43 1.'11.4 .6721.22 1% (a) 22214 28110 (10 . .40 1.01.5 .38t.41
) 41 (a) 40220 36t11 1228 432.23 .952.13 691.75 4J (a) 38219 3027 1228 .682.75 1.22.8 . .671.78 6J (b) <4.0 37120 3125 1229 <.20 .901.10 .25t.25 overall (3.4 35222 32210 1227 462.53 1.01.5 .562.72 Channel Catfish Environmental Station No. C. ALPHA C. BETA K-40 N. BETA .SR-89 SR-90 CS-137 IEE (n) <3.2 38130 34213 12215 .382.34 1.12.7 3.413.7 1X (a) 39118 32215 13112 .9021.50 1.321.2 3.014.0 41 (a) 38120 36210 13 10 1.121.6 1.42.6 452.43 4J (a) 52264 38119 22242 .8811.56 1.01.4 1.112.0 6J (b) <3.2 36222 30110 1127 (.35 2.827.3 .142.16 overall <3.2 41138 34215 14223 .7021.20 1.523.4 1.623.5' (a) Potentially affected stations.
(b) Unaffected station MEAN RADIOACTIVITY CONCENTRATIONS IN CHANNEL CATFISH AND white CRAPPIE (pCi/g Ash)
Environmental Collection Station No. Period Date C. ALPHA C. BETA K-40 N. BETA SR-89 SR-90 CS-137 1EE & 4J (a) ist 3/7-3/21 <2.5 (31 3328 <10 .321.10 1.01.3 1.123.4 6J (b) Quarter 3/21 (2.0 25212 2616 (10 (.50 B.3 .090 1EF 4 4J (a) 2nd 4/18-6/2 <2.5 32112 3428 (10 .602.70 .961.56 1.212.0 6J (b) Quarter 6/22 (4.0 37222 3329 1127 (.20 .862.24 .161.01 1EE & 43 (a) 3rd 1/5-9/13 (4.5 42220 34116 1319 (.98 1.22.7 3.114.8 63 (b) Quarter 9/19 (3.0 38210 29214 12210 (.20 1.0 .25 1EE & 4J (a) 4th 10/16-10/18 (3.0 62270 37122 28147 .471.23 1.12.8 1.22.6-6J (b) Quarter 11/18 (4.0 40220 32210 1229 .352.14 1.11.6 .201.40 1EE & 4J (a) Annual Mean 1977 <3.1 42243 35214 15227 .60s.90 1.12.6 1.623.2 6J '0) Annual Mean 1977 <3.5 36221 30210 1228 .302.30 2.226.0 .181.20 overall Mean (3.3 40240 33114 14223 .511.84 1.413.2 1.112.9 (a) Potentially affected stations.
(b) Unaffected stations.
l
q TABLE IV.7.7 1977 ANNUAL MEAN RADIOACTIVITY CONCENTRATION 8 IN FISH SAMPLES (pCi/g orig. samples)
White Crappie f
i Environmental 9R-90 08-137 Station No. C. ALPHA C. BETA F-40 N. BETA SR-89
)
) 1EE (a) <.20 2.12.7 2.32.5 <.70 <.030 0772.035 0482.089 1X (a) 1.52.8 1.82.8 <.67 .025t.014 0642.041 .0242.021 41 (a) 2,321.0 2.01.6 .722.29 030s.020 .0572.020 0372.039
) 43 (a) 2.111.2 1.81.4 .782.53 0402.046 0712.036 .0401.040 61 (b) <.25 2.12.8 1.82.7 692.29 <.015 .0572.017 .0162.013 Overall <.22 2.121.1 1.92.6 .722.35 .0301.032 .0662.031 .0342.043 Channel Catfish Environmental Station No. C. ALPHA G. BETA K-40 N. BETA SR-89 SR-90 CS-137.
1EE (a) (.15 1.721.1 1.5t.6 .561.44 0141.013 .0462.022 .162.20 IX (a) 1.71.9 1.42.6 .612.52 .0382.062 .055t.054 .122.16 4I (a) 1.72.8 1.62.5 .571.29 0502.072 0612.027 0212.019 4J (a) 2.0*1.3 1.61.7 .752.86 0331.051 .0442.022 .0482.090 6J (b) <.18 1.711.0 1.31.1 .541.40 0182.010 .131.33 0062.008 overall <.16 1.821.0 1.42.7 612.56 .0301.049 0672.153 .070s.160 (a) Potentially affected stations.
(b) Unaffected station.
MEAN RADIDACTIVITT CONCENTRATION IN CHANNEL CATFISH AND VHITE CRAPPIE (pC1/g Orig. Sample)
Environmental Collection Station No. Period Date C. ALPHA C. BETA K-40 N. BETA SR-89 SR-90 CS-137 1EE 4 4J (a) ist 3/7-3/21 (.15 1.72.9 1.821.0 <.58 .0181.008 .0622.017 .0582.174 6J (b) Quarter 3/21 (.10 1.21.2 1.22.1 <.45 <.020 .38 004 1EE 4 4J (a) 2nd 4/18-6/2 (.15 1.61.7 1.72.6 <.53 .030t.043 .0551.063 .0602.085 6J (b) Quarter 6/22 <.25 1.92.6 1.82.7 621.23 <.015 .050 .037 .0091.006 ILE 4 4J (a) 3rd 7/5-9/13 (.25 2.itt.2 1.72.9 .682.46 .0472.054 .0661.045 .152.23 63 (b) Quarter 9/19 <.20 2.021.1 1.52.6 70s.70 <.010 .049 012 1EE & 4J (a) 4th 10/16-10/18 (.090 2.411.1 1.52.4 .982.92 <.020 .0472.017 .0511.006 AJ (b) quarter 11/18 <.20 1.911.2 1.421.2 .582.40 020 .0541.008 .0122.024 IEE 4 41 (a) Annusi Mean 1977 <.17 1.911.2 1.71.8 .692.62 .0292.040 .0582.040 .0772.152 6J (b) Annual Mean 1977 <.20 1.821.0 1.52.9 .592.39 .0171.010 .102.30 .0101.012 overall <.18 1.921.2 1.62.8 .662.56 0262.036 0721.144 .0562.141 (a) Potentially affected stations.
(b) Unaffected stations.
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- t TABLE IV.11.1 AN ALYTICAL D AT A 708 B AB81T S AMPLES CON CE NTR ATIO N (pC1/3 ash)
?
CULLECtION SR 90 D&TE ID G. U ET A N 40 W. 8 ET A SR 89 77 03/09 ft0 N E 584071 20 4 10 6 s1 . 10 t 10 < 2 8.9 i .9 boff IISSOS ST2671 140 e 10 130 s 10 < 20 MU SC LE 5M2671 240 1 10 200 t 20 40 t 20 s
592672 20 10 b A1 10 1 t 10 - 6 s2 12.6 t .U
[ 03/15 bONM 't t 10; 7 tJl 16
- 1 582673 40 t 10 5 21 30i-
) < 10 6 41 ' < 10 4 32 3.9 2 .9 SB2b74 SB2b75 10 t 10 6 t 1 < 10 < 3 16 a2 SOFT TISSJ3 572672 200 1 10 140 a 10 60 t 20 ,
"T267J 200 e 10 140 t 10 60 1 20
) <20<
f 5T2674 150 t 10 140 2 10 ST2675 120 t 10 150 a 10 , e, 10 i
M U SC LE 5M2672 230 1 10 170 1 20 WL t 70 SR2673 160 t to 140 1 10 20 t '20 5M2o74 240 t 10 190 1 20 40 t 20 l 582675 J00 t to 190 t 20 < 20 11 10 t 9 <.9 9.0 2 46 0c/14 DO NE 582761 13 e9 3 21 582762 13 29 14 21 < 9 < 2 3 (7 10.4 532763 14 t 9 4 11 11 a9 < 1 2 .9
< 9 5 a1 <9 ( 8 4.5 t .5 582764 Soft TISs0E STJ761 150 t 10 75 1 8 70' i 10 5TJ76J 100 2 10 60 46 120 1 10 5T2763 130 1 10 79 18 50 t 10 ST2764 120 t to 7J t 7 50 e 10 MUSCLE 582761 240 1 10 100 t 10 140 t 20 5M4762 60 t 10 170 t 20 < 20 582763 240 1 10 100 e 10 130 t 20 SMJ764 220 1 10 100 t 10 130 1 20 11 13 1 9 2.4 2 .6 7.3 * .3 12/27 DohL 5B2967 to
- 9 5 SV r1 TISSUE ST2967 20 0 2 10 190 t 20 < 20 MOSCLE SM2967 240 t 10 190 t 20 50 t 20 14/30 buME bS2964 16 19 6 t 1 10 t 9 < 1 10.2 * .3 SJ PT TIS SU E ST2d68 160 t 10 150 t 20 < 20 M U SC LE 5M2968 250 a 10 200 1 20 50 t 20 TABLE IV.11.2 ANALYTICAL DATA FOR RABBIT SAMPLES CONCENTRATION (pC1/ gram original sample)
CU L L LC TIO N DATE ID G.8 ETA E 40 N. BETA 58 89 SR 90 1 131 (a) 77 03/09 60a8 +82671 9 15 2.6 * .5 6 1 5 < 1 4.1 t 4 502671 < 20 filis oI D SOFT TISSJE *T2671 1. 6 * .1 1.6 1 .2 <.2 MUSCLE *M2671 2.9 2 .2 2.4 A.2 .5 t .3 03/15 DONS *B2b72 10 15 2.9 2 .5 7 A5 J t 1 6.1 t 4
- B267J 19 25 2.5 t .5 17 t 5 4 a1 7.7 1 .5 i
- B2b74 < o J.1 t.6 < 6 2 21 2.1 1 .5
- S2b75 6 t 5 1.0 t.5 < $ < 1 7.9 .8 rura0ID 532672 < 10 502673 < 10 502674 < 10 502675 .< 10 b0ff TISSUE *T267J 2. 4 1 .2 1.7 1 .2 .7 a .2
- T207J 2.4 i .2 1.7 * .2 .7 t .2
- TJ674 2. 0 t .2 1.9 e.2 < .2
- T2675 1. 4 e .1 1.7 i.2 < .2 MJSCLE +M2672 3. 2 * .2 2.3 & .2 .9 1 .3
- M2673 2.J t .2 J.0 t .2 .3 i.3
- M2674 3. 0 t .2 J.u a .2 .6 *.3
- M2675 J.7 t .2 2.5 1.2 < .3 06/14 BON 3 88276) 4 t 3 .9 t 3 3 t 3 < .3 2.7 * .2 882762 2 e2 3.0 t .3 < 2 < .4 .6 t .2 i eB2f63 4 23 1.2 *.3 3 t 3 < 4 J.3 1 .3
- B2764 < J 1.7 a.4 < 3 < .3 1.6 1 .J tHYavID 502761 < 3 j
$02762 < 3 50276) < 3 502764 < J Suff t!S SU E *T2761 1. 9 t .2 . 98 1 .01 .9 1 .2 872762 11.9 *.8 4.0 t .4 7.9 4 .9
- T2763 1. d 2 .2 1.1 *.1 .7 i.2
- T 2 7 6 4 1. 5 t .1 90 t .09 .6 k .2 MJ SC LE *M2761 4.2 e.2 1.7 i .2 2. 5 t .J j
- M2762 .8 t .1 J.6 1 .2 < .3 !
- M2763 3. 8 1 .J 1.6 * .2 2.J t .3
- S2764 14. 2 i .8 6.0 t.6 6 i 1 12/27 BONE *B2367 9 i 4 2.5 i .5 6 t 4 1.1 t .3 3.5 t .1 TH Y R OI D 502967 < 8 Sort TISS3 8 *T2967 2.0 t .1 1.8 s .2 < .2 M J SC LE *M2967 3. 0 t .2 3.0 t .3 .8 4, 12/10 BONE 882966 8 t 4 2.9 1 .5 5 2 4 i < 8 S.1 * .2 T H f uGI D 5029S8 < 7 SOFT TISS43 872168 1. 8 2 .1 1.8 1 .2 < .2 M u sC L E *M2968 3.8 1 .2 3.0 t .3 .8 *f4 (a) 1 131 is measured in pC1/ thyroid
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E i / / / E t e 2 2 2 M t e 2 2 2 M ct 1 1 1 ct 1 1 1 ea - - -
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TABLE IV. 12.1 CAMMA RADIATION MONITOR READINGS (MR/HR)
STATION 1A Range Reading Period Min. Max. Date Readings 12/27/76 - 1/2/77 .012 .012 1/2/77 012 1/3/77 -
1/9/77 .012 .013(c) 1/9 .013 1/10 - 1/16 .012 .012 1/16 .012 1/17 - 1/22 .012 .012 1/22 .012 1/23 -
1/30 .012 012 1/30 .012 1/31 - 2/5 .012 012 2/5 .012 f
i 2/6 -
2/12 012 012(c) 2/12 .012 2/13 -
2/19 .012 .013(c) 2/19 013 2/20 -
2/26 012 .014 2/26 .014 2/27 - 3/5 .012 .013 3/5 .013 3/6 -
3/12 012 012 3/12 .012 3/13 -
3/20 .012 .012(c) 3/20 .012 3/21 - 3/27 012 .012 3/27 .012 3/28 - 4/2 .012 .013 4/2 013 4/3 - 4/9 .012 .012 4/9 .012 4/10 - 4/17 012 012 4/17 012 4/18 - 4/23 .012 .012(c) 4/23 .012 4/24 - 4/30 .012 .013(c) 4/30 .013 5/1 - 5/8 .012 012 5/8 .012 5/9 - 5/14 012 012 5/14 .012 5/15 -
5/21 .012 012 5/21 012 5/22 -
5/29 .012 012(b) 5/29 012 5/30 -
6/5 .012 012 6/5 .012 C/6 -
6/11 012 .012 6/11 012 6/12 -
6/18 .012 .012 6/18 .012 6/19 -
6/25 012 012(c) 6/25 .012 6/26 - 7/3 .012 .015(c) 7/3 015 7/4 - 7/10 012 012 7/10 012 7/11 -
7/16 012 012 7/16 011 7/17 - 7/24 012 .012 7/24 .012 7/25 -
7/30 012 .012(c) 7/30 012 7/31 -
8/7 012 .012 8/7 .012 8/8 -
8/13 .012 .012 8/13 012 8/14 - 8/21 012 012(c) 8/21 (a) 8/22 - 8/28 .012 .012(c) 8/28 .012 8/29 -
9/4 012 .026(b)(c) 9/4 . 012 (d) 9/5 -
9/11 024 029 9/11 029 9/12 -
9/18 019 027 9/18 .019 9/19 - 9/25 .024 .029 9/25 029 9/26 -
10/1 023 .029 10/1 .029 10/2 -
10/9 .021 029 10/9 .029 10/10 - 10/16 021 029 10/16 029 ;
10/17 -
10/23 .018 .029 10/23 .029 10/24 -
10/29 020 029 10/29 .029 10/30 -
11/6 019 029 11/6 .029 11/7 - 11/12 017 .027 11/12 .025 11/13 -
11/20 .016 .027 11/20 .025 11/21 -
11/26 016 .025 11/26 .025 11/27 -
12/3 .015 025 12/3 025 12/4 - 12/10 012 .02? 12/10 .012 12/11 - 12/17 013 .02S 12/17 025 12/18 -
12/23 .014 .023 12/23 .015 12/24 - 12/31 009 .022 '12/31 .012 a) No reading recorded b) Monitor recalibrates on 5/24/77 and 9/2/77 c) Recorder out of service 1/6-1/9/77, 2/10-2/13/77, 3/17-3/20/77, 4/18-4/27/77, 6/23-6/30/77, 7/25-7/27/77, 8/15-8/16/77 and 8/27-9/1/77.
d) Suspect reading, chart indicated .026.
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1s 020 1/2/?F 020 12/27176 - 1/ *. / 7 7 i .020 , .
. 020 1/3/77 -
4/9/77 i I 020 .020 < 1/9
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2/19 2/26 . 021 2/2W -
2/26 ,020 .021 2/2T - 3/f '.020 .021 3/5 . 021
'i 3/6 - 3/le 020 .021 3/12 . 021 1 3/13 - 3/20 .020 .021 (d) 3/20 . 020 3/21 - 3/27 020 .021 3/27 . 021
>3/28 -
4/2 .020 .020 4/2 !.020
.020 4/9 . 020
'4/3 - 4/9 020
. 020 4/10 -
4/17 M20 ,G21 (d) 4/17 s
.020 4/23 . 020 4/1R - 4/23 .020 (d) 's 020 021 4/30 . '021 4/24 -
4/30 ' '
.019 .020 5/8 . 019 5!1 - 5/8 t (a) (a) 5/14 '. 020 5/9 .
5/14 (a) (a) 5/21 . 019 e$
5/15 -'5/21 L
5/22 -
5/31 + (a) (a) ,
5/29 ; ('q) ?
6/1 - 6/5 .020 .920 6/5 -
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6/6 .- 6/11 '
.020 . o a.: 0 6/u\ (9) 1l 6/12 6/18 .020 .020 (d) 6/1% (b) 3 6/19 -
6/73 020 .021 (d) 6/' 5 a 021 6/26 -
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7/in (c) (c) 7/10
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7/16 (c) (c) 7/16 (c)
(c) 7/24 (c)
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- 7/30' ) (c) (c) (c) 7/30 (c)
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E/3 - 8/13 (c) , (c) 8/13 (c) i h/14 < 0/21 (c) . (c) 8/21 (c) 8/22 1 -'a/28 (c)= (c) 8/28 (c)
(c) (c)' 9/4 y (c) 8/29 -
9/6 019
?/7 - - 9 / ,' 1 019 . 0 ?a 9/11 9/11 - 4/10 .021 .022 9/18 021 '
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421 022 9/25' , 021 9/26 - 10/1 ! 019 .022 10/1 l). 019 10/2 - 10/9 019 022 10/9 }t 019 10/10 4 10/26 019 .020 10/16 019 10!17 - 10/23 .022 022 10/23 3 040 (e) 10/27 022 025 10/29 025 10/24 -
030 10/30 - 11/6' 022 030 11/6 11/7 - 11/12 .022 029 11/12 029 11/13 - 11/20 022 030 11/20 030
?1/21 '1L/W 019 022 11/26h 019 11/27 - 12/3 5' 020 022 12/3 020 12/4 - 1?/10 020 022 12/10 020 12/11 - 12/17 .020 022 12/1;o 3 .020 12/18 - 12/23 ,020 022 12/23 ga 020 3 17/31 020 022 '12/31 I 010- oi 12/24 -
j (a) Pecorder.out of iervice *or repnir end recalibration 5/5/77 to-5/31/77, ;t !
recalibrates om 5/24/77 h Meter innperablie ~
e Monitor out fut re pira and calibrer.fou 7/13/7)'to 9/6/77, recalibrates I, on 9/2/77 (d) Recorder out of service 3/14//7, 4/10/~7, 4/20~4/21/77, 6/14-6/15177, ,}
6/21-6/22/77, and (/30/77. O" (t) Suspect reading, terorder did not indicate increase 4 r
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