ML20087H119
| ML20087H119 | |
| Person / Time | |
|---|---|
| Site: | Perry  |
| Issue date: | 12/31/1994 |
| From: | CLEVELAND ELECTRIC ILLUMINATING CO. |
| To: | |
| Shared Package | |
| ML20087H118 | List: |
| References | |
| NUDOCS 9504180420 | |
| Download: ML20087H119 (136) | |
Text
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- '.h 9504180420 950413 PDR ADOD. 05000440 R PDR e_ _ . _ _ - ---- - - -
i ANNUAL ENVIRONMENTAL' OPERATING REPORT FOR PERRY NUCLEAR POWER PLANT January 1,1994 to December 31,1994 Prepared by: Environmental Unit Perry Nuclear Power Plant Cleveland Electric liluminating Company Perry, Ohio April,1995 n I 5 1
Table of Contents
SUMMARY
AND CONCLUSIONS. . . . . . . . . . . . . . . . . . . . . . . . . . . 1 EFFLUENTS.......................................... 1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM. . . . . . . . . . . . . . 1 l 1.AN D U S E C E N S U S . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2 l CLAM / MUSSEL MONITORING . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3 AERIAL REMOTE SENSING . . . .
............................ 3 H ER BICI DE US E . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3 SPECIAL REPORTS . . . . . . . . . . . . ........................ 3 t.
I NTR O D U CTI O N . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5 RADIATION FU N DAM ENTALS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6 l RADIATION AND RADIOACTIVITY . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6 U N ITS OF M EAS U R E . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7 BACKGROUN D RADIATION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7 EFFLUENTS......................................... 9 i PROTECTION STANDARDS AND LIMITS . . . . . . . . . . . . . . . . . . . . . . . . . 10 { EFFLUENT PROCESSES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 10 l RADIOACTIVE RELEASE REGULATIONS . . . . . . . . . . . . . . . . . . . . . . . . . 11 i SOURCES OF RADIOACTIVE RELEASES . . . . . . . . . . . . . . . . . . . . . . . . 11 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM . . . . .13 INTRODUCTION . . . . . . . . . . . . . . . . . , . . . . . . ...........14 SAMPLING LOCATIONS . . . . . . . . . . . . . . . . . . . . ...........14 SAM PLE AN ALYSIS . . . . . . . . . . . . . . . . . .. . .................20 1994 SAM PLING PROGRAM . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 21 Atmospheric Monitoring . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 24 l Terrestrial Monitoring . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 25 Aquatic Monitoring . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 27 Direct Radiation Monitoring . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 29 t INTERLABORATORY COMPARISON PROGRAM. . . . . . . . . . . . . . . . . . . . . . 30 L CONCLUSION . . . . . . . . . . . . . . . . . . . ....................34 LAND USE CENSUS . . . . . . . . . . . ......................3; INTRODUCTION . .. .................................36 DISCUSSiOM AND RESULTS. . . . .................. . . . . . . . . 36 Table of Contents
l CLAM / MUSSEL MONITORING . . . . . . . . . . . . . . . . . . . . . . . . . . . 43 INTRODUCTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 44 COR BICU LA PROG RAM . . . . . . . . , . . . . . . . . . . . . . . . . . . . .' . . . . . 44 DREISSENA PROGRAM. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 45 < AERIAL REMOTE SENSING ............................51 I NTR OD U CTI O N . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 52 PROGRAM,.......... ..............................52 . R ES U LTS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 53 ANALYSIS OF IM PACT . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 53 t HERBICIDE USAGE. . . . . . . . . . . . . . . ...................55 S P E C I AL R E P O RTS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 57 NONCOM PLIANC ES. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 58 UNREVIEWED ENVIRONMENTAL QUESTIONS . . . . . . . . . . . . . . . . . . . . . 58 NONROUTINE R EPORTS. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 58 APPENDIX A: 1994 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM DATA
SUMMARY
.................59 APPENDlX B: 1994 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM DATA . . . . . . . . . . . . . . . . . . . . . . . . . . 61 4
I Table of Contents
SUMMARY
AND CONCLUSIONS The Annual Environmental Operating Report details the results of Environmental Monitoring Programs conducted at the Perry Nuclear Power Plant (PNPP) from January 1 through December 31,1994. This report meets all of the requirements in PNPP Technical Specification 6.9.1.6 and Appendix B of the PNPP Operating License (the Environmental Protection Plan, or EPP). Report topics include Effluents, Radiologicai Environmental Monitoring, Land Use Census, Clam / Mussel Monitoring, Aerial Remote Sensing, Herbicide Use, and Special Reports. . l The results of the Environmental Monitoring Programs for 1994 indicate that the operation l of the PNPP did not result in any significant envlronmental impact. EFFLUENTS ! During the normal operation of a nuclear power plant, small quantitles of radioactivity are released to the environment in liquid and gaseous effluents. Effluent releases are strictly regulated by the Nuclear Regulatory Commission (NRC) All radioactivity released in the plant's effluents was well below applicable federal regulatory limits. The estimated dose ; from plant effluents to the public was also well below all applicable regulatory limits. The l calculated hypothetical maximum Individual dose potentially received by an individual ! resulting from PNPP liquid effluents was 0.101 mrem or 3.4% of the app!! cable limit. The hypothetical maximum individual dose potentially received by an IndMdual resulting from j PNPP gaseous effluents was 2.77 mrad or 73% below the applicable limit. The summa-tion of the hypothetical maximum individual dose from effluents in 1994 is equivalent to less than one percent of the dose that an indMdualliving in the PNPP area receives from all sources of radiation. RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM The Radiological Environmental Monitoring Program (REMP) was established in 1981 to monitor the radiological conditions in the environment around PNPP. The REMP is con-ducted in accordance with PNPP Technical Specification 3.4.12. This program includes the collection and analysis of environmental samples and evaluation of results. The REMP was established at PNPP six years before the plant became operational. This preoperational program was designed to provide data on background radiation and ra-dioactMty normally present in the area. PNPP has continued to monitor the environment during plant operation by collecting and analyzing samples of air, precipitation, milk, fish, produce, sell, grass, water and sediment as well as by measuring radiation directly.
SUMMARY
AND CONCLUSIONS 1
Radiation levels and radioactMty are monitored within a 22 mile radius around PNPP. REMP samples are collected from both Indicator and control locations. Indicator locations are those which would be most likely to display effects caused by plant operation. They are relatively close to the plant, in the predominant wind directions (from the west and south). Control locations are those which should normally be unaffected by plant opera-tion. Typically, they are at a greater distance from the plant, in the least prevalent wind ' directions (from the north and east). Data obtained from the Indicator locations are com-pared with data from the control locations and with the concentrations present in the d environment before PNPP became operational. This comparison allows naturally occur-rin0 background radiation to be taken into account when evaluating any radiological impact PNPP may have had on the environment. Over 1300 radiological environmental samples were collected in 1994 and over 1600 analyses for radioactivity were performed. The results of the REMP indicate the adequacy of the control of the release of radioactMty in effluents from PNPP. These results also demonstrate that PNPP complies with all applicable federal regulations. Results are di-vided into four sections: atmospheric monitoring, terrestrial monitoring, aquatic monitoring and direct radiation monitoring. o Samples of air and precipitation (rain and snow) are collected to monitor the radioactMty in the atmosphere. The 1994 results are similar to those observed in both preoperational and operational programs from prior years. Only background environmental radioactMty was detected and only at expected levels. o Terrestrial monitoring includes analysis of milk, produce, vegetation, and soll samples. The results of the sample analyses indicate concentrations of radioac-tMty similar to that found in previous years. For example, the average concentra-tion of cesium 137 in soll was 302.64 pCi/kg in 994, which is at the low end of
~
the range of 208.5 to 1104.05 pCl/kg obseT6i during the past eleven years. Analyses of other terrestrial samples also detected concentrations of radionctiv-ity similar to those observed in previous years, and indicate no build-up 1-dioactMty attributable to the operation of PNPP. o Aquatic monitoring includes the collection and analysis of water, fish, and shore-line sediments. The 1994 analyses results for water and fish sample results showed normal background concentrations of radionuclides. The results of sedi-ment sample analyses indicated concentrations of radioactMty similar to previous years. The average concentration of cesium-137 was 251 pCilkg, which is well within the range of up to 864 pCl/kg established since 1981. o Direct radiation measurements averaged 51 mrem / year at indicator locations and 51 mrem / year at control locations, well within the range of previous years results. This shows that, in 1994, radiation In the area of PNPP was the same as radiation at locations greater than 10 miles away from the Plant. - Based on these results, the 1994 operation of PNPP resulted in no significant increase in the concentrations of radionuclides in the environment. - LAND USE CENSUS in order to estimate radiation dose attributable to the operation of PNPP, the potential pathways through which public exposure can occur must be known. To identify these exposure pathways, an Annual Land Use Census is performed as part of the REMP. During the census, PNPP personnel travel every public road within a five mile radius of the
SUMMARY
AND CONCLUSIONS 2
a p;;
, plant to locate key radioloolcal exposure pathways.' These key pathways include the nearest resident, garden, and milk animal in each of the sixteen meteorological sectors.
The information obtained from the census is entered into a computer program which is used to assess the hypothetical dose to members of the public. CLAM / MUSSEL MONITORING-Clam and mussel shells can clog plant piping and components that use water from Lake
+ Erie. For this reason, sampling for clams and mussels has been conducted in Lake Erie in -
the vicinity of PNPP since 1971, specifically for Corbicula (Asiatic clams) since their introduction into the Great Lakes in 1981, and for Dreissena (zebra mussels) since their discovery in Lake Erie 1989. Since no Corbicula have ever been found at PNPP, routine Corbicula monitoring provides data to determine when and if this post species will arrive in the vicinity of PNPP. The Dreissena program includes both monitoring and control and is directed at minimizing the mussel's impact on' plant operation. As in past years, this program has successfully prevented Dreissena from causing any operational problems at PNPP in 1994. AERIAL REMOTE SENSING Aerial remote sensing is a way of monitoring the plant area environment by examining detailed photographs taken from an airplane. It is used to help determine the impact, if any, of the deposition of ' drift from the cooling tower plume. The drift has the potential to carry and deposit salts which may harm vegetation. This program has been conducted regularly since 1987; no impact has been observed to date. This is the last year the - program is required to be conducted. Since no impact has been noted since the program began, it is being discontinued following the 1994 results. HERBICIDE USE Because the PNPP site has several special habitat areas, the use of herbicides is closely monitored. This ensures compliance with Ohio Environmental Protection Agency require-ments and protects the site natural areas. Based on the results of surveillances of herbicide applications on sli , herbicide has not had a negative impact on the environ-ment around the plant. SPECIAL REPORTS Significant environmental events, noncompilance with environmental regulations, and changes in plant design or operation that affect the environment are reported to regula. tory agencies as they occur. These special reports are also summarized annually in this report. Since PNPP complied with all environmental regulations, and mado no changes to the plant that affected the environment, no special reports were required in 1994.
SUMMARY
AND CONCLUSIONS 3
T 4 INTRODUCTION t INTRODUCTION 5
I RADIATION FUNDAMENTALS Atoms are the basic building blocks of all matter. Simply described, atoms are made up of positively and negatively charged particles, and particles which are neutral. These par-ticles are called protons, electrons, and neutrons, respectively. The relatively large pro-
- tons and neutrons are packed together in the center of the atom called the nucleus.
Orbiting around the nucleus are one or more smaller electrons: one electron for each proton in the nucleus. Due to their dissimilar charges, the protons and electrons have a strong attraction for each other, which helps hold the atom together. Atoms with the same number of protons in their nuclei make up an element. The number of neutrons in the nuclel of an element may vary. Atoms with the same number of protons but different numbers of neutrons are called isotopes. All isotopes of the same element have the same chemical properties and many are stable or nonradioactive. An unstable or radioactive isotope of an element is called a radioisotope or radionuclide. Radionuclides contain an excess amount of energy in the nucleus, which is usually due to an excess number of neutrons. Radioactive atoms attempt to reach a stable, nonradioactive state through a process known as radioactive decay. Radioactive decay is the release of energy from an atom's nucleus through the emission of radiation. Radionuclides vary greatly in the frequency with which their atoms release radiation. The length of time an atom remains radioactive is defined in terms of half life. Half-life is the time required for a radioactive substance *o lose half its activity through the process of radioactive decay. Half-lives vary from mil-lionths of a second to millions of years. The typical half life for radionuclides released from the plant is approximately five years. RADIATION AND RADIOACTIVITY Radioactive decay is a process in which the nucleus of an unstable atom becomes more stable by spontaneously emitting energy. Radiation refers to the energy that is released when decay within the nucleus occurs. This section includes a discussion on the three main forms of radiation produced by radioactive decay: alpha particles, beta particles, and gamma rays. Alpha Particles Alpha particles consist of two protons and two neutrons and have a positive charge. Because of their charge and large size, alpha particles do not travel very far when released (one to eight centimeters in air). They are unable to penetrate any solid material, such as paper or skin. to any significant depth. However, if alpha particles are released inside the body, they can damage the soft internal tissues because they deposit all their - energy in a small area. Beta Particles Beta particles are essentially electrons and usually carry a negative electrical charge. They are much smaller than alpha particles and travel at nearly the speed of light, thus they can travel for longer distances in air and can penetrate into sclid materials more readily than alpha particles. Beta particles have a similar lonizing effect as alpha particles, but since they are smaller, faster and have less charge, they cause less concentrated damage when interacting with tissue. External beta radiation affects primarily the skin. Because of their electrical charge, beta particles can be stopped by paper, plastic or thin metals. l l INTRODUCTION 6 l I
L l i Gamma Rays j Gamma rays are bundles of electromagnetic energy called photons which behave as though they were particles. They are similar to visible light, but of a much higher energy. For example, X-rays are a type of high-energy electromagnetic radiation. Gamma rays are generally more energetic than X-rays. They can travel long distances in air and are often , released during radioactive decay along with alpha and beta particles. Potassium 40 is an example of a naturally occurring radionuclide found in all humans that decays by emitting a gamma ray. , interaction With Matter When radiation interacts with other materials, it affects the atoms of those materials principally by knocking the negatively charged electrons out of orbit. This causes an atom to lose its electrical neutrality and become positively charged. An atom that is charged, either positively or negatively, is called an lon. Anything that creates an ion is said to be ionizing. UNITS OF MEASURE Some of the units of measure used in this report require some explanation. Activity Activity is the number of atoms in a material that decay per unit of time. Each time an atom decays, radiation is emitted. The curie (Cl) is the unit used to describe the activity of a material and indicates the rate at which the atoms are decaying. One curie of activity indicates the decay of 37 billion atoms per second. Smaller units of the curie are often used in this report. Two common units are the microcurie (pCl), one millionth of a curie, and the picocurie (pCl), one trillionth of a curie. The mass, or weight, of radioactive material which would result in one curle of activity depends on the disintegration rate. For example, one gram of radium-226 is one curie of activity, but it would require about 1.5 million grams of natural uranium to equal one curie since radium-226 decays more energetically than natural uranium. Dose Biological damage due to alpha, beta, and gamma radiation may result from the ionization caused by these radiations. Some types of radiation, especially alpha particles, which cause dense local ionization, can result in much more biological damage for the same energy imparted as do gamma or X rays. Therefore, a quality factor must be applied to account for the different lonizing capabilities of various types of lonizing radiation. When the quality factor is multiplied by the absorbed dose, the result is the dose equivalent, which is an estimate of the possible biological damage resulting from exposure to any -l type of ionizing radiation. The dose equivalent is measured in rem (roentgen equivalent man). In terms of environmental radiation, the rem is a large unit. Therefore, a smaller unit, the millirem (mrem) is often used. One millirem is equal to 1/1000 of a rem. - BACKGROUND RADIATION i Background radiation includes the decay of radioactive elements in the earth's crust, a steady stream of high-energy particles from space called cosmic radiation, naturally oc-curring radioactive isotopes in the human body like potassium-40, decay of radioisotopes used in medical procedures, man-made phosphate fertilizers (phosphates and uranium INTRODUCTION 7
are often found together in nature), fallout from nuclear weapons testing, and even house-hold items like smoke detectors. In the United States, a person's average annual expo-sure from background radiation is 360 mrem, as the Background Radiation Chart (Figure
. 1) shows.
occupattorW 03 % Ottier <1% %
. Consumer Products 5% {a o j Nuclear Medicine 4% !
N Medical /x rays 11%
$ Radon 55%
internal 11% Man Made 18% Terrestrial 8% Natural Sources 82% Background = 360 mrem / year Cosmic 8% e on atton and measurements, aonautg fadiation frposure of the Figure 1: Background Radiation Chart Many radionuclides are present in the environment due to sources such as cosmic ra-dlation and fallout from nuclear weapons testing. These radionuclides are expected to be present in many of the environmental samples collected in the vicinity of PNPP. Some of the radionuclides normally present include:
~
o beryllium-7, present as a result of the interaction of cosmic radiation with the upper atmosphere. o potassium-40, a naturally occurring radionuclide normally found in humans and throughout the environment, and o fallout radionuclides from nuclear weapons testing, including tritium and cesium-137. These radionuclides may also be released in minute amounts from nuclear facilities. Beryllium-7 and potassium-40 are especially common in REMP samples. Since they are naturally occurring and are expected to be present, positive results for these radionu-clides are not discussed in the section on 1994 Sampling Program results. However, the data on these radionuclides are included in Appendix B: 1994 REMP Data. INTRODUCTION 8
' :s ..
9 EFFLUENTS 4 9 EFFLUENTS 9
PROTECTION STANDARDS AND LIMITS The National Ccuncil on Radiation Protection and Measurement has established guide-lines governing the release of radioactMty in liquid and gaseous plant effluents. These guidelines are based on protecting the general public from exposure to harmful amounts
- of radioactMty. The Code of Federal Regulations, Title 10 Part 50, Appendix I (10CFR50, App. I) codifies these guidelines as design criteria. The NRC subsequently incorporated these design criteria into the PNPP Technical Specifications which are par'; of the license authorizing PNPP operation. Table 1 presents these limits.
Table 1: Dose limits to a member of the public i Source Body / organ Dose Limits . Liquid effluents whole body 3 mrem / year I organ 10 mrem / year Gaseous effluents noble gases - garnma 10 mrad / year noble gases - beta 20 mradlyear dose from lodine 131, tritium, and particulates with half-lives greater than eight days whole body 15 mrem / year The EPA has also established limits for exposure to radiation. These limits are also incorporated into PNPP Technical Specifications and require that dose shall not exceed 25 mrem / year whole body, 75 mrem / year to the thyrold, or 25 mrem / year to any other organ. EFFLUENT PROCESSES I During the normal operation of a nuclear power plant, small amounts of radioactive l material are released. These effluents are strictly controlled to ensure radioactMty re-leased to the environment is minimal and does not exceed regulatory limits. Effluent programs include the operation of monitoring systems, in-plant and environmental sam-pling and analysis, quality assurance for effluent and environmental programs, and de-talled procedures covering all aspects of effluent and environmental monitoring. The main objective in the control of the release or exposure to radiation is to ensure that doses are kept As Low As Reasonably Achievable (ALARA). The ALARA principle applies to reducing radiation dose both to the individuals working at PNPP and to the general public. " Reasonably achievable" means that exposure reduction is based on sound eco-nomic decisions and operating practices. By practicing ALARA, PNPP minimizes health ~ risks and possible environmental Impact, and ensures that doses are maintained well below regulatory limits. The radioactive waste treatment systems at PNPP are designed to collect and process the liquid and gaseous wastes in order to remove most of the radioactMty. Monitoring systems are used to provide continuous indication of the radioactMty present and are sensitive enough to measure several orders of magnitude lower than the release limits. Instruments are equipped with alarms and indicators in the plant control room. The alarms are set to provide warnings to alert plant operators at a small fraction of actual limits. EFFLUENTS 10
et : Waste streams are sampled and analyzed to identify .and quantify radionuclides being released. A' meteorological tower is located in the southeast comer'of the plant site. U- - Coupled with gaseous effluent release data, the meteorological data is used to calculate dose to the public. ? - In areas surrounding the plantTdevices maintained for the radiological erwironmental . , monitoring program constantly sample the air in the surrounding environment. Frequent. samples of other environmental media are also taken to determine if any radioactive
. material deposition has occurred. .
. RADIOACTIVE RELEASE' REGULATIONS ' O The maximum concentration for any radioactive release is controlled by the limits set forth'. ! in the Code of Federal Regulations, Title 10 Part 20 (10CFR20). Compliance with these ; concentration limits is ensured by sampling, analyzing, processing, and monitoring the j effluent stream. Dose limit compliance is maintained through periodic dose assessment . ; calculations. The required dose calculations are conservatively performed for the ." Maxi- , mum indhridual." This individual is assumed to reside on the site boundary at the highest . potential dose location all year, and incurs the maximum potential dose from direct . ! exposure (air plus ground plus water), inhalation, and ingestion of water, milk, vegetation, and fish. Because no one actually meets these criteria for the " maximum individual," the
- actual dose received by a rest member of the public is significantly less than what is calculated for the " maximum individual".
SOURCES OF RADIOACTIVE RELEASES-The sources of radioactive material from a nuclear power plant result from fission product
. generation (for examp;e, lodines, noble gases and particulates), or neutron activation of -l corrosion products and water (for example, cobalt and tritium, respectively). The majority j of the fission products generated remain within the nuclear fuel and fuel cladding..The :
majority of the fission products which do escape from fuel cladding as well as the majority of the activated corrosion products are removed by plant processing equipment. l i Liquid effluent releases may be required following the collection of water from small leaks within the plant or the reduction of. stored water volumes from plant systems.'In both . cases, the water is first processed through liquid radioactive waste treatment systems to. reduce the concentration of radioactive material. Dose calculations are then performed to ensure regulatory compliance and that' ALARA is maintained, prior to discharge of this processed water to the lake. Gaseous effluents are made up of noble gases, lodines and particulates. The noble gas - releases are primarily a result of containment purge operations, small steam leaks and off gassing during plant start up operations. The iodine and particulate releases are primarily a result of small steam leaks. Gaseous effluents from PNPP exit the plant from one of four - effluent vents. Each of the four effluent vents contains radiation detectors that continu-ously monitor the air to ensure that radioactivity release levels are well below regulatory limits. Samples are also collected and analyzed on a routine basis to ensure regulatory compliance and that ALARA is maintained. The hypothetical maximum doses potentially received by an individual as a result of PNPP
- effluents is shown in Table 2 below. The summation of the liquid and gaseous hypotheti--
EFFLUENTS 11
- t n - , . , . w e - -, , .-s.---, -r .
3 I cal' maximum Individual whole body doses in 1994 was equivalent to less than one percent of the dose that an average individual receives from all sources of background radiation of approximately 360 mrom (see Figure 1). Table 2: Hypothetical maximum individual doses 1994 Dose Dose Limit % of Limit Liquid Effluents l Whole body 0.101 mrem 3.00 mrom 3.37 % Organ 0.605 mrom 10.0 mrem 6.05 % Gaseous Effluents _ lodine /particulates 0.519 mrem 15.0 mrom 3.46 % Noble gas - gamma 2.77 mrad 10.0 mrad 27.4 % Noble gas - beta 2.16 mrad 20.0 mrad 17.7 % 1 i I A EFFLUENTS 12
I I
.-l l
1 . .. l . .i RADIOLOGICAL ENVIRONMENTAL 1 MONITORING PROGRAM i O e RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 13
t INTRODUCTION
~ The radiological environmental monitoring orogram (REMP) was established at PNPP for several reasons. First, it verifies the adequacy of plant design and operation to control radioactive materials and ilmit effluent releases. Second, it assesses the radiological - impact, if any, that the plant has had on the surrounding environment. Third, it ensures compliance with regulatory guidelines. The REMP is conducted in accordance with the '
PNPP Operating License, Appendix A, Technical Specifications. The Environmental-
-- Technical Specifications, or REMP requirements, were established by the Nuclear Regulatory Commission (NRC).
A wide variety of samples is collected as part of the PNPP REMP. The selection of sample types, sampling locations, and sample collection frequency are based on many things. : Potential pathways for the transfer of radionuclides through the environment to humans, sample availability, local meteorology, population characteristics, land use and Nuclear Regulatory Commiselon requirements are all considered. To ensure that the REMP data are meaningful and useful, detailed sampling methods and procedures are followed. This ensures that samples are collected in the same manner and from the same locations each time. All samples are packaged on site, then shipped to an independent vendor laboratory for analysis. The vendor laboratory analyzes the samples and reports results to the PNPP Environmental Unit staff, the Lake County General Health District, and the State of Ohio Department of Health. -l The REMP began in 1981 with 24 direct radiation monitoring locations, four sediment locations, and two fish sampling locations. In 1982, collections of air, water, milk, food products, and feed / silage were started. The program was augmented in 1985 to include precipitation and soll.' Although these last three media were not required by the NRC, they were incorporated into the program to expand its scope and provide additional data useful for analyzing environmental impacts of plant operation. In 1993, feed / silage sampling was , dropped from the program based on the past ten years of data. Also based on having l established a large baseline of data during the last ten years, all strontium analysis was - I deleted from the program in 1994,
)
SAMPLING LOCATIONS REMP samples are collected at numerous locations, both onsite and up to 22 miles away from the plant. Sampling locations are divided into two general categories: Indicator and control. Indicator locations are those which would be most likely to display effects caused by plant operation. They are relatively close to the plant, in the predominant wind direc-tions. Control locations are those which are considered to be unaffected by plant opera-
~
)
tion. Typically, they are a greater distance from the plant, In the least prevalent wind l directions. Data obtained from the indicator locations are compared with data from the ! ,, control locations. This comparison allows naturally occurring background radiation to be taken into account when evaluating any radiological impact PNPP may have had on the environment. Table 1 and Figures 2,3 and 4 identify the PNPP REMP sampling locations, q Many REMP samples are collected in addition to those required by the PNPP Operating License. In some cases (precipitation and soll, for example), the sample type is not required to be collected at all, in other cases (air sampling and direct radiation monitor-ing, for example), the PNPP REMP includes more locations than are required. The RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 14
, .- .. -. . .. . -. = . - LOperating License requirements for each sample type are discussed in more detail below. Sample types and locations that are required by the~ Operating License are shown in BOLD in Table 1. Table 1: REMP sampling locations -
~
'# Description Miles Direction Media (f) ,
'1 Haines Rd 3.4 ENE TLD, AIR 2 Site boundary 0.7 E TLD 3 Meteorologi%l tower 1.0 SE TLD, AIR, PR, SOIL 4 Site boundary 0.7 S TLD, AIR, PR, SOIL 5 Quincy Substation 0.6 SW TLD, AIR -
6 Concord Service Center 11.0 SSW TLD, AIR, PR,. SOIL, VG 7 Site boundary 0.6 NE TLD, AIR, PR, SOIL, VG - , 8 Site boundary 0.8 E TLD 9 Site boundary 0.7 ESE TLD, SOIL 10 Parmly Rd 0.8 SSE TLD 11 Parmly Rd 0.6 SSW TLD . 12 Site boundary 0.6 WSW TLD, PR, SOIL ! 13 Madison-on-the-Lake 4.7 ENE TLD 14 Hubbard Rd 4.9 E TLD 15 Eagle St Substation 5.1 ESE TLD ! 16 Dayton Rd 5.0 SE TLD 17 Chadwick Rd 5.2 SSE- TLD 18 Blair Rd - 5.0 S TLD 19 Lane Rd 5.3 SSW TLD
- 20 Nursery Rd 5.3 SW TLD 21 Hardy Rd 5.1 WSW TLD 22 Main St 6.9 SW TLD '
23 High St 7.9 WSW TLD 24 St. Clair Ave 15.1 SW TLD 25 Offshore at PNPP Discharge 0.6 NNW . SEDIMENT, FISH l 26- Offshore of Redbird 4.2 ENE SEDIMENT 27 Offshore of Fairport Harbor 7.9 WSW SEDIMENT j 28 CEI Ashtabula Plant intake 22.0 ENE WATER 29 River Rd 4.3 - SSE TLD 30 Lane Rd 4.8 SSW -TLD 31 Wood and River Rd ~ 4.8 SE TLD 32 Offshore of Mentor 15.8 WSW SEDIMENT, FISH l 33 River Rd 4.5 S TLD 34 PNPP Intake 0.7 NW WATER . .. 35 Site boundary 0.6 E TLD, AIR, PR, SOIL, VG 36 Lake County Water Plant 3.9 'WSW TLD, WATER 41 Clark Rd 1.1 SW TLD . 42 Parmly Rd 0.8 S TLD 43 Parmly Rd 1.0 SSE TLD 44 Parmly Rd 1.0 SSE VG 45 Clark Rd 0.9 SSW TLD 47 Zoldak milk farm 6.5 E MILK l 51 Rettger milk farm 9.6 S MILK 53 Neff Perkins Company 0.5 WSW TLD RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 15 l l l l
I j s 54 Hele Rd School 4.6 SW- TLD ) 55' Center Rd ~ 2.5 S TLD 56 . Madison High School 4.0 ESE TLD 1 58' Antioch Rd 0.8 ENE TLD 59 Lake shoreline at Green Rd 4.0 ENE WATER
-- 60 - Lake shoreline at Perry Park 1.0 WSW WATER 61 Keller milk farm . 7.4 SE MILK 62 Shreve farm 1.2 ENE FOOD PRODUCTS 63 Minor stream mouth 0.08 NNE SEDIMENT ;
64 Northwest Drain mouth 0.09 NW SEDIMENT 65 Major Stream mouth 0.18 W SEDIMENT - 70 H&H Farm Stand 16.2 SSW FOOD PRODUCTS ' 71 Mosley Farm 7.9 SE MILK 77 Orosz Form 1.2 E FOOD PRODUCTS (1) AIR - Air lodine and Particulate VG - Vegetation PR - Precipitation TLD - Thermoluminescent Dosimeters 1 1 I I e e 9 l RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 16 1
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- _ -___- _ - - - _ _ _ _ _ - _ _ _ _ _ _ - _ _ _ _ _ _ _ _ _ _ _ _ _ ______________________A
' SAMPLE ANALYSIS-When environmental samples are analyzed for radioactMty, several types of measure-monts are performed to provide information about the types of radiation and radionuclides
- present. The major analyses that are performed are discussed below. >
Gross heta analysis measures the total amount of beta emitting radioactMty present in a t sample.' Beta radiation may be relecsed by many different radionuclides. Since beta
. decay results in a continuous energy spectrum rather than the discrete energy levels or -
" peaks" associated with gamma radiation, identification of specific beta emitting nuclides ;
is much more difficult. Therefore, gross beta analysis only indicates whether the sample contains normal or abnormal concentrations of beta emitting radioactMty; it does not identify specific radionuclides. Gross beta analysis primarily acts as a tool to identify samples that may require further analysis. Gamma spectral analysis provides more specific information than does gross beta analysis. Gamma spectral analysis identifies each radionuclide present in the sample that emits gamma radiation, and the amount of radioactivity associated with each. No two radionuclides emit the same energy gamma rays. Therefore, each radionuclide has a very specific " fingerprint" that allows for accurate identification. i lodine analysis measures the amount of radioactive iodine present in a sample. Some I media (for example, air sample charcoal cartridges) are analyzed directly. In other media ; (for example, milk), lodine is extracted by chemical separation. , Tritium analysis maesures the amount of the radionuclide tritium (H 3) present in a sample. l Tritium is an isotope of hydrogen that emits low energy beta particles. Tritium occurs -1 naturally and is also man-made. Gamma doses received by thermoluminescent dosimeters (TLD) while in the field are determined by a special laboratory procedure. Thermoluminescence is a process by which lonizing radiation interacts with the sensitive phosphor material in the TLD. Energy-i is trapped in the TLD material and can be stored for months or years. This provides an i excellent method to measure the dose received over long periods of time. The amount of .l energy that was stored in the TLD as a result of interaction with radiation is released by. j a controlled heating process and measured in a calibrated reading system. As the TLD is 1 heated, the phosphor releases the stored energy as light. The amount of light is directly proportional to the amount of radiation to which the TLD was exposed. The readinc process also zeroes the TLD and prepares it for reuse. Table 2 provides a list of the analyses performed on environmental samples collected for the PNPP REMP in 1994. j i Sample results are often reported as below the lower limit of detection (LLD). The LLD is the smallest amount of radioactive material that will show a positive result for which there can be confidence that radioactivity is present. This statistical parameter is used as a measure of the sensitivity of a sample analysis. When a measurement is reported as less than the LLD, it means that no radioactMty was detected and that had radioactMty been present at (or above) the stated LLD value, it statistically would have been detected. The NRC, as part of the PNPP Operating License, has established values for the LLDs for REMP sample analysis. The vendor laboratory was able to comply with those values in RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 20 l
1994 with the exception of one lodine analysis for an air sample from Location 5 on March
- 3. The LLD was exceeded (0.319 pCl/m3 vs. 0.050 pCl/m3) due to a low sample volume.
. The low volume was due to the sampler head being mispositioned on the air sampler (see
" Missed Samples", below). The NRC requires special reporting if sample analysis results exceed set limits. No values exceeded these reporting levels in 1994. ,
Table 2: Analyses performed on REMP samples. "_ Sample type Frequency Analyses Performed - Atmospheric Monitoring Airborne Particulates Weekly Gross Beta Quarterly Gamma Spectral Airborne Radiolodine Weekly lodine 131 Precipitation Monthly Gross Beta, Gamma Spectral, Tritium Terrestrial Monitoring Milk Bl/ Monthly Gamma Spectral, lodine 131 Food Products Monthly Gamma Spectral Vegetation Monthly Gamma Spectral Soll Quarterly Gamma Spectral Aquatic Monitoring Water Monthly Gross Beta, Gamma Spectral Quarterly Tritium Fish Blannually Gamma Spectral Sediment Blannually Gamma Spectral ( 1 Direct Radiation Monitoring j i- TLD Ouarterly Gamma Dose Annually Gamma Dose l 1994 SAMPLING PROGRAM The contribution of radionuclides to the environment resulting from the operation of PNPP is assessed by comparing results from the 1994 program with preoperational data (i.e., data from before 1986), operational data from previous years, and control location data. The results for each sample type are discussed below and compared to historical data to *; determine if there are any observable trends. All results are expressed as concentrations. Refer to Appendix B,1994 Radiological Environmental Monitoring Program Data, for detailed results. , l Program Changes There were several changes to the program in 1994. These changes include the addition and deletion of sample locations as follows: 1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 21 I l l I b
.l l
)
~ January During an audit by PNPP Ouality Assurance it was noted that the TLDs in :
- the southeast and south sectors were positioned.slightly outside the five mile limit required by the Technical Specifications; mvo TLD locations, #31 and #33 were added to tha program to fulfill the r, virement. l 2
., - February ' The sediment sampling locatiori in the minor stream lower pool (#76)" was '
deleted from the program. Samples from this location have been used to document and track very slight contamination found in the stream bed (see
.. 1992 Annual Environmental Operating Report for Information). Sampling
-and tracking this area has become part of documentation kept in accor.
dance with 10CFRSO.75(g), the decommissioning rule. June. Seven produce sampling locations wera dropped from the program as a result of establishing permanent agreements with two farms closest to the plant site, and one farm serving as a control location. Missed Samples ,' On occasion, samples cannot be . collected. This can be due to a variety of events, including equipment malfunction, animal husbandry practices, lost shipments, or vandal-Ism. Table 3 provides a list of missed samples, the sample location, and the reason the. sample was missed, j Table 3: Missed REMP samples,1994 l Media Loca. Date Reason Missed
' Food Products 62,70,77 Apr, May, Jun Vegetables not ready for harvest 1 Food Products ' 62 Jul Vegetables not ready for harvest Food Products 70 Oct Vegetables past harvest Milk. 47 1994 Not participating in 1994 l Milk 61 Jan, Feb, Mar, Dec Drying period for goats (1)
Lake water 59,60 Jan, Feb, Mar Lake covered with ice > TLD 22 2nd Otr. Location vandalized (2) >
~
TLD 41 4th Otr. Lost in field (2) Grass 44 1994 Area recovering from construction Grass 6,7,35 Apr Insufficient growth to harvest (1) - The drying period for goats is an annual occurrence. Goats, unlike cows, cannot produce mdk all year. (2) Missing TLDs can be the result of vandalism. At locations where vandalism has been
, identified as a recurring problem, the TLD is relocated. Loss of the TLDs listed above was unusual; they were not relocated as a result of this single event.
in addition to the missed samples listed in the table, grass samples are collected only during the growing season and therfore are not collected between October 30 and April 1. A major construction project at location #44 prevented any sample collection there in 1994. This project was a continuation of work that began in 1993. If the completed prcject results in permanent. loss of the grassy area, the location will be dropped from the ,- program in 1995, and suitable replacement sites evaluated. i RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 22
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Efforts to collect food product samples are conducted during the growing season, April 1-
~ to October 30. Samples were available only during the months of July through' October.
This year, agreements with the two local produce growers nearest the plant in areas of
~ high predicted deposition were semblished in order to facilitate consistent sample collec-tion. An' agreement was'also established with a. control location. The PNPP Operating ~ l License requires collection of three types of food products from each'of two indicator . -
locations ~and similar food products from a control location. Due to different planting
. schedules, weather, and harvesting' schedules, these requirements were met only during the peak of the harvest season in September. -
Events may also occur which prevent a sample from being collected in the normal way, or prevent a complete sample from being collected. The following is a discussion of these events for 1994. AIR - On March 3, the air sampler at Location 5 was. replaced, but the sample head was not positioned properly on the unit. This resulted in a low sample volume (1064 cubic feet vs. approximately 10,000 cubic feet in a normal sample), which in turn resulted in the vendor radio-logical laboratory not being able to achieve the LLD for the radioiodine adsorption cannister. < On August 31, air samples from Locations 6 and 7 had lower than - normal gas meter and timer readings (approximately eight and three hours lower than normal, respectively). This may have been caused by a short power outage related to severe weather on August 28. On October 12, Location 1 was found vandalized with the power breaker in the OFF position. This resulted in a low air volume sampled (5308 cubic feet). On November 30, the timer reading for the sample from Location 7 i was two hours icwor than normal. This may have been a result of a i power outage. WATER - In January, a grab sample was taken at Location 28 due to a sampler malfunction. The' sampler was replaced with a new unit. September through December, grab samples were collected at Location 28 in lieu j of a composite sample. This sampler is located in the intake at the. Ashtabula CEI plant; it was disconnected during this time due to construction. ; A grab sample was collected at Location 36 in January and February. 1 in both cases, the sampler intake was clogged with Jdebris which i pievented the pump from drawing sufficient volume for a sample. In , each case, the intake was cleaned and the sampler returned to service. TLD - The annual TLD at location 22 was noted to be missing at the time of : 1 the second to third quarter changeout (7/7/94), it was replaced on - I 7/12 and remained in place for the rest of the year. Both quarterly TLDs were missing at this time also, as noted in Table 3.
- Both quarterly TLDs at location 42 were vandalized during the third !
quarter. They were replaced on 8/24 and remained for the rest of the _ 1 quarter. l RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 23 1
FOOD - In July, only two food products were collected from Location 70; in PRODUCTS August and October, only two were. collected from Location 62. This was due primarily to differences in planting and harvest schedules among the three produce growers and for different crops. M/LK In September, culk from location 61 was collected 10/24 to 10/27 rather than 10/21 to 10/24. This was due to a scheduling problem with the farmer. Atmospheric Monitoring AIR Air samp!!ng is conducted to detect any increase in the concentration of airborne radionu. clides. Five locations (four indicator and one control), are required by the PNPP Operating License. Air sampling pumps are used to draw continuous samples at a rate of approxi-mately one cubic foot per minute, which is roughly the same rate as human respiration. The air is drawn through glass fiber filters, to collect particulates, and charcoal cartridges, to adsorb lodine. The samples are collected on a weekly basis,52 weeks a year, from each of seven air sampling stations. Six of the locations are within four miles of the plant site; the seventh is used as a control location and is eleven miles from PNPP. Air samples are analyzed weekly for gross beta, lodine, and by gamma spectral analysis (quarterly). A total of 364 of each type of air sample (particulate and iodine) was collected in 1994. Gruss beta activity was detected in all but one air sample and ranged up to 0.04 pCl/m3 The annual average concentration of gross beta at both indicator and control locations was 0.02 pCl/m3. Historically, the concentration of gross beta in air has been essentially identical at indicator and control locations, as shown in Figure S. INDICATOR 0.030-g E CONTROL E 0.025-w v R 0.020- ; , , g : s
>- 0.015 - 4 l l l !- ! ( ! ;
s
> 0.010- : s l l !
p [ ! ! ! o 0.005- H ; l ! !
<C 8 i
i ; 0.000 ; i 82 83 84 85 86 87 88 89 90 91 92 93 94 YEAR Figure 5: Annual average concentration of gross beta in air. RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 24 i i
)
H
' Except for naturally occurring beryllium 7, no radionuclide was identified in the gamma spectral analysis above the LLD. lodine 131 was not detected in any sample above the LLD of 0.05 pCl/m3 PRECIPITATION 1 Precipitation sample analysis allows us to detect radionuclides deposited from the at- .
mosphere. Precipitation in the form of rain, snow, sleet or hall provides a way to wash airborne radionuclides from the atmosphere. Although not required by the PNPP Operating License, samples are collected from six locations using passive collection . ; containers. Containers are removed monthly or when full, strained to remove debris, and 1 shipped to the laboratory for analysis. There are five indicator locations within one mile of PNPP and one control location, which is located eleven miles from PNPP. Precipitation samples are analyzed for tritium, gross beta, and by gamma spectral analysis. A total of 72 precipitation samples were collected in 1994. Tritium was not - detected above the LLD of 1500 pCl/l in any of the samples. The results of gamma spectral analysis were all below LLD as well. Gross beta activity was detected in all samples and ranged from 1.40 pCl/l to 16.30 pCl/l. - The annual average concentration of gross beta was 4.76 pCill at the indicator locations and 4.79 pCill at the control locations. The annual average concentration was within or below the range of previous years (from 2.71 pCl/l to 11.79 pCl/Q. Terrestrial Monitoring Collecting and analyzing samples of milk, food products and vegetation provides data to , assess the build-up of radionuclides that may be ingested by humans. The data from soil samples provides information on the deposition of radionuclides from the atmosphere. Neither vegetation nor soll samples are required by the PNPP Operating License. MILi< Samples of milk are collected once each month from November through March, and twice each month from April through October. Sampling is increased during the summer be- 1 cause animals usually feed outside on pasture and not on stored feed. The PNPP REMP - includes four milk locations (three within eight kilometers of the plant, and one control); if j no milk locations are withb this distance, fooo product sampling must be performed. ' Since there were no milk producing animals within the required distance, food product sampling (discussed below) was performed. Milk was collected from *.he available loca-tions even though they did not meet the Operating License requirements if new locations that meet the Operating License requirements are identified in the future, they will be added to the program. Milk samples are analyzed for iodine and by gamma spectral analysis. A total of 50 milk - samples were collected in 1994. lodine was not detected above the LLD of 0.75 pCi/l in 1 any of the samples. The concentrations of all radionuclides except naturally occurring - potassium-40 were below LLDs in all samples collected. The results for potassium-40 -! were similar at indicator and control locations, as expected. FOOD PRODUCTS j Food products can provide a direct pathway to humans by ingestion. They can absorb i radionuclides from atmospheric deposition from airborne sources or irrigation water drawn from a lake or pond receiving airborne or liquid effluents. Also, radionuclides in the soll ) may be absorbed by the roots of the plants and become incorporated into the edible ! RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 25 I
--a - --. --- -- -_ -_ . _ _ . - ,- -e m# -
. e m w , ==v -
I I portions. Because there is not a sufficient number of milk sampling locations, the PNPP REMP is required to include two food product Indicator locations and one control location. 1 Food products are collected monthly during the growing season from two farms in the ) vicinity of PNPP. The control location for food products is 16.2 miles from PNPP. l
. A total of 27 food product samples were collected in 1994 and analyzed by gamma spectral analysis. Seven food products were collected, including several varieties of cab-bage, broccoli, cauliflower, dill, lettuce, beet greens and turnip greens. Beryllium-7 and potassium-40, naturally occurring radionuclides, were found in several samples, as ex-pected. No other radionuclides were detected above the LLDs.
VEGE~ATION Vegetation (grass) was collected monthly during the growing season from three locations (two indicator and one control) in 1994. Grass is clipped from open areas using standard lawn trimming equipment. The controllocation for vegetation is eleven miles away. A total of eighteen grass samples were collected in 1994 and analyzed by gamma spectral analysis. Two naturally occurring radionuclides were detected: beryliium-7 and potassium-
- 40. No other radionuclides were detected above the LLDs.
SOIL Soll samples are collected semiannually from seven locations (six locations and one control). The control location is eleven miles away. Only the top inch of soll is sampled in an effort to identify possible trends in the local environmental radionuclide concentrations. Fourteen soll samples were collected in 1994 and analyzed by gamma spectral analysis. Two naturally occurring radionuclides, potassium-40 and radium-226 were detected in the samples, as expected. Cesium-137 activity was detected in all samples and ranged from 66.00 - 628.00 pCl/kg. The annual average concentration of ceslum 137 was 317.00 pCl/kg at the indicator locations and 216.50 pCi/kg at the control location. For all sample sites, the annual average concentrations were similar to those measured in previous years (Figure 6). The downward trend apparent in the figure represents the decrease in cesium-137 deposition from atmospheric weapons testing in the 1960's and '70's. _ 1,200- . cn . E INDICATOR E CONTROL o 800- ? it 600-p ( 400-h . g
~
l ' l 0 , i i i i i , i i 85 86 87 88 89 90 91 92 93 94 YEAR Figure 6: Annual average concentration of cesium-137 in soll RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 26 I l
The difference between indicator and control location results is not surprising since the presence of radionuclides in soll is so dependent on site specific factors such as soll type and drainage. These factors determine the abilliy of the soll to attract ions. For example, differences in soll types at the six indicator locations resulted in cesium-137 concentra-tions ranging from 66.0 pCl/kg to 628.0 pCilkg. Aquatic Monitoring Radionuclides may be present in Lake Erie from many sources (other than PNPP) includ-
- Ing atmospheric deposition, run-off/soll erosion, and releases of radioactMty in liquid effluents from hospitals, universities or other industrial facilities. These sources provide two forms of potential radiation exposure, external and internal. External exposure can occur from contact with water or shoreline sediments. Internal exposure can occur from ingestion of radionuclides, either directly from drinking the water, or as a result of the transfer of radionuclides through the aquatic food chain to the eventual consumption of aquatic organisms, such as fish. To monitor these pathways, PNPP samples water, shore-line sediments, and fish.
WATER Water is sampled from five locations along Lake Erie in the vicinity of the PNPP as required by the PNPP Operating License. Samples from three locations are collected using composite sample pumps. The pumps are designed to collect water at regular intervals and composite it in a sample container. The containers are removed monthly and the samples shipped to the laboratory for analysis. Samples from two locations are col-lected weekly and combined. Each month the combined sample is shipped for analysis. Fifty-four water samples were collected and analyzed for groas beta activity and by gamma spectral analysis in 1994. From these, monthly samples were composited into quarterly samples and analyzed for tritium. Gross beta activity was detected in all samples collected and ranged from 1.30 - 4.80 pClil. The annual average concentration of gross beta was 2.42 pCl/l at the indicator locations and 2.63 pCl/l at the control location. For all sample locations, the annual average concentrations were similar to those measured in previous years (Figure 7). 10-9 INDICATOR Nb E CONTROL R 6- l
>- i F-- ? .
5 4- l 1 F i p ' 4 l
* ~
? : : l i i l l, lllll i . i i i 82 83 84 85 86 87 88 89 90 91 92 93 94 YEAR F10ure 7: Annual average concentration of gross beta in water RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 27
1 1 I The sign'ficant difference between pre-1988 data and post-1988 date has been attributed to a change in vendor laboratories in 1987/1988. A comprehensive explanation is provided in the 1988 Annual Environmental Operating Report. No radionuclides were detected by gamma spectral analysis above the LLD. Tritium was
. detected in ten samples and ranged from 173 to 282 pCl/l. The annual average con. l centration of tritium was 226 pCl/l at the indicator locations and 173 pCi/kg at the control location. These results are well within the range of those measured in previous years . which have ranged from below the lower limit of detection to 2,200 pCill.
SEDIMENT Sampling take bottom sediments can provide an indication of the accumulation of un-dissolved radionuclides which may lead to internal exposure to humans through the in-gestion of fish, through resuspension into drinking water, or as an external radiation source from shoreline exposure to fisherman and swimmers. Although only one location is required by the PNPP Operating License, sediment is sampled twice each year from l seven locations, two of which are also fish sampilng locations. Sediment samples from offshore are collected using a hand dredge. Near shore samples are collected usin0 a scoop. Fourteen sediment samples were collected in 1994 and analyzed by gamma spectrometry. The predominant radionuclide detected by gamma spectral analysis was potassium-40, which is naturally occurring. Potassium-40 has been detected in all sam. ples since the program began in 1981. Ceslum-137 was detected in eight samples and ' ranged from 43 478 pCi/kg. The annual average concentration was 243 pCi/kg at the , indicator locations and 276 pCl/kg at the control location. These are within the range of ' concentratiens measured in previous years (Figure 8), The changes in cesium-137 concentration from year to year may be related to the move-ment of sediment on the lake bottom. Wave action and currents can cause significant sediment movement between sample collections. For this reason, it is unlikely the same bed of sediment is sampled at each collection. This would contribute to inconsistent data, as Figure 8 demonstrates. 1,000-E INDICATOR en s o 800- E CONTROL O 600-b 400-2 ! b 200- ! n ! ! 0- $ ! 81 82 83 84 85 86 87 88 89 90 91 92 93 94 YEAR Figure 8: Annual average concentration of cesium-137 in sediment RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 28
E FISH Fish are analyzed primarily to quantify the dietary radionuclide intake by humans, and secondarily to serve as indicators of radioactivity in the aquatic ecosystem. Fish are collected from two locations, twice each year as required by the Operating License. Important sport and commercial species are targeted, and only the fillets are sent to the laboratory for analysis. A scientific collecting permit is obtained annually from the Ohio
- Department of Natural Resources for fish samp!!ng.
Twenty-five fish samples were collected in 1994 and analyzed by gamma spectral - analysis. Nine species of fish were represented, including walleye, drum, smallmouth bass, carp, white sucker, white perch, yellow perch, redhorse sucker, and rockbass. As expected, naturally occurring potassium-40 was found in all samples. No other radlonu-clides were detected above the LLD. Direct Radiation Monitoring THERMOLUMINESCENT DOSIMETERS Environmental radiation is measured directly at thirty-nine locations around the PNPP site (the REMP is required to include 28 locations, two of which are control locations). The locations are positioned in tuo rings around the plant as well as at the site boundary. The inner ring is within a one mile radius of the plant site; the outer ring is four to five miles from the plant. Control locations are over ten miles from the plant in the two least prevalent wind directions. Each location is equipped with three thermoluminescent do-simeters (TLDs). Two are changed quarterly and one is changed annually. A total of 348 TLDs were collected and analyzed in 1994. This includes 309 collected on a quarterly basis, and 39 collected annually, in 1994, the annual average dose for all indicator locations was 51.05 mR, and for all control locations was 50.85 mR. Figure 9 shows historical TLD data. The TLD results are higher prior to 1988 due to a change in vendor laboratory services. A comprehensive explanation of the difference is provided in the 1988 Annual Environmental Operating Report.
$ E INDICATOR 5 20- p : E CONTROL {
Q = l i ! 5 ~ l l <
$10- l l ; j l f ! ! I 2
- 5 l ;
l l I O ' *
! l l :
< 0 ! ! ! I l
4 i . . 81 82 83 84 85 86 87 88 89 90 91 92 93 94 ! YEAR j Figure 9: Average dose per quarter RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 29 i I l l
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INTERLABORATORY COMPARISON PROGRAM The purpose of the interlaboratory Cross-Check comparison program is to provide an ; independent check on the vendor laboratory's analytical procedures. Samples with a i known concentration of specific radionuclides are provided to the vendor laboratory. The ,
. vendor laboratory measures and reports the concentration of specified radionuclides. The i known values (EPA values) are then compared to the vendor results. Results consistently outside established acceptance criteria indicate a need to check instruments or - procedures. 1 in 1994, the vendor laboratory analyzed 42 samples of air filters or water for this program.
One result was outside the acceptable range (see (1), below). The results of this program are shown in Table 4. Results are expressed in pCi/l for liquid samples, pCi/ filter for filter samples, and mg/l for potassium results. Results shown in BOLD were outside the control limits and are discussed in the footnotes below. In addition to their participation in the EPA Interlaboratory Comparison Program, the vendor laboratory conducts an Internal crosscheck program for dosimeters. Table 5 shows the results of this program. The vendor laboratory routinely monitors the quality of their analyses by analyzing
" spiked" samples (samples with a specific quantity of radioactive material present in them. The quantity is not known by the sample analyst). Table 6 shows the results of this program for 1994.
I i i RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 30
1 l,
' Table 4: 1994 EPA Cross-Check intercomparison Program results.
Sample Acceptable } Date Type Analysis Vendor Result EPA Value Range Jan. Water Sr-89 20.0 20.0 16.3 - 33.7 J Sr-90 14.0 15.0 6.3- 23.7 - Gross alpha 20.3 15.0 6.3 - 23.7 )l Gross beta 55.3 62.0 44.7 79.3 i Feb. Water 1131 110.0 119.0 98.2 - 139.8 - Ra-226 19.4 19.9 14.7 - 25.1 ; Ra-228 15.0 14.7 8.3 - 21.1 Uranium 9.7 10.0 4.9-15.3 , Mar. Water H3 4843.3 4936.0 -4078.9 - 5793.1 Pu-239 28.2 27.6 22.7 - 32.5 Apr. Water Gross alpha 73.3 86.0 47.8 -124.2 Ra-226 16.9 20.0 14.8 - 25.2 Ra-228 19.7 20.1 11.4 - 28.8 Uranium 25.1 25.0 19.8 - 30.2 Co-60 20.3 20.0 11.3 - 28.7 Cs-134 32.3 34.0 25.3 -42.7 Cs 137 31.3 29.0 20.3 - 37.7 Gross beta 101.0 117.0 85.8- 148.2 Sr-89 15.0 20.0 11.3 - 28.7 Sr-90 14.3 14.0 5.3 - 22.7 Jun. Water Ra-226 15.0
]
15.0 11.0 - 19.0 l l Ra-228 14.8 15.4 8.6 - 22.2 {
- Uranium 45.7 52.6 43.4 - 61.8 <
l Ba 133 Co-60 87.3 48.7 98.0 50.0 80.7 - 115.3 ) 41.3- 58.7 I Cs 134 35.0 40.0 31.3 - 48.7 Cs-137 51.3 49.0 40.3 - 57.7 Ru-106 184.7 252.0 208.6- 295.4(1) Zn-65 135.3 134.0 11.4 - 156.6 Jul. Water Gross alpha 19.3 32.0 18.1 -45.9 Gross beta 12.7 10.0 1.3-18.7 l Sr89 26.0 30.0 21.3 - 38.7 l Sr 90 18.7 20.0 11.3 - 28.7 Aug. Water H-3 10186.7 9951.0 8224.7 -11677.3 Air Filter Cs 137 14.0 15.0 6.3 - 23.7 l Gross alpha 29.3 35.0 19.4 -50.6 -l Gross beta 56.0 56.0 38.7 - 73.3 , I l Sr-90 16.0 20.0 11.3 - 28.8 Sep. Water Ra-226 10.1 10.0 7.4 12.6 Ra-228 9.8 10.2 5.6 -14.7 ' Uranium 31.9 35.0 29.8 - 40.2 ; Oct. Water 1131 81.3 79.0 65.1 - 92.9 1 U)- The vendor radiologicallaboratory received a letter from the EPA with this result. The EPA letter stated, "The Radiation Quality Assurance Program has been experiencing problems with Ruthenium 406 curisatly used in the Performance Evaluation (PE) Studies and in the Standards Distribution Program. If these problems can be satisfac- , tority resolved, this analyte will once again be placed into this PE Study. If the l l i l RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 31 1
'1
s 3' ' q o I problems cannot be resolved, the Ruthenium-106 will be replaced. Formal wnttero notice will be given to all participants in the ' gamma water PE Study before the Ruthenium 106 is reintroduced or replaced. At that time, new calibration standards will be available to all participants in the Gamma Water PE Study." The vendor radiological laboratory will continue to monitor this situation, but plans to talte no additional action. Table 5: 1994 Vendor internal crosscheck program for dosimeters e Date Sample Type Vendor Result .Known Value Nov. LIF-100 Chips 15.6 14.9 i 30.2 29.8 59.2 59.7 CaSo4:Dy Cards 14.9- 14.9 ., 30.8 29.8 1 58.9 59.7' l 15.4 14.9 31.4 29.8 60.1 59.7 Table 6: 1994 Vendor laboratory " spiked" sample results Analysis Known Acceptable Date Sample Type Result Value Range Jan. Water Co 144 2593.1 2692.5 1615.5 - 2961.8 Ce 144 1705.1 1749.8 1049.9-1924.8 Ce 144 55.4 49.0 29.4 - 59.0 Gross alpha 34.4 41.7 20.9 - 62.6 Gross beta 33.6 30.2 20.2 - 40.2 Gross alpha 66.8 83.4 41.7 -125.1 Gross beta 63.8 60.4 50.4 - 70.4 H-3 17080.0 17163.0 13730.4 -20595.6 Co-60 1514.0 1545.0 1390.5-1699.5 ' Cs 134 433.7 479.0 431.1 - 526.9 Cs 137 742.7 732.0 658.8- 805.2 Milk Cs 134 328.3 338.0 304.2 - 371.8 Cs-137 1019.6 1114.4 1003.0 1225.8 Cs-134 27.2 31.7 21.7 - 41.7 Cs 137 34.6 34.8 24.8 - 44.8 Sr-89 28.2 35.0 25.9 - 45.0 l J.' Sr-90 41.2 40.7 32.6 - 48.8 > Sr-89 9.5 11.9 1.9 21.9 : Sr-90 19.4 20.1 10.1 - 30.1 Air filter Gross beta 4.8 4.2 0.0 -14.2 l Cs 137 1.4 1.3 1.2 - 1.4 ; Feb. Charcoal 1131 1449.9 1452.8 1162.2-1743.4 ; Water 1131 76.4 90.9 72.6 109.0 : 90.2 90.8 54.5 -100.8 ! Milk l-131 40.4 43.6 31.6 - 55.6 !' 41.8 43.6 26.2 - 53.6
- Mar. Sediment H3 97.2 105.4 0.0 - 630.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 32 v v , *r-> a v--e n- -e-- - --
Analysis Known Acceptable Date Sample Type Result Value Range Water Sr-89 25.5 26.4 16.4 - 36.4 Sr-90 16.2 18.8 8.8 28.8 Apr. Water H-3 9847.8 9855.0 7884.0 - 11826.0 , Co-60 21.6 22.6 12.6-32.6 Cs 134 33.3 '33.6 23.6 -43.6 Cs 137 37.6 36.3 26.3-46.3 . Gross alpha 44.8 41.6 .'20.8-62.4 Gross beta 24.1 25.4 15.4 - 35.4 fAlik Cs 134 52.0 50.6 40.6 - 60.6 Cs 137 61.6 54.5 44.5 - 64.5 ' Air filter Cs 137 1.3 1.3 1.2 - 1.4 May Water Fe-55 56.7 58.5 38.5 - 78.5 Fish Cs 137 6.9 - 6.8 0.0-16.8-Sediment Cs 137 6.2 6.0 0.0-16.0 Jun. Water 1131 46.0 51.8 39.8-63.8 50.9 51.8 31.1 61.8 Gross alpha 20.8 23.4 11.7- 35.1 Gross beta 29.5 31.8 21.8 - 41.8 > Milk l131 51.7 51.8 39.8 63.8 51.3 51.8 31.1 - 61.8 Vegetation 1131 0.9 1.0 0.6 - 1.1 Charcoal 1131 1.9 1.8 0.0 13.8 Jul. Water H-3 24504.6 25019.0 20015.2 - 30022.8 Milk Sr-89 16.4 22.5 12.5 32.5 Sr90 25.3 25.4 15.4 35.4 Water Cs 137 240.8 221.5 199.4 - 243.7 Air filter Gross beta 7.9 8.3 0.0-18.3 Cs-137 1.3 1.3 1.2 - 1.4 Fish Cs 137 8.3 8.5 0.0 18.5 Oct. Water 1131 77.4 79.9 63.9- 95.9 85.5 79.9 47.9-89.9 92.5 95.8 76.6-115.0 98.2 95.8 57.5-105.8 Milk Cs 134 35.0 36.4 26.4 - 46.4 Cs 137 46.1 44.1 34.1 - 54.1 1131 65.2 63.' 51.1 76.7 68.4 63.9 38.3 - 73.9 Vegetation 1131 1.7 1.6 0.0 13.6 Sediment Cs 134 0.3 0.3 0.2 - 0.5
~
Fish Cs 137 11.6 12.1 2.1 22.1 Nov. Water Ni-63 1851.6 1931.0 1158.6 - 2703.4 Tc-99 63.2 66.0 46.2-85.7
- H-3 24099.2 24260.0 19408.0 29112.0 Excluding one parameter which the OEPA has subsequently withdrawn, the vendor labo-ratory has successfully completed their quality control samples. This is a continuation of excellent programs during the past two years, r
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 33
i i CONCLUSION No unusual radionuclide concentrations or exposure levels were detected during 1994. Atmospheric monitoring results were consistent with past results. The prevalent radionu-clide in air was beryllium 7 which is naturally occurring. Naturally occurring potassium 40 was detected in all terrestrial samples, as expected. Cesium 137 was detected in soll and is the result of fallout from weapons testing. The concentrations were similar to those measured in previous years and are not related to plant operation. There was no significant change in radionuclide concentrations at indicator locations for aquatic samples in 1994. Cesium-137 was detected in sediment. Results were within the range of past data. i Finally, direct radiation measurements are consistent with past data. l l 8 4 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 34
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I l 1 1 LAND USE CENSUS : j i b e b
]
LAND USE CENSUS 35
INTRODUCTION Each year a land use census is conducted to identify the locations of the nearest milk animal, garden (of greater than 500 ft2), and residence in each of the meteorological sectors. The Land Use Census is required by the PNPP Technical Specifications, Section .
. 3/4.12.2. The information gathered during the Land Use Census is used for off-site dose assessment and to update sampling locations for the Radiological Environmental Monitoring Program.
- The Land Use Census is conducted by traveling all roads within a five-mile radius of the plant site, and recording and mapping the location of the nearest resident, milk animal, and vegetable garden in each of the meteorological sectors around the plant that are over land. The 1994 Census was conducted on July 14,15 and 18. The location of the nearest residences, vegetable gardens (larger than 500 square feet), and milk producing animals were recorded. Produce growers, and recreational areas were also recorded.
A survey update was also completed this year. It included identification of all public drinking water facilities, fish harvst and population within 50 miles of the plant. The information has been tabulated below; garden, residence and milk animal locations are plotted on the map in Figure- 1. Note that the W, WNW, NNW, NW, N, and NNE . sectors extend over Lake Erie and therefore were not included in the survey. DISCUSSION AND RESULTS in Deneral, the predominant land use within the survey area continues to be rural / agricultural. There were no changes in nearest residences within five miles of the plant. Table 1 lists the nearest residence by sector. The residence with the highest X/O (highest dispersion factor and therefore highest possible calculated dose) is located at 3121 Center Road, in the south sector, approximately 0.9 miles from the plant. This is the same residence identified in the 1993 Land Use Survey. Table 1: Nearest residence by sector
)
Sector Location Miles XA;) Value Map Address from PNPP (Sec/m3) Locator NE 4385 Lockwood Rd 0.8 2.17E-6 1 ENE 4602 Lockwood Rd 1.0 1.13E-6 2 E 2684 Antioch Rd 1.1 6.77E-7 3 ESE 2774 Antioch Rd 1.2 4.44E 7 4 SE 4495 N. Ridge Rd 1.2 3.89E-7 5 ^ SSE 3119 Parmly Rd 0.9 1.89E-6 6 S 3121 Center Rd 0.9 2.25E-6 7 : SSW 3850 Clark Rd 0.9 1.11 E-6 8 l SW 3440 Clark Rd 1.2 4.98E 7 9 WSW 2815 Perry Park 1.0 1.72E-6 10 LAND USE CENSUS 36
-. . .- - . . . ~ . . . .. - ~_ -
, -< 1
- The following changes in nearest gardens were recorded in the 1994 census:
o.. ENE Sector A new garden was identified at 4650 Lockwood Road. o E Sector - A new garden was identified at 2740 Antioch Road. o o SE Sector - A new garden was identified at,4679 Middle Ridge Road. o ' SSW Sector - A now garden was identified at 3515 North Ridge Road.' - o WSW Sector A new garden was identified et 2975 Perry Park Road. .
~
j Table 2 lists the nearest gardens that occupy at least 500 square feet. The location with L the highest D/Q (highest calculated deposition) value was 3121 Center Road in the south ; sector. This is the same garden identified in the 1993 Land Use Survey.' l
- Table 2: Nearest garden by sector .
Location Miles DK) Value Map Sector Address , from PNPP per m2 Locator . , 1 t NE 4398 Lockwood Rd 0.8- 1.09E-8 11 ENE* 4650 Lockwood Rd 1.2 4.11 E-9 12 , E* 2740 Antioch Rd 1.2 4.56E-9 13 ESE 2774 Antioch Rd 1.2 3.41 E-9 4- i SE* 4679 Middle Ridge Rd 1.9 1.31E 9 14 SSE 3119 Parmly Rd 0.9 1.23E 8 6 S 3121 Center Rd 0.9 1.31 E-8 7 4 SSW* 3515 N. Ridge Rd 1.7 1.19E-9 '15 SW 3440 Clark Rd 1.2 2.24E 9 9 WSW* 2975 Perry Park Rd 1.2 2.31 E-9 16.
- Indicates a new location for 1994 A milk animal (goat) was recorded during the 1994 census. There had been no milk '
animals within a five mile radius of the plant since 1991. At the time of the survey the goat was not being milked and would not be milked in 1994. For this reason, the location was not added to the REMP. Table 3: Milk Animal Location Miles DQ Value Map , Sector Address from PNPP ' perm 2 Locator E 2874 Burns 4.1 4.81E 10 17 q c Produce growers are listed in Table 4; recreational areas are listed in Table 5. Survey . . update information on public drinking water facilities is included in Table 6. Fish harvest and population are discussed below. ; LAND USE CENSUS 37 .;
.s
-1 i
' Table 4: Produce growers within the vicinity of PNPP Sector Name and Address of Facility Miles DA;) i from PNPP ENE Shreve Farm,2431 Antioch Rd 1.2 4.1E 09 )
ENE Gerlica Farm,4860 Lockwood Rd 1.5 2.8E 09 l ENE Rainbow Farms, Townline Rd 1.9 1.9E 09 ENE Rutand Farm,2210 Haines Rd 2.0 1.7E-09 ENE Twins Creek Farm,2299 Haines Rd 3.2 7.4E-10 I E Orosz Farm,2674 Antioch Rd 1.2 4.6E 09 i' E Sabo Farm,5674 N. Ridge Rd 2.9 8.9E 10 E Resident,6325 Middle Ridge Rd 3.9 . 5.3E-10 ! E Woodworth Farm, Middle Ridge Rd 4.6 3.9E 10 ; E Wayman Farm, Hubbard Rd 4.8 3.6E-10 E Hub Ridge Market, Rt. 528 4.8 3.6E-10 ESE Secor Nursery, N. Ridge Rd 1.8 1.7E-09 , ESE Resident,5674 Middle Ridge Rd 3.2 5.6E-10 ESE Resident,5936 Middle Ridge Rd 3.3 5.3E-10 ESE Resident,6030 Middle Ridge Rd 3.9 3.9E-10 ESE Hart's Acres, Rt 528 5.0 2.5E 10 SE* Resident,3815 Townline Rd 3.0 5.9E 10 SSE Peg's Produce, Rt 84 3.2 3.7E-10 l S Resident,4030 Middle Ridge Rd 1.5 2.4E-09
]
S Brookside Farm, Middle Ridge Rd 1.7 2.0E-09 SSW Golding Farm, North Ridge Rd 1.7 1.2E-09 ) i SSW Champion Nursery, North Ridge Rd 1.8 1.1 E-09 SW Golding Farm, Perry Park Rd 1.5 1.5E-09 SW West Orchard & Fruit Market 1.6 1.4E-09 . Perry Park / Clark Rds ; SW Resident, 3191 N. Ridge Rd 2.4 6.7E-10 - SW West Orchard & Fruit Market, N. Ridge Rd 2.7 5.5E 10 j SW Garden Center, North Ridge Rd 3.6 3.3E-10 SW* Sycamore Row Farm,252 Hale Rd 4.2 2.5E 10 q SW* Resident, 2503 Hale Rd. 4.2 2.5E 10
- Indicates a new location for 1994.
I LAND USE CENSUS 38 1
m t N/ Table 5: Recreational areas Sector : ;Name and Address of Facility Miles kom PNPP NE North Perry Pk, Lockwood Rd 0.7 - N. Townline Pk, Townline Rd - !
'ENE 2.3 - .n ENE Lake Metro Pk, Lockwood Rd . 1.7 ENE' Chapel Cove Pk, Chapel Rd ' 3.2 ENE~ Tuttle Pk, Tuttle Park Rd 3.7. I ENE Madison C.C.. Chapel / Green Rd 4.0 S Lake County YMCA Outdoor Center, 4.6 4540 River Rd SW Fairway Pines Golf Course, Corner of Blase Nemeth U.d Bacon Rd 4.8
- WSW Perry Township Pk, Perry Park Rd 1.1 l WSW Camp Roosevelt, Perry Park Rd 1A Based on 1990 census data, the population within 50 miles of the plant is 3,464,671.
Information on fish harvest was obtained from the Ohio Department of Natural Resources :; and includes both sport and commercial data. The annual sport harvest of major fish species for the last five years is shown in Table 6. Annual commercial harvest of major , fish species for the last five years in shown in Table 7. Public drinking water facilities > within 50 miles of the plant are shown in Table 8. l Table 6: Annual sport fish harvest (in thousands of pounds of fish) , Species 1989 1990. 1991 1992 1993 Walleye 10,372 6,831 5,170 5,997 7,428 Yellow perch 2,473 551 933 722 -876 . White bass 217 69 64 31 85 Smallmouth bass '43 54 66 66 77 Freshwater drum 60 63: 133- 63 ~54 Channel catfish 12 56 30 63 54
- ; White perch 148 188 175~ 93 36 l Tabel 7: Annual commercial fish harvest (in thousands of pounds of fish)
Species 1989 1990 1991 1992 1993
. Yellow perch 1,700 1,591 '684' 372 '344-White bass 549 - 392 445 382 225 Freshwater drum 485. 640 505 604 774 i Channel catfish 342 365- 376 333 326 :
White perch 521 796 1,007 848 338 Suckers 39 41 41 55 53 Carp 895 1,190 1,063 1,824 1,176 - LAND USE CENSUS 39- ,
, - _ .,~ _ _ . . . _ ~ . _ - . . . _ _ _ _ . . _ _ ___ . . _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ . _ _ _ _ - _ .
Table'8: Public drinking' water faciltles
- County Facility name ; i Water source .
Ashtabula Andover Village Well
' Orwell Village . Well ' " Roaming Shore Village Roaming Rock Lake 4 Rock Creek Village : Grand River.
City of Conneaut . Lake Erie
- Camplands Water Company Well Ohio American Water Service Lake Erie
.Cuyahoga' City of Berea Rocky River :)
City of Cleveland Lake Erie .J Chagrin Falls Village Well j
.Geauga - Burton Village Well l Chardon Village. Bass Lake 1 Middlefield Village Weil Lake Fairport Harbor Village Lake Erie ]
Lake Co. East & West Water Dist.' Lake Erie .l Ohio Water Service Lake Erie : City of Painesville Lake Erie ' Mahoning Milton Township Well i Portage Mantua Village Well i Windham Village Well City of Kent Well City of Ravenna Lake Hodgson Fairlane Water Company Well Citizens Utility - Well Summit Lakemore Village Well j City of Akron Lake Rockwell i City of Cuyahoga Falls Weli ! Hudson Village Well i Copley Square Water Company Well City of Barberton Wolf Creek Reservoir ;j Peninsula Water & Sewer Well , Shepard Hills. Water Company - W ell : Trumbull West Farmington Village Grand River City of Courtland Well City of Hubbard Well City of Newton Falls Mahoning River City of Warren Mosquito Reservoir ! Shenango/Masury Water Company Shenango River i Mercer (PA) Shanango Valley Water Company Shenango River ' Sharpsville Boro Water Company Shenango River
. Reynolds Water Company. Big Run River 'j Greenville Municipal Water Shenango River Crawford (PA) Tuttle Point Pymatuning Pymatuning Reservoir Cambridge Springs Borough French Creek )
Erie (PA) Erie Bureau of Water Lake Erie -] I LAND USE CENSUS 40 l
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4 - e _ __m.- ~a w a 4 e K a 4.- 9 O CLAM / MUSSEL MONITORING I I 1 CLAM / MUSSEL MONITORING 43
c l 4 INTRODUCTION Sampling for benthic macroinvertebrates (clams and mussels) has been conducted in .
' Lake Erie in the vicinity of the Perry Nuclear Power Plant (PNPP) since 1971. The clam /
mussel program currently focuses on two species: Corbicula fluminea (Asiatic clam) and ;
.. Dreissena polymorpha ~ (zebra mussel).
, CORBICULA PROGRAM The initial monitoring program specifically for Corbicula was developed by NUS Corporation for PNPP in response to an NRC bulletin and concerns of the Atomic Safety
~
and Licensing Board. The' current monitoring program was developed in conjunction with i Aquatic Systems Corporation and incorporated into the Environmental Protection Plan (Operating License Appendix B) in July,1988 by License Amendment 15. The program consists of periodic sampling of areas at both the PNPP and Eastlake Power Plants. Its 1 purpose is to detect Corbicula, should it appear in the study area. No Corbicula have ever been found in any sample collected from PNPP or from Lake Erie in the vicinity of PNPP. Two Corbicula were found in a sample collected from the Eastlake plant in June,1987. No Corb/cula have been found in any other sample collected since that time. A more detailed program history can be found in the 1986 and 1987 PNPP Annual Environmental Operating Reports. Monitoring -1 Samples were collected quarterly in 1994 from in-plant locations at PNPP shown in , Figure 1, and semiannually from the vicinity of the Eastlake Power Plant at locations ' shown in Figure 2. Sample collection dates are listed in Table 1. Table 1: 1994 Corbicula sampling dates and locations .i Date Sample Location 1/13 Service water (SW) and Emergency Service Water (ESW) forebays and , trash baskets l 4/ 6 SW and ESW forebays and trash baskets l 4/13 Cooling tower basin ! 6/ 9 Lake Erie in the vicinity of the Eastlake Plant 7/22 SW and ESW forebays and trash baskets 9/12 Lake Erie in the vicinity of the Eastlake Plant 10/14 SW and ESW forebays and trash baskets Weekly inspections of PNPP property shoreline, weather permitting ) l' All samples were collected by Ponar hand dredge, hand scoop, or scraper. They were
- examined for bivalve shells and fragments, which were then identified to the lowest possible species.
In addition to sample collections, plant components that use raw water are inspected whenever opened for maintenance or repair. Also, active communications were main-tained with other agencies involved in benthic macroinvertebrate monitoring on Lake Erie. Several publications developed and distributed specifically for the purpose of providing information on bivalves are used as resources. CLAM / MUSSEL MONITORING 44 i
;7 m is ji. ,
i sfc > Results No Corbicula were found in any sample colected during the 1994 monitoring program. All . bivalves collected are listed in Table 2.-
-Table 2: Blvelves collected during the 1994 Corbscula monitoring program
-PNPP EASTLAKE ..
Dreissena polymorpha x x-Dreissena bugensis x x
.Pisidium caeseratinum x x Pisidium compressum - x Pisidium tilljeborgi- 'x.
Pisidium hurugineum ~x - Pisidium amnicum x Pisidium sp. x x Sphaerium striatinum x Sphaerium transversum ' x' x' r Sphaerium comeum x Sphaerium sp. x x e
' Unionidae . x :
Anodonta sp. x Conclusions j The collection in June 1987 was the first indication that Corbicula are slowly spreading , into the central basin'of Lake Erie. However, it has not been demonstrated that the presence of these clams is creating any operational problems at the Eastlake Power Plant ' or at PNPP. 1 DREISSENA PROGRAM :l ! Zebra mussels were first discovered at PNPP in September 1988. The initial collection of-19 mussels was made as part of the Corbicula monitoring program. The Dre/ssena pro-gram began in 1989 with monitoring and testing. The current control program was de- .l signed and implemented in 1990. 4 Monitoring ; in addition to visually inspecting plant raw water systems when they are opened for H maintenance or repair, monitoring methods include the use of commercial divers, artificial substrates, sidestream monitors, and plankton nets. : Commercial divers monitor mussel infestation when they are inspecting forebays, basins, . and the intake and discharge structures. They have also been used to take underwater videotapes of the water basins and intake tunnel. Artificial substrates include concrete blocks suspended by rope into the plant service water basin. The substrate is removed .- ! weekly for inspection for settlement. Sidestream monitors are flow-through containers that receive water diverted from plant ; systems. PNPP used them in two in-plant locations during the mussel season, May -i through October. They are fitted with slides and inspected we6kly for veliger settlement. A ; plankton net is used to obtain weekly samples of incoming service water that are sub- ! sequently examined for veligers. 1 i CLAM / MUSSEL MONITORING 45 J I J
.. : . .w...:.- .
l g , l Resu4s of the veliger monitoring program for 1994 are shown in Table 3. Samples were - collected from the service water basin using vertical tows with an 80 micron mesh plank-ton net. Treatment > Chemicals used for mussel control in 1994 included chlorine and a commercial mollusci-cide. The system provides chlorine to plant service water, emergency service water, and
.- circulating water systems. Sodiun sulfite is added to plant discharge water to dochlori-nate it before discharge to Lake Erie.
Table 3: Result:; of the 1994 Perry Nuclear Power Plant veliger sampling program. , Date Miter Lake Temp (F) 5/31 0.0 59 6/7 0.0 62 - 6/14 0.0 63 6/21 < 1.0 64 - 6/28 < 1.0 66 7/5 34.7 66 7/23 8.2 74 7/19 4.2 72 7/26 12.9 75 > 8/2 2.9 75 8/9 2.4 l 72 8/16 < 1.0 70 8/24 2.6 71 8/30 2.6 72 ! 9.6 1.3 71 9/13 0.0 - 69 9/20 0.0 69 The use of commercial mNiuscicides requires approval of the Ohio Environmental Protection Agency (OEPA). The chemical selected for use at Perry Nuclear Power Plant in - 1994 was didecyl dimethyl ammonium chloride. A treatment was applied on ' Sept. 22,1994 near the end of the settlement period. The active ingredients were detoxi. .I fled by adsorption onto bentonite clay prior to discharge into Lake Erie. Results The effectiveness of the Intermittent chlorination treatment has been determined in sev-eral ways. First, eleven visual inspections of raw water system components were con. l ducted in 1994. . In addition, settlement monitors were inspected weekly for new - settlement. No live settlement has been found in any plant component or in the settlement monitors to date. , i The effectiveness of the application of the commercial molluscicide was measured by . observing mortality of mussels placed in a flow-through container placed in plant service' , water and subjected to the chemical treatment. Mortality observed in the flow-through ; container was 100%. To date PNPP has had no problems relaid io zebra mussels. i 1 d CLAM / MUSSEL MONITORING 46 ! l
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Conclusions Perry Nuclear Power Plant has t'aken the approach that the best method for avoiding , problems with zebra mussels is preventive treatment of plant water systems. The current - program of monitoring and chemical treatments will be continued to minimize the possibil-ity that PNPP will experience future problems due to zebra mussels. . 3 9 1 3 Y i l I i 1 1 l l l l l CLAM / MUSSEL MONITORING - 47
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l l l AERIAL REMOTE SENSING l 1 i i i i i 4 4 k l*
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AERIAL REMOTE SENSING 51 ,
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1 I INTRODUCTION Aerial remote sensing is a method of monitoring the plant area environment by examining ) photographs taken from an airplane.'It is used in the vicinity of PNPP to monitor for vegetative stress. Vegetative stress is any disturbance of the normal growth cycle .of
. vegetation which results in changes in appearance. it can be caused by a variety of both natural and man-made factors including insect posts, disease agents, drought, pollution, I
mechanical damage, or salt deposition.
~*
Salt deposited from the cooling tower plume would be the most likely cause of vegetative stress attributable to PNPP. Solids (salts) dissolved in the lake water used in the cooling tower may be contained in the droplets that make up the plume. As the droplets settle to i the ground, the salts may accumulate either in soils or directly on foliage. Stress can then ! result from 1) the direct toxic effects of the salt,2) a decrease in the availability of soil moisture to the plant, or 3) the alteration of the mineral balance in the plant tissues. Aerial remote sensing has been conducted at PNPP regularly as a requirement of the Environmental Protection Plan (Appendix B of the Operating License).-It was first con. ducted in 1987 and followed in 1988,1990,1992 and the final year of the study,1994. PROGRAM in order to determine whether the operation of the PNPP cooling tower has impacted the surrounding vegetation, the site and vicinity within one kilometer of the cooling towers in all directions were aerially photographed to detect and assess the significance of damage (or lack of damage). The photography was done by aerial overflight on August 23,1994 1 (detalls are listed in Table 1, flight lines are shown in Figure 1). l 1 Table 1: Detells of the 1994 photomission l Item Data ' Date August 23,1994 Time 1135 to 1?.20 Eastern Daylight Savings Time Film type Aerochrome infrared Weather Clear with a few scattered clouds Altitude 3625 ft. to 3700 ft. above ground level ! Camera / lens model Jena MRB 15/2323 I Camera focal length 152.026 mm . l Shutter Speed 1/400 second l Aperture f 4.5 l Scale 1 in. - 500 ft. Low altitude color infrared photography is used in order to allow potentially stressed vegetation to be identified. Healthy green plant tissue is a strong absorber of visible light. 'l 11 appears as red on the infrared film. Stressed areas can be identified by observing l different hues on the photographs as well as noting changes in patterns or textural ) characteristics. -! Once developed, photographs were inspected to check for quality of color and resolution, and to identify those areas where the need for more detailed inspection was necessary. They were also compared to previous years' studies to determine whether there were any 1 sigalficant changes. I l I , AERIAL REMOTE SENSING 52 g ,. ,.-.-w
1 l l i Areas identified for further inspection were located on maps and compared to previous data and walked down in the field and inspected if necessary. RESULTS i There has been no adverse environmental Impact from the operation of the PNPP cooling - tower. Ten areas were identified as showing variations in spectral signatures (see Figure 1). One . 1
^
of these locations occurred within the area predicted to receive maximum deposition. All areas exhibiting potential stress were ground truthed and compared to 1992 photos. The variations h1 spectral signature in the ten areas identified in the 1994 study were attributable to a variety of factors: stress due to wind damage and root exposure In trees along the lake shore and ravines - variations in species composition in the arboreal canopy (different species reflect light differently, which results In different shades on the infrared film) arboreal mortality due to over maturity ANALYSIS OF IMPACT Historically, the vegetative stress that has been observed in the vicinity of PNPP has been attributable to factors unrelated to operation of the cooling tower. This remains true for 1994. lI l l l l AERIAL REMOTE SENSING 53 l
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CLEVELAND EIICTRIC III.UMINATING CO.
'""' PERRY NUCLEAR PLANT
) TRUTHED LOCATIONS c4muu asso so sin una infr ri romo aux:ar so o rr mman.rar sc.ta : 0o-Daft QF PED 10GRAPWT s.23 94 FUCAL 1ENGTW 152.022 Mu FHOTO SIDEI KALS l'e2000' 95 ~0 418 0 4 20 -O/ _~
e 4 HERBICIDE USAGE 1 i l i I l 4 HERBICIDE USAGE 55
Because the PNPP site is home to several special habitat areas, like that for the spotted ! turtle, herbicides are used sparingly on site. An application must be made to the PNPP 'l Environmental Monitoring Element prior to spraying to ensure that only approved chemi- ! cats are used, and on;y in approved areas. l
- Table 1 provides a compilation of herbicide usage at the PNPP for 1994. All usage was in )
compliance with Ohio Environmental Protection Agency regulations. No adverse environ- l mental impacts as a result of this usage were noted during weekly site environmental I
, inspections. Surflan AS and Round Up were used in equal portions to make up the total l quantity except where noted, j Table 1: Herbicide usage I l
Date Total i Applied Location Acres Gallons i 5120 E field and outer perimeter (1) 3.86 3.9 l 61 3 E-fleid and outer perimeter 3.86 7.7 I 6/4,8,17 Unit 1 graveled areas 5.30 10.6 6/2,22 Unit 2 graveled areas 20.60 41.2 8/18 Landscaped yard areas (2) 2.00 5.0 (1) - Surflan only (2) - Round-up only e 6 HERBICIDE USAGE 56
o SPECIAL REPORTS , l 4 1 1 i i l
)
l l l SPECIAs. REPORTS 57
l NONCOMPLIANCES NPDES Permit Noncompliances The National Pollutant Discharge Elimination System, or NPDES permit, is issued by the Ohio Environmental Protection Agency (OEPA). It establishes monitoring requirements and limits for discharges from the plant. It also specifies the locations from which the plant is allowed to discharge. There were no NPDES noncompliances in 1994. EPP Noncompliances The Environmental Protection Plan, or EPP, is a part of the PNPP Operating License. It requires non-radiological environmental monitoring programs and reporting. There were no EPP noncompliances identified in 1994. UNREVIEWED ENVIRONMENTAL QUESTIONS All proposed changes in plant design or operation, as well as tests or experiments con-ducted during 1994 were reviewed for potential environmental impact In accordance with the EPP and administrative quality assurance procedures. The reviews ensured that no changes were performed which could cause an adverse environmental impact. Therefore, there were no potentially significant unreviewed environmental questions in 1994. NONROUTINE REPORTS ; There were no nonroutine reports in 1994. se I e SPECIAL REPORTS 58
l l i l APPENDIX A: 1994 RADIOLOGICAL ! ENVIRONMENTAL MONITORING PROGRAM DATA
SUMMARY
a 1 l l 1 I I I i l l 1 J J APPENDIX A: 1994 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM DATA
SUMMARY
59
)
i
_.,.i RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
SUMMARY
Name of Pacility: PERRY NUCLEAR POWER PLANT Docket no. : 50-440/50-441 Location of Pacility Lake County Ohio Reporting period : 9400
+- b1LE&qSS-QETA. _ _ + +----- _+. +_ -- + +
I i 1 1 I I l l I i 1 -) I i I I l- 'l I I I I I I Location with Nighest '" l l Type and l All I l l l l Annual Mean l l Medium l Tot. (n) l Lower l Locations l l All +- -+ -
-+ All l and l Analysis l Limit l (Indicator a Control) l Indicator Locations IDist. .I l Msamurement IPerformedl (LLD) l Mean (1) (Range) l Mean (1) (Range) l Direct l l Mean (1)
(Range) l Control Locations. l Mean (1) (Range)
+- +-- -+-- .+ l l
+- -
+-------+- __+- =+
l APTB l G-BETA l .0075 l 0.02 l 0.02 lPCI/CU.M. l 364 l 1 5 l 0.02 1 0.02 l l (0363/0364) l (0311/0312) l 0.6 l (0051/0052) l (8052/0052) l l I I I I O.00-0.04 I O.00-0.04 I sw 0.00-0.03 I 1 0.01-0.03 1-1 1 1 1 I I I I l l I I I I I 1 I I I I i .l-I I I I I I I I I I l' I I I i l I i i i I I I I i i 1 -1 1 1 I I I I 1 I I I I l- 1 1 1 1 1 I I I I l-1 I I I I i I i I I I I I I I I 1 1 1 I l I i l I I 't I I I I
! 1 I I I- I 1 I I I I I I I I I I i l l l l l l I I I I I I -l l- .I I I I 1 I I I I i 1 I I I I I I I 1 I I I I i I I I 1 I I I I I I i 1 I
I I I 1 I I I i l I I I I I I I I I I I I I I l l l I I I I l l I I I I I i I i 1 1 1 1 I i i l i i
+ + +--- _ - - + _ _ --
+- +--.
I __+ +. + 1 - The ratio of-positive results to the number.of samples analysed for the parameter of interest. LLD - Lower Limit of Detection.
em a, RADIOLOGICAL ENVIRONMENTAL MONITORING FROGRAM
SUMMARY
Name of Facility: FERRY WUCLEAR FOWER PLANT Decket me. 50-440/59-441 Location of Facility : Lake County Ohio Reporting period : 9400
+___ ATA_ICOI!HL_+ + - - - - -
+ +- __
+ +
1 1 I I i 1 1 I I I I I I I I I l l l l l l Location with Eighest l l l l Type and l l All l l Annual Mean l l l Medium l Tot. (n) l Lower l Locations l All + + + All ..I l and l Analysis l Limit l (Indicator s control) l Indicator Locations lDist. l Mean (1) { Control Locationa l l M3asurement lForformed] (LLD) l Mean (1) (Range) l Mean (1) (Range) l Direct l (Rangel l Meam (1) (Bange) l-
+----. --+-- + +- + -
+ + . ---+ -+
I AI I I-131 I .oS I I I I i I lFCI/CU.M. l 364 l l LLD l - l - l - l - l-1 I I I I I I I I I I I I I I I I I I I I I I I I I l-1 I I I I I I i i 1 i I I I I I i 1. 1 I I I I I I I I I I I I I I I l' i 1 1 1 1 I I I I 1 I I i 1 1 1 I I I I i 1 I I I I I I-1 I I I I I I I l-l 1 I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I i 1 1 I I I I I I I I I I I I I I 6 I I I i 1 I I I I I i i i I I I I i 1 1 I ! I I I -l I I i I i I I i i i I i i i l I I i l i i i i l i l I I i l i i l i l I i i I I I i I I I i I I 1 l I I I I I I I
+___ + --+ + + .-- + . + . - + +
1 - The ratio of positive results to the number of samples analysed for the parameter of interest. LLD - Lower Limit of Detection. I i _
+. ,
_e-- . l
< 8 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
SUMMARY
Name of Facility: PERRY NUCLEAR POWER. PLANT Docket no. 5o-44o/5o-441 Location of Facility : Lake County Ohio Reporting period 94co
.. AIR GAMMA SP,FC _ . ,
I I I I I 1 I I I I i 1 I L l -1 l l l l l l Location with Nighest l IType and l All I -l l l l Annual Mean l- l Medium l Tot. (n) l Lower l Locations l All + +- + All l l and l Analysis l Limit j (Indicator s control) l Indicator Locations lDist. l Mean (1) l Control Locationa
)
l Maasurement. - +IPerformedl (LLD) l Mean (1) (Range) l Mean (1) (Range) l Direct'l (Range) l' Mean (1) (Range) 1 j.
._+- +- -
+- _ .+ __+ + -+
l APTG l BR-7 l NA l o.o? IPcI/co.M. l o.o? l 4 l o.os l .o.o? l l 2s l l {co2s/coas) l too24/co241 l o.7 I (coo 4/ coo 4) l (coo 4/ coo 4) l l l o.os-o.1o l l I- c.os-o.1o Is I o.o7-o.os o.os-o.os-I l I I i i 1 l i co-se 1 NA l I i i l l l l l l l 2s 1 I LLD 1 - l - 1 - l I I I I I l I I I I I i i I I i i I I co-60 i NA I I l { [ [ j 3 2s l LLD ] 1 l l - 3 I - l - l-1 I I i i i I i I I I i 1. I l 1 l l cs-134 I .o37 I I I l-l l 2e I LLD I - I l - I l .I l - I --
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,1 .+-- i l l l
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- .m
~ O v RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
SUMMARY
Name of Facility: PERRY NUCLEAR POWER PLANT Docket no. t 50-440/50-441-i Location of Facility. : Lake County Ohio Reporting period 9400
, PRECIPITAT_I_Of_i TRITI_L?f, , _. ,__ _ _ _ _ , . __ _,
I I I I I I- 1 I i 1 1 1 I I I I l l l l l l Location with Nighest l j' l l Type and I l All l Annual Mean Medium l l l l l Tot. (n) l Lower l Locations l All + -+- + All l l and l Analysis l Limit l (Indicator & Control) l Indicator Tocations lDist. l Mean (1) l Control Locations l l Mzasurement l Performed l (LLD) l Mean (1) (Range) l Mean (1) (Range) l Direct l (Range) l Mean (1) (Range)- l
+--.. + -+ + -+- + - - + + .-+
l TRITIUM l N3 l 1500 l l l l l l lPCE/L I 72 I I LLD l - l - I - l - l 1 I I I i 1 I I I I I I I .1 I I i i 1 1 I I I I I i 1 I I I I I I I I I I i I I i i i i I , 1 I I I I I I I I I I I I I i 1 I .I I I I I I I I i 1 1 1 1 1 I I I I I I I I I I I I I I I 'l i I I I i 1 1 I I I I I I I I I I I I I I I I I I I I i i I i l I ! -1 I I I I I i l I i i i i I : I I I I I I I .I i i 1 1 I I I i i i I I i I I 'l i I i .I-1 I i 1 i i I I i i i i l I i 1 i l i 1 i I 1 ? I I I I I I i 1 I I I I I I I i 1 'l l- 'l i I I I I I I I I I I I I I I -I I I I
+ - -+- +--- + -
+-- .+ ___+- _.+ __+.
1 - The ratio of positive results to the number of samples analysed for the parameter of interest. LLD - Lower Limit of Detection.
,, __ +- ~.m. . , -, . .- . . _ , . ,,. - -. . - , . . , - , ,
2 ,
* . m
-e RADIOLOGICAL ENVIRONMENTAL McNITORING PROGRAM S UMKILRT Name of Facflity: PERRY NUCLEAR POWER PLANT Docket no. 50-443/50-441 Location of Facility : Lake county Ohio Reporting period : stoo l
+ EBE91FJJAnQti GEOSS_#TA . , , _ _, _,. _ _ , ,
1 I -1 I I I I i l i l i l i l i I i l l I I Location with Nighest i I I IType and i I All I [- Annual Mean Medium Locations +
.I l-1 ITot. (n) 1 Lower i 1 All + + All 1-I and IAnalysis I Limit'l (Indicator & Control) 1 Indicator Locations IDist. -l Mean (1) l Control Locations 'l'
,1 M3asurement _+ IFerformed[ +- (LLD) e__ i Mean (1) (Range) l- Mean (1) (Range) IDirect I (Range) l Mean (1) (Range) .I'
+ _+_-
-_-+ . + --+
1 prs I o-sETA I3 4.77 4.7s 1 1 I 3 I s.s7 I 4.7s -1 IrCI/L 1 12 1 I (oo72/co72) I (ooso/coso) I 1.o I (oo12/so12) 1- (oo12/co121_ l i I I i 1.4o-1s.30 1 1.4o-is.30 I sE 1 2.1o-1s.30- 1 -1.4o-s.2e .I I i l l I -1 1 1 l 1 1 I I I I I I .I I I I I I I I I I i l 1 I I I I I I I I I i -l i I I I I I I I I I I .I I I I I I -l 1 1 I i ll l l 8 l e 1. 1 I I l I l 1 1 i 1 I I l'- l' I I l I I i I I 1 i l I I I I I I I I I I I I- 1 1 I l i I I I I I I I I I l- 1 I I I I i I i i 1 I i 1 I I i 1 1 I. I I I I I I I I I I I I I I I I i 1 1 I I I I I I I I i I 1 I I I I I I ! 1 l 'l i I I I I I 'l I I I I l-1 I I I I I I I I I I I I I i I I I- 1 1 1 I I 1 l 1 I I l-
+ + - + +
1 l I i
+- .+ _+ + -
.+
1 - The ratio of positave results to the number of samples analysed for the parameter of interest. LLD - Lower Limit'of Detection. _ _ _ _ _ _ _ _ _ _______.__.______.___.,m._ . _ _ _ _ _ _ _ _ _ _ . _ . - _ _ . _ _ _ _ - _ _ _ _ _ _ . _ _ _ _ _ _ _ _ _ , _ ._ ._m m__ _ _ --2 . __4. . - , - . - , u .w . . - 6w.---= 4e e_e n , . - - - - .
RADIOLOGICAL ENv!RONMENTAL MONITORING PROGRAM
SUMMARY
Name of racility: PERRY NUCLEAR POWER PLANT Docket no. t 50-440/53-441 Location of Pacility : Lake county chio Reporting period 9400
. EBSCJU_TAUQU GMtfA.4PE____. _
1 I I I I I i l I I .I l 1 1 i I l' l l l l Location with Nighest-l l Type and l 1 l l l All l l Annual Mean l l Medium l Tot. (n) l Lower i Locations All + l-l +-- + 'All l l and l Analysis l Limit l (Indicator s control) 1 Indicator Locations lDist. l Mean (1) l control Locatiema' l l Maasurement IPerformedl (LLD) 1 Mean (1) (Range) l Mean (1) (Rang *) l Direct l (Range) [ Mann (1).(Range) l'
+-- .+ +-- +- +. +
PRG _+- .+- -- - +- 1 g mA-14o 1 45 l l IPcI/L t 72 l l LLD 1 - l l l l. t 1 1 - I -- 'l
! I I I I I 8 I I 1 1 1 I I i I J co-se i 11 1 I -1 I 1
i l 1 72 l l LLD l - l - l i l - ' l-1 l i i 1 1 I I I l i I I I I l I ._ i i co-80 1 11 1 1 I I 1 I 72 I I LLD I l-I - I - I - I - 1. I I I i I I I i 1 1 1 1 1 I I I I I I cs-134 l 11 l l l l l I l l 72 ' l LLD t
'l l -'
l - l - l_ - l l 1 I I i l I I i i i I I I l l I es-137 I I I 1 13 l l l l l 1 i 72 l 1 LLD -- 3-1 I - I - l - I I I I I I 1 I I i 1 l i i 1 I I I I rE-59 1 22 I I l l l l l I 72 I LLD l _l I I - - I 1 I I 1 - l - l I I I _l i I i l i I I I I I l l LA-140 l 11 l l l l -l. I j. 1 I 72 I I LLD 1 - l - l - 1 -
-1; ,
1 I i 1 1 I l i
-1 I l- I I I
.l ------- __+. +-. --+ + ,I
+- .I . - ,I 1 - The ratio of positive results to the number of samples analysed for the parameter of. interest.
LLD - Lower Limit of Detection.
, , , . . , , , . , . - - . , , e ,-- v *- v'"~" ^'
" ' ^ * ' ' " ~ * ~~
s 3 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
SUMMARY
s Name of Facility: PERRY NUCLEAR POWER PLANT Docket no. : 50-440/50-441 Location of Facility : Lake County Ohio Reporting period 9400
+.ERECLEIIAT10#.faAlftm_SyE_C .___ .__ _
I I I I I i l i I I l- I I l I I I i l 1 Location with Nighest 1 I l -1 l l Type and l l All l l Annual Mean l Medium l l ITot. (n) l Lower i Locations l All + +- + All'
} and l Analysis l Limit I (Indicator & Control) l Indicator Locations lDist. l l Mean (1) l Control Locations l l M3asurement l Performed l (LLD) l +-
Mean (1) (Range) l Mean.(1) (Range) l Direct I (Range) l Mean (1) (Range) l
--+ +- + + + +-- + +
l PRG l MN-54 l 11 l l 1 l lPCI/L l 72 -l I LLD l - 1 l 1 1-1 - l 1 1 I I I ll l 1 1 I I I I I NS-95 I .I I I I l 11 l l H l l l l I 72 I I LLD I - I - 1 - 1 - l-1 I I I I I I i 1 1 I I I i 1 I I I I I EN-65 l 22 l l l l l l l 72 I I LLD l I - 1 1 - 1 - I i 1 I . I I i 1 l' I 1 I I I I I I I I I En-95 1 22 1 1 I i 1 I l l 72 l 1 LLD l - l 1 l - l -- l ll l t i I i l l i 1 I 1 I I I I I I l I l I I I I l 1 I 1 I I I I I I I I I I I i i i l I I I i i l l- 1 I I I I I I I I I I I I I I 1 I I I I I i i I I l I I I I I I I I l l l l l' I I I I l 1 1 I I l I i I i I I I I I I I I l 1 I I I I l~ l +- -+ + + I I I I
-+-- +- +- +- -
.+
1 - The ratio of positive results to the number of samples analysed for the parameter of interest. LLD - Lower Limit of Detection. m , _ _ - . _ . ._.- ., - . , _ . . . .- . - , , . .. .. _ - . . , . . , __
"y.y ,
'1 RADIOLOGICAL ENVIRONMENTAL MONITORING FROGRAM SUMMART -
Name of Facility: PERET NUCLEAR FOWER PLANT Docket no. t 50-440/50-441 Location of Facility : Lake County Ohio Reporting period 9400
+ +. -_ +.
+11LLE 1DDlFK+ --+ +- -. _ I I I .I I I I 1 I I I I I i 1- 1 I l 1 I I I Location with Righest i I I IType and 1 I All l l Annual Mean I. :I Medium Locations All + + + All' l I ITot. (n) I Lower i 1 _ 1 and IAnalysie 1 Limit I (Indicator a control) l Indicator Locations IDist. 1 Mean til- I control Locations: l I M3asurement-IFerformed) (LLD) l+ Mean (1) (Range) i Mean (1). (Range) IDirect I (Range) I. Mean (1) (Range) 't.
+. +. + +. --+ .. + ---------+
+-- MLEr I I I I :1 l I x-tat I .75 I - IPCr/L I 50 I I LLD 1 1 I - I 1 I I I I I I I I I I I I I i 1 I i 1: I I I i i i i 1 -l i i i 1 l I l I ~1 I I I I I I I l< 1 1 I i i I i i i i 1 I I I I I I -1 1 i I I I I I i i l I i i :1 1 I I I I I I I I i i i I i i i i 1 I I I i 1 1 I I I I I I I i I I i 'l i i 1. I 1 I I I I i 1 I I i I i I I I i I I I I I i 1 I i l l-1 I I I I I I I I I I I I I I I I I I I l- I I I: 1 I I I I I I I i 1 I I I I I I I i 11 I I I I -l I l- 1 I I i 1 I I .I I I l~ l i I i I I i I i i i i 1 1 1 I l- 1 1 I i 1 I I I l- I +--- -+-- + + ---- + -.-+- +-- . . +_------- -_. --+ 1 - The ratio of positive results to the number of samples analysed for the parameter of interest. LLD - Lower Limit of Detection. ve -
~
. . l .A RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
SUMMARY
Name of Facility: PERRY NUCLEAR POWER P ANT Docket no. : So-44e/So-441
-Location of Facility : Lake county chio Repreting period : 940o
+ MllE . cam 9id SE E
+ + __.+- -+- - -- + - - - -4.
1 I I I i 1 1 -I-1 I I I I I l- 1 I I I I I I Location with Nighest i I l l Type and i 1 All l I Annual Mean i I I Medium l Tot. (n) l Lower i Locations l All + -+- -+ All i 1 and IAnalysis I Limit I (Indicator s control) 1 Indicator Locations lDist. I Mean ti) l Control Locations l~-1 1 Msasurement IPerformedl (LLD) 1 Maan (1) (Rangel 1 Mean (1) (Range) l Direct I (Range) 1 Mean (1) (Range); +- -
+ + + + + +- + +-
1 MLEG l BA-14o 1 45 I I I I I I IPcI/L I so 1 I LLD 1 1 1 I - 1 I I I I I I I I I I I I I I I I I I I I es-134 1 11 I I I i 1 I I I so l I LLD I - I - I - 1 l1 1 I I I I I i 1- 1 I I I I I I I I I I I cs-137 1 13 I I I I I l. I so l l LLD 1 I - 1 l - I I I I i 1 l I~ l l I I I I I i 1 l l K-40 i NA i 15o9.to 1 1528.75 1 61 1 1819.29 I - 1476.11 1 I I 50 1 1 18850/00503 I (co32/co32) I 7.4 I (oo14/co14) 1 (oots/ cots) I y i I I i 1200.00-19s0.00 1 1200.o0-195o.0o I sE I 1450.oo-1950.00 1 132o.co-1s2o.co .I I I I i l 1 I l i I I LA-140 1 11 I I I I I I I I so I l LLD 1 I -- 1 1 1 I I I I I I I I I I I I I I I I I i l 1 I I -1' I I I I i 1 1 I I I I I I I I I I I I I I I I l . I I l' I i 1 i H I I I I I I I I I I I I i 1 1 1 I I 'l i I I I I I I I I I i 1 +. --+. _+ . -+ ._
+- -+ --+ . + _ .. _+
1 - The ratio of positive results to the number of samples analysed for the parameter of interest. LL3 - Lower Limit of Detection.
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
SUMMARY
Name of Facility: PERRY WUCLEAR-POWER PLANT Docket no. t So-44e/So-441 Location of Facility : Lake County Ohio Reportlag period : stee
+ M- MhF +_ -+ _
+
I
- - - - - - - - - +
I 1 1 I I I I i I I I I I i i Location with Righest I l I I I l l l l Type and l l All I I Amasal Mesa l- 1 l +
+ All l Medium l Tot. (a) l Lower l Locations l All --+
l l and IAnalysis l Limit l (Indicator & Control) l Indicator Locations IDist. I Mesa (1) l Control'Locatione l Mean all (Rangel l 1 Mansurement trerformedt (LLD)-+__l Mean'(1) (Range) l Mean (1) (Range) l Direct I (Rangel
.+
1
+. __+ ---+
----+ -+
+- -__+ -
212.se' 354.88 4o2.5e 77 l 4e2.5e l l l rr I aE-7 I NA I l 1 toess/setz) I tese2/seos) l lacI/mGtwET) I 27 I I toose/so27) l tooos/cols) 1 1.2 I 177.ee-se2.oo 2es.oe-224.se l 177.co-so2.so i 177.co-se2.co IE I l 1 l l 1 I 1 I I I I I 1 1 I I I l I I co-Sa l wA I I ' - l 27 l l LLD I - I - I - l l l I I I I 1 I I l 1 I i I I I I I I I g-l t cO-so I NA I I i l l LLD - I - I - 1 l 1 I 27 I l I I I I I I I I I I I i 1 1 I I I .I I l- l l cs-134 1 45 l 1 l i l LLD - I - 1 1 1 27 I I 1 I - 1 I I I I I I I I I I I I I I I i 1 1 l l cs-137 l so i I I l l l l l 27 I l .LLD l - I - l - l- - 1 I I I I I l l I I I I I I I I l 1 1 .g J.I-131 l 45 l l l 1 l l - i 1 27 1 i LLD I - 1 I - 1 1 I I I I I I I .I I l i 1 1- 1 I i l l K-40 i NA 4292.15 l 4ss3.is l 77 I 5214.se 1 333s.75 1-l 1 l l l 27 I l too27/se27) I tests /eoist- l 1.2 I tes12/es12) l teses/eess) l l l l l 1sas.co-7:2o.co I isas.ee-7:2e.se iE I 37ss.ee-7sas.co I .isse.ce-st72.ee i I 1 1 I I l l l .I
--+ +_ ---+- + .+_ -_, + +- .+_ -
1 - The ratio of positive results to the number of samples'enalysed for.the parameter of interoat. LLD - Lower Limit of Detection.
~
a, - . - , . _ e- r - - > v +- e -
,, -em ,g -+-- - - = , - e , - - - - - ,
, ,. - ry A
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
SUMMARY
Name of Facility: PERRY NUCLEAR POWER PLANT Docket no. so-44e/50-441 Location of Facility : Lake county chio Reporting period 94ee s + - EEAFA GMHLSPIE.---+ - +-- --
+- --+ +
1 I I i 1 1 I l~ l I I I l l l .I I I I i 1 i Locatios with Nignost 1 I I IType and i I All 1 I Annual Mean l l l Medium ITot. in) 1 Lower i Locations 1 All + + + All l I and IAnalysis I Limit I (Indicator a control) I Indicator Locations loist. I Meau (1) l Centrol Locations i I Msasurement Irerformedl (LLD) 1 Mean til (Rangel 1 Mean til (Rangel Ipirect I tRangel i Mean (1) (Rangel I +- - = __
+ -+--. +--- --.
+__ .. - - - + .+. +----------- ----+;
I re i se-7 I na 1 3397.11 1 327s.2s I s i 3sse.es I _ ssse.e3 l-Irc!/Rotws?) I te ! I testefoots: I toot 2/ce12) I 11.el teess/sessi i teses/ sees) i 1 1 I I s17.co-se74.co l' to15.so-ss74.co I ssw I s17.co-so74.se I s17.es-so74.se i I I I I I i 1 I I I I co-se i NA I I I I I I I I is l I LLo 1 1 1 I - 1 I I I I i 1 1 I I i l l l l l l 1 l i I co-so I NA i 1 1 I I I I I is i 1 Lto 1 1 1 I - 1 I I I I i 1 1 I I I I i 1 1 I- 1 I I I I cs-134 1 45 1 1 I I I l l 1 le i I LLo 1 I - 1 I - 1 I I I I I I I I I I I I I I I I I I I l cs-137 1 se 1 I I I I I I I is 1 I LLo I - 1 1 I - 1 I i 1 1 1 I I I I I I I I I I I I I I I I-131 1 45 I i 1 1 I I I I is l I LLo I - 1 I - I - 1 I I I I I I I I I I I I l i I I I I I I s-4o 1 mA 1 5451.94 1 . 53s7.as I s I sset.33 I ssel.33 . I I I is 1 I toote/eote) I tee 12/oe12) I 11.el feess/eess) I teses/ sees: I I I I I 3s74.co-7192.e6 1 3s74.e0-s7es.co I Ssw I 42s7.se-7192.ee i 42s7.se-7192.ee' I I I I I I I I I I +-- ----+ -+-------+ - - - - - _+- + + -+ --+ 1 - The ratio of positive results to the number of samples analysed for the parameter of interest. LL3 - Lower Limit of notection.
w r z
'e :: .
.-y J
5 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
SUMMARY
Name of Facility PERRY NUCLEAR power. PLANT Docket no. : so-44o/50-441 Location of Facility : Lake County Ohio Reporting period : 9400
+ SQIL GM9fA. 4EEC------+-------+ +__ + -
--+ --- +1 ~
l I I I I I i 1
'l i I I i -l 1 -l-l l ll l l l Location with Highest 1 .. l :
l l Type and l All l l Annual Mean I I-l Medium l Tot. (n) [ Lower i Locations l A11 +-------+- All-and .
. l l l Analysis I Limit l (Indicator & Control) l Indicator' Locations IDist.
l Msasurement l Performed l (LLD) l Mean (1) (Range) Mean (1) (Range)- l Direct l 1 Mean (1) (Range)
+.
l Control Locations--1
+-------------+---- >- +
1 .l Mean (1) (Range); l-
--+_ +-_ _+- . +_ .+
l s0IL l Co-se l 3oo l l l l 1 1-lPCI/KGtDRY) l 14 l l LLD I - I - [ - I -
.I I I I l i I I l' I-1 I I i l 1 l l 1 1 I CO-so I 40 1 I I I- I' i l l 14 l l LLD l -
l - I - t - l-1 I I l l 1 1 I l-l I I l l I 1 1 I l l Cs-134 l so l I l l l l l I 14 l l LtD l - l - l - I 1 l l l l l 1 I 1 I I I l 1 l -l l 1 l I l j Cs-137 I so l 302.64 . -l 311.00 l 12 I .544.50 216.50. 1 l l l 14 I l too14/co143 l t0012/o012) I o.6 l toco2/ coo 2) -l toco2/ coo 2) -l l l l l .ss.co-s2s.co I ss.co-s2s.co I wsw l 4si.co-s2s.oo 1 215.oo-21s.co .l l l l l 1 I I n-40 1 I I I l nA l 1257s.43 1 . 12143.s3 l s.l 151ss.co l 151ss.co- 1. i I 14 i 10014/00148 I- l- 11.01 (o002/00021 I- t0012/o012) 1 (0002/0002) 'l l 1 l l 10614.00-15324.00 1 1os14.00-13:51.00 l ssw 'l 15o4s.00-15324.00 1 1504s.00-15324.00- l 1 1 1. I i i l I l' l 1 na-22s i NA I 1519.o7 I 14o4.e3 l 6 l 2204.50 l 2204.50 t i I 14 I l (o014/o014) l . 1oo12/0012 11.01 toco2/ coo 23 l- toco2/ coo 2) 1157.co-22ss.co 1 -l l l l l I 1157.o0-163a.00 l ssw l 214o.co-22ss.co l 2140.00-22s9.00- .I I l l l -l i I I .I l I i 1 1 1 1 I I l l 1 l' i 1 1 I I I I l l .I l I I l 1 1 1 i 'l i I
+-___.
+. -+-------+ --
+ _+ __ ,I - .+. . ,l '
1 - The ratio of positive results to the, number of samples analyzed for the parameter of interest. LLS - Lower Limit of Detection. g .h -
' ~' " '
. .: .. i.i -
s RADIOLOGICAL ENVIRONMENTAL MONITORING FROGRAM
SUMMARY
Name of Facilityt PERRY NUCLEAR P0wER PLANT Docket no. t 50-440/50-441 - Lecation of racility : Lake County Ohio Reperting period 9400 +.WAIXE GEDSS AETA ---+ +-- -. + +_ --+ I I I I I I .I l-1 I I I I I I 'l' l l l l l l Location with Nighest' l 1 l l Type and l l All l l Annual Mean l l l Medium l Tot. (a) l Lower l Locations -l All +- - + .
-+ .
All .l l and l Analysis l Limit l { Indicator & Control) l Indicator Locations lDist. l Mean it) l . Control Locations l Mean (1) (Range) Mean (1) (Range) (Range) l Mesa (1) (Range) l Msasurement l Performed l (LLD) l l (Direct l
+ +-- -+
l.
--+ + +
+-- +._ --+ wTRs l G-sETA l 3 2.47 l 2.42 1 60 1 2.68 .I 2.63- 1 l 1 lPCI/L l 54 l l (0054/0054) [ (0042/0042) l 1.0 l (0009/0009) l (0012/0012) l: l l l l 1.30-4.80 l 1.30-3.80 l wsw I 1.60-3.80 l _1.90-4.80 .l l 1 1 1 1 1- 1 I I i 1 1 1 I I I I li l I i i I I i I 'l i I I i i I I I I I I I I I I I I i I i i l i i i i l ll 1 I i l I 1 I I I I . I ll l 1 I I i 1 1 I I I I I I I i 1 1 I i 1 I I i 1 1 I I I 1 ll 1 1 1 1 I I i 1 l l I 1 1 1 I I I I I i i 1 i I < l l I I I .I I I i 1 I I I I I I I I I I I . 1 I I I i 1 I I I l I I i l I 1 I h l I I I I l' 1 I h i I I I I I-1 I H I I I i 1 .I I I h I I I I I I I I H I I I I i i l 1 -4 I l' I I I I I I I I I I i l I + +-- + +- --+- +- +__ + - . _ . -+ 1 - The ratio of positive res11ts to the number of samples analysed for the parameter.of interest. LLD - Lower Limit of Detection.
U RADIOLOGICAL ENVIRONMENTAL MONITORING FROGRAM
SUMMARY
Name of Facility: FERRY NUCLEAR FOWER PLANT Docket no. : 50-440/50-441 Location of Facility : Lake County Ohio Reporting period : 9400 +WATEB_G M g EREC_ , ,. .. _ I I I i I I I 'l i i 1 1 I I I I I l l l l l Location with Nighest i I l l Type and l l All l l Annual Mean l l l Medium ITot. (n) I Lower l Locations l All + +- + All l l and l Analysis I Limit l (Indicator E Control) i Indicator Locations IDist. I Mean (1) l Control Locations i I M3asurement lPerformedi (LLD) l Mean (1) (Range) l Mean (1) (Range) IDirect I (Range) 1. Mean (1) (Range) l +- + + + + + +- + +- l WTRG I SA-140 1 45 l l- 1 I I I IPCI/L I 54 I I LLD I - l - 1 - 1 l I I I i i i i I i l I I I I i i 1 -1 I I Co-5s i 11 I I I I I I I I 54 I I LtD I - l - I - I - l-1 1 1 I I I I I I I I I I I I I I I I I Co-60 l 11 I I I I I I i 1 54 I I LLD 1 I - I - I - I-1 I I I I I I I l~ l i I l i i I i i l l Cs-134 l 11 l l l l l lI-1 1 54 I I LLD I - l- - I - 1 . I I i 1 1 1 1 I I I I I 1 I I I I i 1: 1 I Cs-137 l 13 l l l t i I I i 54 l l LLD I - l - 1 I -- 1 I I i 1 1 1 1 I I I I I i 1 1 I l' I I I PE-58 1 22 I I I I i 1 I I 54 I I LLD I - 1 l - l - I ! I I I I I I I l' i 1 1 1 I I I I I~ l I LA-140 1 11 I i l I i i i I 54 I I LLD I - I - 1 I - 1 I I I I I I I I ~ I-l 1 ! I I I I l +- + + -+ + ---+ + + - ... ,l 1 -'The ratio of positive results to the number of samples analysed for the parameter of interest. LLD - Lower Limit of Detection.
mg
~ <
RADIOLOGICAL ENVIRONNENTAL MONITORING PROGRAM
SUMMARY
Name of Pacilityt PERRY NUCLEAR POWER PLANT Docket no. : 50-440/50-441 Location of Pacility 2 Lake County Ohio Reporting period 9400
+X4HB_9MtfA.EMC ..-- - _______
I I I I I I I 1 I I I I I I 1 l l l l l l Location with Nighest 1 l l Type and l All l 'l l l Annual Mean l' hedium l Tot. (n) l Lower l Locations l All + l
--+ +
l l. All l l and l Analysis l Limit l (Indicator E Control) l Indicator Locations lDist. l Mean (1) l Control Locations l l Mnasurement ,l Performed) (LLD) l Mean (1) (Range) l Mean (1) (Range) l Direct l (Range) :l Mean (1) (Range) j 4 _., __ l WTRG. l MN-54 l 11 l l l l l l lPCI/L l 54 l l LLD 1 - l- - l - l 1 1 I I l I I I l 1. I I I I i l l N8-95 l 11 l l 1 I I i-54 l l 1 l l l l- l LLD l - l - l - l - 1-1 I I I i 1 .I I I I i 1 1 1 I I I I l l EN-65 l 22 l l l l l l l 54 l l LLD \ l - l I I l i I l - I - ' -
'l I I I I I I I I I i 1 I l l 3R-95 l 22 l l l l l l'
l I 54 I l LLD l l - 1 l - I - I 1 l l l t I I I I I I i 1. I I i -l I I 1 I I I i I l l I 1 i Ll I I I l' l. I I I I I i i I I I i i 1 I l' I I I I I I I I I I I I I I I I l' I I l' 1 1 1 I I I I I l l i I I I i 1 1 1 1 I l i I I I 1 I I I i 1 I I I I I i i I I I I I I I l-1 I I I I
+- + -+ + .+
I I i
--+ + .+_ --.1 1 - The ratio of positive results to the number of samples analysed for the parameter of interest.
LLD - Lower Limit of Detection.
7-. q i 4 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
SUMMARY
Name of Facility: PERRY WUCLEAR POWER PLANT Docket no. 50-440/s0-441 Location of Facility : Lake County chio Reporting period 9400
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==+ +- + + + _ ,I _- +. -+.
1 TRITIUM i na l 1500 1 230.00 1 23s.33 I ss i 255.50 1- -173.00 ~l IPCI/L i 18 l l (0010/0010) I (0009/0014) i 3.9 I (0002/0004) I :(0001/0004) .I, l l l l 173.00-282.00 l 204.00-282.00 l WSW l- 229.00-202.00 l 173.00-173.00 l 1 1 I I I I I I l I I i i I i i 1 1 I I I I I I I I I I I I i l i i !- 1 I i 1 1 I I I I l 1 i i i l I l .I' I I I I I I I I I I i i i i i I l I I I I I I I I I I I i 1 I I I I I I l-1 1 1 I l i I l' I i 1 1 1 i l i I .I I I I I I I I I I I I I I I I I I I I I I I I i 1 .I l-1 I I I I I I I
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+ + + -+ + +
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p24001 .4 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
SUMMARY
PAGE: SSL Name of Facility: PERRY NUCLEAR POWER PLANT Docket no.
- 50-440/50-441-Location of Facility : Lake County' Ohio Reporting period : 940o . .
iSEDJWJLT_ Gat $tlA.DJ'F&__+_______ _
.+ +-
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+ -+----- +
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+
i Measurement l Performed l (LLD) l Mean (1) (Rangel l Mean (1) (Range) IDirect l (Range) l- Mean (1) (Range). l= ___-__+ _.+. _+- -
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-+- _+ ,-___
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1 SED I CO-se I so I l l-lPCI/KG(DRY) l 14 l LLD 1 l l<
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+-____________.I_________._______+_______________________+_____- ._____________._______.____________________,1 ____________________1. _ ,
1 - The ratio.of positi're results to th- aumber.of. samples analyzed'for the parameter-of interest. LLD - Lower. Limit of Detection.
- - _ . _ _ - - - . l-. - - - - - - - - ---
'4 RADIOLOGICAL ENVIRONMENTAL MONITORING'FROGRAM
SUMMARY
Name of Facility: PERRY WUCLEAR FOwtR PLANT Docket no. t so-44e/se-441 +
" I Location of racility Lake County Ohio' Reporting period 3,s400
+ EISB_SR21& SPEC -+ +- -.- -
. + --+
1 l 1 I I I I~ l 1 I I I l l l 1. I I I I l l Location with Righest I l l IType and I l All I l Annual Mean l l l Medium l Tot. (n) l Lower i Locations I All +-- -+ + All . I. I and IAnalysis I Limit I (Indicator a control) i Indicator Locations.lDist. l Mean (1) 1. Control Locations' l l Measurement IPerformedi (LLD) l Mean (1) (Range) 1 Mean (1) (Range) IDirect I (Range) -l Mean -(1) (Range) 'l
+- _
+----- -+--= _+ -+ .+ --+ +
+
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-l -
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.I I I I I I I l l 1 I I I I I I '. I 'l-1 l Cs-137 1 112 I l I I I I I I 2s I I LLD I -
I - I - I - 1. I I I I l l 1 - l~ l I l i - I I I l l .I I l rE-ss l 1ss I I I I .I I l l 2s I I LLD I - 1 I -- l - 1 I I l 1 1 I I l- il I l .I I I - l I I I I l x-4o I mA . I 2232.2e i 221s.se 1 32 1 .224s.se l 224s.se 1; I I 25 i 1 (es2s/ seas) I feel 3fests) I is.el- '(ss12/se123 l . (es12fes12)- .I l 1 I i 132e.ee-337o.es l 142s.se-so77.es I wsw l 132s.se-337e.se l 132e.se-337e.ee. I I I I I I I I I I I l Mn-se 1 57 I I I I I I l 25 -l LtD l - l I 1 - - l - l-1 I I I I l l- l El-1 i i I I i i i i
+ -+-- +-------+ - - + _
+- + , +
1 - The ratio of positive results to the number of samples analysed for the parameter of interest. LLD - Lower Limit of Detection.
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- 1 .
3 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
SUMMARY
Name of Facility: PERRY NUCLEAR POWER PLANT Docket no. : 50-440/50-441 Location of Facility : Lake County Ohio Reporting period ~ : 9400
+U.S}L_ GAMMA SfEC ..___ , ________,_ ., __, _,
I I I I I l l l. 1 I I I I I I l-I . l l l l Location with Highest l l l Type and l l All l l Annual Mean I l l Medium 'l To t . (n) l Lower l Locations i A11 +--- --+-- + All- ?l l and (Analysis l Limit') (Indicator & Controll l Indicator Locations lDist. l Mean (1) l' Control Locations l-l Msasurement l Performed l (LLD) l Mean (1) (Range) l Mean (1) (Range) l Direct l (Range) l Mean (1) (Range)- l,
+- _ +--_-___ +-------+___ -+ +. -+ + ----+ .
I rsa I zN-65 l 195 1 l l l l 1 LLD l -: I IPCI/KG(wtT) I 25 l l l - l - - l I I i 1 I I I I I I I I I -l i I I I I I i 1 l- 1 I I I I I I I I I I I I-1 I i i I I I i ~I I I I I l i I I -1 I l l I I i 1 1 I I I i 1 .I l' 1 1 1' 1 I I I I I I I I I I I I I i i i I I I I I I I i .I I i l I i I i l l I I I I I I I i 1: 1 I I I I I I I I I i i i l i I I I I I I I I i 1 1 I ll l t i I I I I I ll t 1 I I I I I I 1 1 I I I i i l I I I i 1 i l- l ll 1 1 I 'l l I I I I I I I I I I I I I I i i l i I i i I 1 I i I I I I 1 I I I I i l l 1 I. I I I l- 1 I i 1 t
+ --
- + - + +- -+- -+ + + --_+ -
{ 1 - The ratio of positive results to the number-of samples analysed for the parameter of-interest. LLS - Lower Limit of Detection. m_ es+z_ % __._.u._______.__-.L.m_u_-_ _ _ - _ _ _ --r u_+_.m-wmu.- _a i le ur g- .uk Wue n-
~ -
, RADIOLOGICAL ENVIRONMENTAL MONITORING FROGRAM
SUMMARY
Name of Facility:-FERRY NUCLEAR FOWER PLANT Docket no. : 50-44e/59-441 Location of Facility : Lake County chio Reporting period : 9498
. --__UA .- --.-- . . . _..- J l i I I I I I I I i 1 1 I I . 1 IL I l l l l l Location with Nighest. 'l l 1 IType and l l All l I Annual Mesa l 1 l Medium ITot. (n) l Lower i Locations l . A11 +-- -+ + All l-l and l Analysis l Limit l (Indicator & Control) l Indicator Locations (Dist. l Mean (1) I Control Locations -l l M3asurement IForformedl (LLD) i Mean (1) (Range) l Mean (1) (Range) IDirect I (Range) 1 -Mesa (1) (Range)' l
+ -
+- + -+ +- +- + + .+
l TLD l DIRECT l NA l 13.49 l 13.45 l 18 l 21.33 I 14.16 1 lMR/91 DAYS l 155 I I (0155/0155) l -(9147/0147) 1 5.9 I (0984/9004) l . (8808/0000) l-l l l 1 8.10-24.20 l 8.10-24.20 l 5 l 14.10-24.29 l 11.18-17.78~ l 1 I I I I I I I l-1 I I I I I I I I I I I I I I I I I I I I I I I I I 'l l I I I I I I I I I I I I I I I i ~l' I I I I I I I I I i 1 1 1 I I i 1 1. I I I I I I I I -- l - 1 I I I I I .l. l .I I I i i I I I I I I I I I I i 1 I l-1 I I I I I I i i i I I I I I I i 'I I I I I I I I i 1. I I I I I i 1 l- 1 I I I I I I I I I I I I I I I I I I I I I i 1 1 1. I i 1 1 I l' I I I l' I I I I i 1- 1 I l l_ 1 1 1 I I I I I l -- l l 1 1 I I I I I I I I l- 1 .I I I I I i 1 1 1 1 I I
+----- +-- + + +-- + .+ + .___._,I .
1 - The ratio of positive results to the number of samples analysed for the parameter of interest. LLD - Lower Limit of Detection.
. s i_, . , , , - + 4 v'
- n RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
SUMMARY
Name of Facility: PERRY NUCLEAR POWER PLANT Docket no. : 50-449/50-441 Location of Facility : Lake County Ohio Reporting period : 9409
-+ --+ + + + + +
1 1 I I I I I l-1 I I I I I I i l l l l l l Location with Righest l l l IType and l [ All l l Annual Mesa l . l-Medium Locations l All --+-- + + All- l l l Tot. (n) I Lower l and l Analysis l Limit l (Indicator a Control) l Indicator Locations lDist. l Mean (1) l Control. Locations. l. l Mean (1) (Range) l M2asurement l Performed l (LLD) l Mean-(1) (Range) l Mean (1) (Range) l Direct l (Range) l
+ -
l
+
+ -
+ + --+ --+ +- +-
14.20 l 18 [ 21.98 l 14.76 l l TLD I DIRECT l NA l 14.23 l (0004/8008) lM2/91 DAYS I 154 I I (0154/0154) l (0145/0146) l 5.0 j (8804/8004) l _1 l l l l 9.60-23.70 l 9.60-23.10 l 3 I 19.50-23.70 1 12.50-17.08 l l l I I I I l l 1 l I I I I I I l l I I i 1 I I I I I I I I I i 1 1 I I l I i 1 1 I I I i ; i I I I I I i 1 l' I I I I l i I i l-l 1 1 I I 'I l 1 1 l I I I I i i i I l l' l i I I I l I 1 I I I I i ! I I I I I I I I I l- 1 I I I I i i l I l-1 I I I I I i i I i l i i l i I i i l-i i l 1 I I i l I I I I I I I 1 I I I l- 1 I I I i -1 l I I I I I I l 1 1 I I I I I i 1 1 1 I I I I I I I I I I l i I I I I I I-l l l 1 I I I i l l l I I I I I I I i I I I I I I I I I.
+
+ +- + -+
! + +- + + 2 ! 1 - The ratio of positive results to the number of samples. analyzed for the parameter of interest. l LLD - Lower Limit of Detection. (
- +
cp RADIOLOGICAL ENVIRONMENTAL MONITORIP9 **0 GRAM
SUMMARY
Name of Facility: FERRY NUCLEAR power PLANT .et no. : 50-440/5e-441 Location of Facility : Lake county Ohio Reporting period : 9400 UJ2 -+-- ---+----- -+ --
+------ -- +- - --------+--
+-- 1 I I I I I I i 1 1 1 1 I I I 1 l l l l Location with Nighest l l l 1 I 1 IType and 1 I All i I Annual Mean i I Medium ITot. (a) I Lower i Locations I All +-- +-- + All i I and IAnalysis Limit I (Indicator & Controll 1 Indicator Locations IDist. Mean (1) (Range) I Mesa.(1) (Range) l Control Locations 'l l Mean (1) (Range) l i Msasurement IFerformedi (LLD) I+_ Mean (1) (Range) i IDirect I
----------+
+- .--+ -----+_- + _
+ -+ .+
1 TLD I DIRECT I WA I st.oe I st.as I is I is.le I so.es l IM2/38s DAY 8 1 38 I I (8039/08351 1 (0837/8837) 1 58 I (oest/seet) I (ono2/ose2) I I I I I 23.4o-1s.1o 1 23.4e-19.lo Is 1 7s.ao-7s.ie i es.4e-52.se i I I I I I I I I l i I I I i I 1 1 .I I I I I I I I I -- I I I I I I I i 1 l' I i i 1 I I i l i 1 I i l 1 i 1 -1 1 I I I I I I l- l 1 i I I I I I I I l-1 I I I I I I I I I I I i 1 I I I I I I I I I I I I I I I I I I I l . I I I I I I I I I I I I I I I I I I I I I I I i l I I I I I I I I I I I I I i i 1 1 I I I I I I I i 1 1 I I I I I i 1 1 I I I -1 1 1 I I I I I I I I I I I I I I I I I I I I I i l I I I I i 1 1 I I l 1 I I I I I I i- 1 I I I I I I I l l l- l
+ - -+- + +__ + __-- + -+ + +
1 - The ratio of positive results to the number of samples analysed for the parameter of interest. LLD - Lower Limit of Detection.
l l l 1 l l I;
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APPENDIX B: 1994 RADIOLOGICAL : ENVIRONMENTAL MONITORING PROGRAM 1 DATA i l t T t APPENDIX B: 1994 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
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t' CLEVELATB EL3CTRIC ILLUMIEATICS CO. - PEPP. -- CEMP TEACKICS SYSTEM G-DSTA AIR CEPOLT SAMPL3 PROF;T3 CT IS: wtEELT RESULTS IN PCI/CU.M. +/- 2 SIGRA M9 M ATD COLLECTION PERIOD STATION LOCAT!oNS 66 el 35 940921 To 940928 .616+/ .003 .018+/ .094 .011+/ .884 OCT 940924 To 941985 .411+/ .003 .998+/ .003 .999+/ .903 941005 TO 941012 .019+/ .003 .916+/ .003 .019+/ .es3 941012.To 941019 .022+/ .403 .022+/ .004 .829+/ .403 941019 To 941026 .919+/ .004 .016+/ .004 .019+/ .004 NOT 941026 To 941102 .921+/ .993 .823+/ .944 .023+/ .984 941102 TO 941109 .020+/ .004 .019+/ .004 .920+/ .004
' 941109 to 941116 .025+/~.003 .422+/ .004- .624+/ .894 941116 To 941123 .918+/ .003 .020+/ .004 .421+/ .004 941123 To 941139 .416+/ .004 .020+/ .004 .022+/ .004 DEC 941130 TO 941207. .029+/ .004 .827+/ .004 .513+/ .003 941207 To 941214 .014+/ .004 .916+/ .004 .916+/ .084 941214 To 941221 .925+/ .004 .025+/ .004 .024+/ .884 941221 TO 941228 .031+/ .004 .425+/ .004 .929+/ .004 4
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y . SAMMA SPEC REPO%T OF AI'. SAMPLE FREGrG2CY.ZSt'W2 EELY ~ CESULTS 13 PCI/CU.M. +/- 2 SICMA - --- p i .,:, - ATR IODINE STATION SAMPLE COLLECTION- I-131 L3 CATION TYPE DATE 01 AIR 931229/940105 LT .018
- 01 AIR 940105/940112 LT .017 01 AIR 940112/940119 LT .018 01 AIR 940119/940126 LT .030 01 AIR 940126/940202 LT .024 01 AIR 940202/940209 LT .031 01 AIR 940209/940216 LT .024 01 AIR 940216/940223 LT .017 01 AIR 940223/940302 LT .025 01 AIR 940302/940309 LT .027 01 AIR 940309/940316 LT .013 01 AIR 940316/940323 LT .014 01 AIR 940323/940330 LT .019 01 AIR 940330/940406 LT .019 01 AIR 940406/940413 LT'.022 01 AIR 940413/940420 LT. 016 01 AIR 940420/940427 LT .016 01 AIR 940427/940504 LT .019 01 AIR 940504/940511 LT .018 01 AIR 940511/940518 LT .015 01 AIR 940518/940525 LT .019 01 AIR 940525/940601 LT .024 01 AIR 940601/940608 LT .011 01 AIR 940608/940615 LT .012 01 AIR 940615/940622 LT .015 01 AIR 940622/940629 LT .014 01 AIR 940629/940706 LT .007 01 AIR .940706/940713 LT .012 01 AIR 940713/940720 LT .015 01 AIR 940720/940727 LT .011 01 AIR 940727/940803 LT .019 01 AIR 940803/940810 LT .014 01 AIR 940810/940817 LT .000 01 AIR 940817/940824 LT .013 01 AIR 940824/940831 LT .021 01 AIR' 940831/940907 LT .019 01 AIR 940907/940914 LT .018 01 AIR 940914/940921 LT .013 01 AIR 940921/940928 LT .009 01 AIR 940928/941005.LT. 013 01 AIR 941005/941012 LT .026 01 AIR 941012/941019LLT .006 01 AIR 941019/941026 LT .014:
el AIR 941026/941102 LT .010 01 AIR 941102/941109 LT .011 01 AIR 941109/941116 LT .022 _ ._ _ _ _ _ _ _ _ _ _ . . _ . _ ._n______________u._______-_i__ _ _ _ - _. . . . - . __ ~.;_.-._-.._. . , - - , . ' C .. ,
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REMP TRACR2LG SYSTEM 1h SAMRA SPEC REPORT OF AI SAMPLE FREQUENCY IS: WEERLY ""i RESULTS IN PCI/CU.M. +/- 2 SIGMA AIR IODINE i STATION SAMPLE COLLECTION Z-131 LSCATION TYPE DATE ! 01 AIR .941116/941123 LT .019 , 01 AIR 941123/941130 LT .010 01 AIR 941130/941207 LT .006 01 AIR 941207/941214 LT .009 01 AIR 941214/941221 LT .021 91 AIR 941221/941228 LT .022 03 AIR 931229/940105 LT .018 ! 03 AIR 940105/940112 LT .016 4 03 AIR 940112/940119 LT .018 l 03 AIR 940119/940126 LT .028 03 AIR 940126/940202 LT .023 03 AIR 940202/940209.LT .030 1 03 AIR 940209/940216 LT .023 03 AIR 940216/940223 LT .017 03 AIR 940223/940302.LT .024 i 03 AIR 940302/940309 LT .027 l 03 AIR 940309/940316 LT .013
- 03 AIR 940316/940323 LT .015 j 03 AIR 940323/940330 LT .020
- 03 AIR 940330/940406 LT .020 ,
03 AIR 940406/940413 LT .023 03 AIR ,940413/940420 LT .015-
- 03 AIR 940420/940427 LT .013 63 AIR 940427/940504 LT .016 03 AIR 940504/940511 LT .015 03 AIR 940511/940518 LT .013 i 03 AIR 940510/940525 LT .016 03 AIR 940525/940601 LT .020 93 AIR 940601/940600 LT .010 03 AIR .940608/940615 LT .010.
03 AIR .940615/940622 LT .013 03 AIR 940622/940629.LT .013 03 AIR 940629/940706 LT .000 03 AIR 940706/940713 LT .014 03 AIR 940713/940720 LT .417 03 AIR. 940720/940727 LT .013 93 AIR 940727/940003 LT .021 03 AIR 940403/940810 LT .012 03 AIR 940810/940817 LT .007 03 AIR 940017/940824 LT .011
-93 AIR 940024/940031 LT .018 03 . AIR 940831/940907 LT .016 03 AIR 940907/940914 LT .016
- 03 AIR. 940914/940921 LT .012 i- 83 ' AIR _940921/940928 LTL.017
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.. .* .. 4 CAMMA SPEC REPOOT OF AI'
-SAMPLE FREKU20CY 15: CEEELY-EEEULT3 13 PCI/CU.M. +/- 2 SIEMA ATR TODINE STATION SAMPLE COLLECTION I-131 L& CATION TYPE DATE 03 AIR 940928/941005 LT .011 03 AIR 941005/941012 LT .014 03 AIR 941012/941019 LT .006 03 AIR 941019/941026 LT .014 03 AIR 941026/941102 LT .009 03 AIR 941102/941109 LT .011 03 AIR 941109/941116 LT .021 03 AIR 941116/941123 LT .018 03 AtR 941123/941130 LT .009 03 AIR 941130/941207 LT .006 03 AIR 941207/941214 LT .009 03 AIR 941214/941221 LT .021 03 AIR 941221/941228 LT .022 04 AIR 931229/940105 LT .018 04 AIR 940105/940112 LT .016 04 AIR 940112/940119 LT .017 04 AIR 940119/940126 LT .029 04 AIR 940126/940202 LT .024 04 AIR 940202/940209 LT .032 04 AIR 940209/940216 LT .024 04 AIR 940216/940223 LT .017 04 AIR 940223/940302 LT .025 04 AIR 940302/940309 LT .028 04 AIR 940309/940316 LT .013 04 AIR 940316/940323 LT'.014 04 AIR 940323/940330 LT .020 04 AIR 940330/940406 LT .020 04 AIR 940406/940413 LT .023 04 AIR 940413/940420 LT .015 04 AIR 940420/940427 LT .016 04 AIR 940427/940504 LT .017 04 AIR 940504/940511 LT .016 04 AIR 940511/940518 LT .014 04 AIR 940518/940525 LT .017 04 AIR 940525/940601 LT .022 04 AIR 940601/940608 LT .010 04 AIR 940608/940615 LT. 010 04 AIR 940615/940622 LT .013 04 AIR '940622/940629 LT .013 04 AIR ,940629/940706 LT .000 64 AIR 940706/940713 LT .014 04 AIR 940713/940720 LT .016 04 AIR 940720/940727 LT .013 04 AIR 940727/940003 LT..021 04 AIR 940803/940810 LT .012-
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CLEVELAED' ELECTRIC ILLUMINATIEG CO. -'PEPP. " REMP TRACKIEG STSTEM l- CAMMA $PSC REPOET OF AI j SAMPLE FREQUENCT IS: WEERLY RESULTS IN PCI/CU.M. +/- 2 SIGMA ATR T OD T NF. STATION SAMPLE COLLECTION I-131 LOCATION TTPE DATE 04 AIR :940810/940817 LT .007 04 AIR 940817/940824 LT .011-04 . AIR 940824/940831 LT .018 04 AIR 940831/940907 LT .016 04 AIR 940907/940914 LT .016 04 AIR 940914/940921 LT .012 04 AIR 940921/940928 LT .014 04 AIR 940928/941005 LT .011 04 AIR 941005/941012 LT .014 04 AIR 941012/941019 LT .006 04 AIR 941019/941026 LT .014 04 AIR 941026/941102 LT .009 04 AIR 941102/941109 LT .011 04 AIR 941109/941116 LT .021 04 AIR 941116/941123 LT .018 04 AIR 941123/941130 LT .009 04 AIR 941130/941207 LT .006 04 AIR 941207/941214 LT .009 04 AIR 941214/941221 LT .021 04 AIR 941221/941228 LT .022 05 AIR 931229/940105 LT .017 05 AIR 940105/940112 LT .015 05 AIR 940112/940119 LT .016 05 AIR 940119/940126 LT .026 05 AIR 940126/940202 LT .021 05 AIR 940202/940209 LT .027 05 AIR 940209/940216 LT .020-05 AIR 940216/940223 LT .014 05 AIR 940223/940302 LT .021 05 AIR 940302/940303 LT .319 05 AIR 940309/940316 LT .018 05 AIR 940316/940323 LT .020 05 AIR 940323/940330 LT .028 05 AIR 940330/940406 LT .028 05 AIR 940406/940413 LT .032 05 AIR 940413/940420 LT .016 05 AIR 940420/940427 LT .014 05 AIR 940427/940504 LT .017 05 AIR 940504/940511 LT .016 05 AIR 940511/940518 LT .014 05 AIR 940518/940525 LT .017 05 AIR 940525/940601 LT .021 05 AIR 940601/940608 LT .010 05 AIR 940608/940615 LT .010 05 AIR 940615/940622 LT .013 1
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A' ~ CAMMA SF3C REPCRT CF AI ' SAMPL3 FREgUEECY IS: WEEELY 1 EESULTS 12 PCI/CU.M. +/- 2 SIGMA AIR TODINE STATION SAMPLE COLLECTION I-131 L3 CATION TYPE DATE 05- AIR 940622/940629 LT .012 05 AIR 940629/940706 LT .000 05 AIR 940706/940713 LT .014 i 05 AIR 940713/940720 LT .017
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05 AIR -940720/940727 LT .013 05 AIR 940727/940803 LT .021 05 AIR 940803/940810 LT .012 i 05 AIR 940810/940817 LT .007 05 AIR 940817/940824'LT .011 05 AIR 940024/940831 LT .019 05 -AIR 940831/940907 LT .016 05 AIR 940907/940914 LT .016 05 AIR 940914/940921 LT .012 05 AIR 940921/940928 LT .015 05 AIR 940928/941005 LT .012 05 AIR 941005/941012 LT .015 05 AIR 941012/941019 LT .006 05 AIR 941019/941026 LT .013 05 AIR '941026/941102 LT .009 05 AIR 941102/941109 LT .011 05 AIR 941109/941116 1Mr . 0 21 ' 05 AIR 941116/941123 LT. 018 05 AIR- 941123/941130 LT .010 05 AIR 941130/941207 LT .006 05 AIR 941207/941214 LT .010 ' 05 AIR 941214/941221 LT .022 05 AIR -941221/941228 LT'.023 06 AIR 931229/940105 LT .018' 06 AIR 940105/940112 LT .018 06 AIR '940112/940119'LT .019 06 AIR 940119/940126 LT .033 06 AIR 940126/940202 LT .026 06 AIR 940202/940209 LT .034 06 AIR 940209/940216 LT .026 06 AIR. 940216/940223 LT .019-06 AIR 940223/940302 LT .028 06 AIR 940302/940309 LT .031 06 AIR 940309/940316 LT .015. 06 AIR 940316/940323 LT .017 06 AIR 940323/940330 LT. 022 06 AIR 940330/940406 LT .022-06 AIR 940406/940413 LT .028 4 06 AIR 940413/940420 LT .017 06 AIR 940420/940427 LT .015 06 AIR 940427/940504.LT .018 _ _ . _ , _ . . . . . . . .....u_ _.- _n..--,. ._,.L. __,m - . . . - . ,- - - . . .. . _ _ . . ..m~ . . . . . ~__ _____________._.______._.__.=_2 _
.CLEVELA2D ELECT 2IC ILLUMICATICG CO. - P2PP.
CEMP TOACKICG SYSTEM CAMMA SPEC REPOLT CF AI SAMPLE FREQUENCT ISt WEEKLY ij RESULTS IN PCI/CU.M. +/- 2 SIGMA AIR IODINE STATION SAMPLE COLLECTION I-131 LCCATION TYPE 'DATE 06 AIR 940504/940511 LT .017 06 AIR 940511/940518 LT .015 06 AIR 940518/940525 LT .018 06 AIR 940525/940601 LT .023 06 AIR 940601/940608 LT .010 06 AIR 940608/940615 LT .011 06 AIR 940615/940622 LT .014 06 AIR 940622/940629 LT .014 06 AIR 940629/940706 LT .008 06 AIR 940706/940713 LT .013 06 AIR 940713/940720 LT .015 06 AIR 940720/940727 LT .012 06 AIR 940727/940803 LT .020 06 AIR 940803/940810 LT .013 06 AIR 940810/940817 LT .008 06 AIR 940817/940824 LT .012 06 AIR 940824/940831 LT .019 06 AIR 940831/940907 LT .018 06 AIR 940907/940914 LT .017 06 AIR 940914/940921 LT .013 06 AIR 940921/940928 LT .016 06 AIR 940928/941005 LT .012 06 AIR 941005/941012 LT .016 06 AIR 941012/941019 LT .006 06 AIR 941019/941026 LT .015 06 AIR 941026/941102.LT .011 06 AIR 941102/941109 LT .012 06 AIR 941109/941116 LT .023 06 AIR 941116/941123 LT .020 06 AIR 941123/941130 LT .010 06 AIR 941130/941207 LT .006 06 AIR 941207/941214 LT .010 06 AIR 941214/941221 LT .023 06 AIR 941221/941228 LT .025 07 AIR 931229/940105.LT .019 07 AIR 940105/940112 LT .017 07 AIR 940112/940119 LT .019 07 AIR 940119/940126 LT .031 07 AIR 940126/940202.LT .026 07 AIR 940202/940209 LT .033 07 . AIR . 940209/940216 LT .025 07 AIR 940216/940223 LT .018 07 AIR 940223/940302 LT .027 07 AIR 940302/940309 LT .029 07 AIR 940309/940316 LT .014 __.___._____.m __.___._u___.m__ ,__ . , ,, e 1, -
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SAMMA SPEC EEFSOT OF AI RAMPLE F2EQU2CCT ISt t!EEELY
'C32ULTS IU FCI/CU.M. +/- 2 SICMA AIR IODINE STATION SAMPLE COLLECTION I-131 L3 CATION TYPE DATE
~
07 AIR 940316/940323 LT .016 07 AIR 940323/940330 LT .021 07 AIR 940330/940406 LT .021 07 AIR 940406/940413 LT .025 07 AIR 940413/940420 LT .016. i 07 AIR 940420/940427 LT .014 07 AIR 940427/940504 LT'.018 07 AIR 940504/940511 LT .017 07 AIR 940511/940518 LT .014 07 AIR 940518/940525 LT .017 07 AIR 940525/940601 LT .022 07 AIR 940601/940608 LT .010 07 AIR 940608/940615 LT .011 07 AIR 940615/940622 LT .014 07 AIR 940622/940629 LT .013 3 07 AIR 940629/940706 LT .004 07 AIR 940706/940713 LT .014 07 AIR 940713/940720 LT .016 07 AIR 940720/940727 LT .012 07 AIR 940727/940803 LT .021 07 AIR 940803/940810 LT .012 07 AIR 940810/940817 LT .007 07 AIR 940817/940824 LT .012 07 AIR 940824/940831 LT .018 07 AIR 940831/940907 LT. 017 07 AIR 940907/940914 LT .016 07 AIR 940914/940921 LT .012 07 AIR 940921/940928 LT .015 07 AIR 940928/941005 LT ' . 012 07 AIR 941005/941012 LT .015 07 AIR 941012/941019 LT .006 07 AIR 941019/941026 LT .014 07 AIR 941026/941102 LT .010 07 AIR 941102/941109 LT:.011 07 AIR 941109/941116 LT .021 07 AIR 941116/941123 LT'.018 07 AIR 941123/941130 LT .009 07 AIR 941130/941207 LT .006 07 AIR- 941207/941214 LT-.009 07 AIR 941214/941221 LT .021 07 AIR 941221/941228 LT .022 35 AIR 931229/910105 LT .017 35 AIR '940105/940112 LT .016 35 AIR 940112/940119 LT .016-35 AIR 940119/940126'LT .013 _ _ _ _ _ _ _ _ _ _ _ _ . _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ ____ .m_ _ _ . _ _ _ _ . _ _ _ ____m -u .. - - - . . . - . , . - _ _ . - . _ . . --_. - _
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3 CLEVELA%D.. ELECTRIC ILLUMIEATIEG'CO.1- PEPP. ;~. ~ REMP TRACEISS SYSTEM' CARMA' SPEC CEPCOT SF AI-SAMPLE FEEQU2LCY IS: CORELT-RESULTS.IN PCI/CU.M. +/- 2 ' SIGRA - ' h.c
~ AIR IODINE
'. STATION SAMPLE ~ COLLECTION I-131
- LOCATION TYPE DATE 15 AIR 940126/940202 LT .016
-J5 AIR 940202/940209 LT .032 35 AIR 940209/940216 LT .028 35 AIR 940216/940223 LT .022 35 AIR 940223/940302 LT .016 35 AIR. 940302/940309 LT .031 35 AIR 940309/940316 LT .021
+ 35 AIR 940316/940323 LT .027 35 AIR 940323/940330 LT .017 < 35 AIR 940330/940406 LT .021 35 AIR 940406/940413 LT .019 35 AIR 940413/940420 LT .018 35 AIR 940420/940427 LT .023 35 AIR 940427/940504 LT .020 .; i 35 AIR 940504/940511 LT .012
- 35 AIR 940511/940518 LT .009
, 35 AIR 940518/940525 LT .016 t. i 35 AIR 940525/940601 LT .009 35 AIR 940601/940608 LT .014 35 AIR 940608/940615'LT .007 35 AIR 940615/940622 LT .010 35 AIR .940622/940629 LT .015 35 AIR 940629/940706 LT .006 35 AIR 940706/940713 LT .016 35 AIR 940713/940720 LT .013 35 AIR 940720/940727'LT .014 35 AIR 940727/940803 LT .024 35 AIR 940803/940810 LT .014 35 AIR 940810/940817 LT .021 . 35 AIR 940817/940024 LT .012 t 35 AIR 940824/940831 LT .014 i' 35 AIR 940831/940907.LT .009 35 AIR 940907/940914 LT .013 35 AIR 940914/940921'LT .012 ! 35 AIR 940921/940928 LT .010 35 AIR '940928/941005 LT .009 l 35 AIR .941005/941012 LT .015 35 AIR 941012/941019 LT .009 35 '941019/941026 LT .017 t AIR 35 AIR 941026/941102 LT .006-35 AIR 941102/941189 LT .012 35 AIR 941109/941116 LT .014 -t 35 AIR' 941116/941123 LT .015
- 35. AIR 941123/941130.LT~.016 35 AIR. 1941130/941207 LT .008
- j. 35 AIR 941207/941214 LT .015 1
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N - CLEVELAUD ELECTRIC ILLUMIEATIUS CO. - PEPP. REMF TRACKIEC SYSTEM GAMMA SFRC CEPORT GF APTS SAMPLE FREQUENCY IS: QUARTERLY RESULTS IN PCI/CU.M. +/- 2 SIGMA AIR GAP 99L SPEC , STATION SAMPLE COLLECTION SE-7 CO-58 CO-68 CS-134 CS-137 LCCATION TYPE DATE S1 AIR 931229/940330 .066+/ .022 LT 881
. LT .002 LT .002 LT'.881 81 -AIR 940339/940629 .991+/ .814 LT .001 LT .001 LT .001 LT .901 01 AIR 948629/940928 .063+/ .019 LT 001
. LT .001 LT .001 LT .481 61 AIR 940928/941228 .070+/ .012 LT .001 LT .001 LT .001 LT .991 83 AIR 931229/940330 .074+/ .816 LT 801
. LT .001 LT .991 ~ LT .001 93 AIR 940330/940629 .097+/ .019 LT 001
. LT .001 LT .001 LT .981 03 AIR 940629/940928 .074+/ .018 LT 001
. LT .001 LT .891 LT .002 03 AIR 940928/941220 .074+/~.016 LT .001~ LT .001 LT .991 LT .401
- 04 AIR 931229/940330 .077+/ .017 LT 001
. LT .001 LT .001 LT .001 04 AIR -940330/940629 .092+/ .016 LT 401
. LT .001 LT .001 LT .001 84 AIR 940629/940928 .873+/ .022 LT .401 LT .001 LT .002 LT .002 04 AIR 949920/941228 .083+/ .015 LT .001 LT .001 LT .991 LT .001 05 AIR 931229/940330 .078+/ .022 LT 001
. LT .001 LT .001 LT .982 05 AIR 940330/940629 .085+/ .016 LT 001
. LT .001 LT .001 LT .081.
05 AIR 949629/940928 .069+/ .019 LT .001 LT .001 LT .982 LT .902 05 AIR 940928/941228 .675+/ .017 LT 001
. LT .001 LT .001 LT .001 06 AIR 931229/940330 .072+/ .015 LT 001
. LT .001 LT .381 LT .001 06 AIR 940330/940629 .081+/ .017 LT 001
. LT .001 LT .001 LT .991 06 AIR 940629/940928 .064+/ .022 LT 001
. LT .001 LT .001 LT .001 06 AIR 940928/941228 .070+/ .021 LT 601
. LT .001 LT .001 LT .991 07 AIR 931229/940330 .067+/ .017 LT 001
. LT .001 LT .991 LT .001 07 AIR 940330/940629 .000+/ .018 LT .001 LT .001 LT .001 LT .801 ,
07 AIR 949629/940928 .051+/ .029 LT 441
. LT .001 LT .991 LT .002 07 AIR 940928/941228 .080+/ .014 LT .001 LT .001 LT .001 LT .001
-35 AIR 931229/940330 .068+/ .017 LT 891
. LT .001- LT .002 LT .401 35 AIR 948339/940629 .058+/ .012 LT 001
. LT .001 LT .891 LT .001 35 AIR 940629/940928 .063+/ .019 LT 001
. LT .401 LT .001 LT .002 35 AIR 949928/941228 .067+/ .910 LT .001 LT .001 LT .001 LT .001 s
.g O
- ., o , . . - . - , ,- . *.,y - + - , , ,w , , - - , , , ,.
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- 5
- CAMMA SP3C. R3PSOT CF TTM 2j SAMPLE FCE";U2T.CY ISt,MILTOLT' EESULTS IU PCI/L +/-'2.51GMA' ;
PRFrTPTTATTON TRYTTifM STATION SAMPLE COLLECTION- H3 L3 CATION TYPE DATE 03 FR 931229/940126 LT 185.00 03 FR 940126/940223 LT 188.00 03 FR 940223/940330 LT 190.00 03 PR 940330/940427 LT 191.00 03 PR 940427/940525 LT 191.00 03 FR 940525/940629 LT 156.00 03 FR 940629/940727 LT 166.00 03 PR 940727/940824 LT 161.00 03 FR 940824/940928 LT 150.00 r. < 03 FR 940928/941026 LT 158.00 03 FR 941026/941130 LT 169.00 03 FR 941130/941228 LT 161.00 04 PR 931229/940126 LT 185.00 04 PR 940126/940223 LT 188.00 04 PR 940223/940330 LT 190.00 04 PR 940330/940427 LT 191.00 04 PR 940427/940525 LT 191.00 04 PR 940525/940629 LT 156.00 04 PR 940629/940727 LT 166.00 04 PR 940727/940824 LT 161.00 04 PR 940824/940928 LT 150.00 04 PR 940928/941026 LT 156.00 04 PR 941026/941130 LT 169.00 04 PR 941130/941228 LT 159.00 06 PR 931229/940126 LT 185.00 06 PR 940126/940223 LT 188.00 05 PR 940223/940330'LT 190.00 06 PR 940330/940427 LT 191.00 06 PR 940427/940525 LT 192.00 06 PR 940525/940629 LT 156.00 06 PR 940629/940727 LT 165.00 06 PR 940727/940824 LT 161.00
$6 PR 940824/940928 LT.150.00 06 PR 948928/941026 LT 156.00 06 PR 941026/941130 LT 169.00 06 PR 941130/941228 LT 161.00 07 PR 931229/940126 LT 185.00 07 PR 940126/940223 LT 188.00 07 PR 940223/940330 LT-190.00 07 PR 940330/940427 LT 191.00 07 PR 940427/940525 LT 192.00 07 PR 940525/940629 LT 156.00 07 PR 940629/940727 LT 166.00
CLEVELA2D ELECTHIC ILLUMICATINS Co. - FIFF. - SAMMA SPEC R2FCET CF TTM r. SAMPLE FREQUEWCT IS: MORTRLT- ,. RESULTS IN FCI/L +/- ' 2 SIGRA-PRFTTPTTATTON TRTTTID4 STATION SAMPLE COLLECTION N3 LOCATION TYPE ~ DATE 07 PR 940727/940824 LT 161.00 07 PR 940824/940928 LT 150.00 07 PR 940928/941026 LT 156.00 07 PR '941026/941130 LT 169.00 07 PR 941130/941228 LT 161.00 12 FR 931229/940126 LT 185.00 12 FR 940126/940223 LT 108.00 12 FR 940223/940330 LT 190.00 12 FR 940330/940427 LT 191.00 12 FR 940427/940525 LT 191.00 12 FR 940525/940629 LT 155.00 12 FR 940629/940727 LT 165.00 12 FR 940727/940824 LT 161.00 12 FR 940824/940928 LT 150.00 12 FR 940928/941026 LT 156.00 12 FR 941026/941130 LT 169.00 12 FR 941130/941228 LT 171.00 35 PR 931229/940126 LT 185.00 35 PR 940126/940223 LT 188.00 35 PR 940223/940330 LT 190.00 , 35 PR 940330/940427 LT 191.00 35 FR 940427/940525 LT 192.00 35 PR 940525/940629 LT 156.00 35 FR 940629/940727 LT 165.00 35 PR 940727/940824 LT 161.00 35 PR 940824/940928 LT 150.00 35 PR 940928/941026 LT 153.00 35 FR 941026/941130 LT 169.00 35 FR 941130/941228 LT 161'.00 l
, , ,- .. . . - - . , - - . , ...,+-,c, nn . , w , -. , , . , ,
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SAMPLE FCEEUSCCY ISt MO72T2LT RESULTS ED PCI/L +/- 2 SIEMA PRECIPITATION GROSS BETA '
?
COLLECTION PERIOD STATION LOCATIONS 03 04 06 07 12 35 JAN 931229 TO 940126 6.10+/ .70 6.50+/ .40 9.20+/ .50 1.80+/ .50 5.60+/~.60 6.90+/ .60 FEB 940126 TO 940223 8.50+/ .50 4.90+/ .40 4.90+/ .40 3.50+/ .30 5.30+/ .40 3.40+/ .30' .'" MAR 940223 TO 940330 10.90+/ .50 1.40+/ .30 8.30+/ .50 5.80+/ .40 5.10+/ .60 4.10+/ .40 APR 940330 TO 940427 12.20+/ .60 2.00+/ .30 6.90+/ .40 2.20+/ .30 6.80+/ .40. 4.60+/ .40 MAY 940427 TO 940525 5.00+/ .40 3.50+/ .30 1.90+/ .30 4.60+/ .40 6.00+/ .40 6.00+/ .40 JUN 940525 TO 940629 2.10+/ .40 2.20+/ .30 1.40+/ .20 2.20+/ .30 2.10+/~.30 1.50+/ .20 JUL 940629 TO 940727 3.50+/ .40 5.00+/ .50 3.80+/ .50 3.00+/ .40 3.60+/ .40 3.50+/ .60 AUO 940727 TO 940824 4.10+/ .30 3.60+/ .30 2.40+/ .30 2.60+/ .30 3.60+/ .30 3.10+/ .30 SEP 940824 TO 940928 5.60+/ .80 5.70+/ .90 3.20+/ .70- 2.60+/ .60 6.70+/ .60 4.40+/ .00
- OCT 940928 TO 941026 4.80+/ .60 3.20+/ .50 3.50+/ .50 3.80+/ .50 3.30+/ .50 5.00+/ .60 NOV 941026 TO 941130 16.30+/ .90 5.00+/ .40 8.00+/ .70 7.80+/ .70 6.60+/ .60 9.90+/ .70 DEC 941130 TO 941228 4.60+/ .60 2.80+/ .50 4.00+/ .50 '1.60+/ .40 4.60+/ .50 2.70+/ .50
CLEVELAND ELECTRIC ILLUMINATING CO. - P3PP. CAMMA SPEC CEPCCT CF P23 SAMPLE FDtMU0CCT IS: M2CTRLT RESULTS IN PCI/L +/- 2 SIGMA PRECIPITATTON STATION SAMPLE COLLECTION BA-140 Co-58 Co-60 CS-134 CS-137 LOCATION TYPE DATE FE-59 LA-140 MN-54 NS-95 En-65 ER-95 03 PR 931229/940126 LT 19.60 LT 2.00 LT 4.50 LT 2.70 LT 4.80 LT 8.90 LT 6.10 LT 2.20 LT 4.90 LT 7.20 LT 11.50 03 PR 940126/940223 LT 23.90 LT 1.80 LT 2.20 LT 5.00 LT 3.80 LT 5.C0 LT 2.60 LT 3.90 LT 2.70 LT 5.60 LT 7.10 03 PR 940223/940330 LT 20.30 LT 6.40 LT 1.60 LT 3.30 LT 3.80 LT 5.00 LT 3.20 LT 6.00 LT 2.20 LT 7.10 LT 2.30 03 PR 940330/940427 LT 18.50 LT 4.60 LT 8.00 LT 6.80 LT 6.60 LT 9.20 LT 5.50 LT 7.80 LT 5.10 LT 17.20 LT 10.70 03 PR 940427/940525 LT 22.30 LT 2.30 LT 2.90 LT 2.50 LT 4.50 LT 4.00 LT 2.10 LT 2.40 LT 3.60 LT 6.60 LT 5.10 03 PR 940525/940629 LT 27.90 LT 4.50 LT 4.00 LT 3.10 LT 4.40 LT 3.20 LT 3.40 LT 4.30 LT 2.90 LT 3.30 LT 5.60 03 PR 940629/940727 LT 36.60 LT 5.20 LT 5.20 LT 7.10 LT 5.90 LT 12.70 . LT 7.30 LT 3.20 LT 8.00 LT 10.20 LT 14.10 03 PR 940727/940824 LT 16.50 LT 4.00 LT 1.60 LT 1.80 LT 3.80 LT 2.40 LT 2.20 LT 3.90 LT 2.30 LT 8.00 LT 5.60 03 PR 940824/940928 LT 8.40 LT 2.40 LT 2.30 LT 2.70 LT 3.80 LT 6.20 LT 3.10 LT 4.30 LT 3.10 LT 1.90 LT 3.20 03 PR 940928/941026 LT 26.30 LT 4.10 LT 3.50 LT 2.20 LT 3.70 LT 2.10 LT 3.30 LT 3.10 LT 2.70 LT 3.70 LT 8.60 03 PR 941026/941130 LT 21.60 LT 4.50 LT 3.20 LT 3.50 LT 2.80 LT 3.00 LT 1.40 LT 2.60 LT 4.50 LT 5.10 LT 6.40 03 PR 941130/941228 LT 24.60 LT 4.50 LT 5.40 LT 6.80 LT 2.70 LT 5.30 LT 3.80 LT 4.90 LT 3.10 'LT 6.90 LT 6,70 04 PR 931229/940126 LT 15.30 LT 3.60 LT 2.30 LT 2.90 LT 2.90 LT 11.90 LT 3.70 LT 2.70 LT 2.70 LT 4.20 LT 6.20 04 PR 940126/940223 LT 13.50 LT 1.40 LT 2.80 LT 3.00 LT 3.00 LT 3.00 LT 3.10 LT 2.80 LT 2.50 LT 2.20 LT 4.10 04 PR 940223/940330 LT 16.90 LT 5.80 LT 3.20 LT 3.70 LT 4.00 LT 15.80 LT 1.70 LT 3.10 LT 3.00 LT 7.60 LT 4.00 5 4 _ _ _ _ _ . _ - ,__-_.__m _ _ _ - -
"^" ^', ,'llkbvE LACD ELECTRIC'ILLUMIRATING ~CO. l@PP..-
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Y- e.. .
- GAMMA SPEC REPORT OF PR$ '
SAMPLE F28tutECY IS: MSETELY RESULTS IB PC1/L +/ .2 SIGMA PRECTPTTATTON i !- STATION SAMPLE COLLECTION ~ BA-140 CO-58 CO-60 Cs-134- .CS-137 LOCATION TYPE DATE FE-59 LA-140 MW-54 95-95 EN-65 3R-95 4 t t 04 PR 940330/940427 LT 2".60 LT 4.70 ' LT 3.00 LT 5.40 LT'5.30 LT 10.70 LT 6.10 LT 2.40 LT 2.80 LT'10.10 LT 8.80 04 PR 940427/940525 LT 18.30 LT 3.50 LT 5.00 LT 5.70 LT 6.10 -i LT 9.10 LT 4.30 LT 4.20 LT 4 . 4 0 -- LT 4.00 LT 4.50 i 04 PR 940525/940629 LT 15.30 LT 3.20 LT 2.20 LT 3.20 LT 4.30 LT 2.90 LT 4.50 LT 3.60 LT 3.40 LT 3.60 LT 3.20 04 PR 940629/940727 LT 14.70 LT 2.20 LT 3.60 LT 3.20 LT 1.90. LT 2.90 LT 2.20 LT 1.50 LT 2.70 LT 2.50 LT 2.40 04 PR 940727/940824 LT 23.60 LT 1.20 LT 4.20 LT 1.90 LT 3.10. > LT 3.70 'LT 2.80 LT 2.60 LT 3.20 LT 5.10 2 LT 4.70 04 PR 940824/94092. s? 18.90 LT 2.30 LT 4.00 LT 4.10 LT 2.60' l LT m.40 LT 2.80 LT 4.40 LT 7.40 LT 8.40 LT 18.50 i 04 PR 940928/941026 LT 29.10 LT 2.70 LT 3.30 LT.3.60 LT 4.70 ' LT 2.60 LT 7.00 LT 5.90 LT 5.70 LT 13.50 : , LT 14.40 I 04 PR 941026/941130 LT 15.60 LT 4.80- LT 4.00 LT 6.30 LT 5.70-i LT 8.30 LT 6.20 LT 4.00 LT 4.70 LT 5.20 LT 4.20 04 PR 941130/941228 LT 15.20 LT 2.70 LT 3.10 LT 4.40 .LT 2.20 LT 3.30 LT 6.80 LT 1.70 LT 5.50 LT 7.80 LT 11.80 06 PR 931229/940126 LT 19.80 LT 1.50 LT 4.00 LT 2.30 LT 5.00 LT 5.40 LT 5.00 LT 4.00 LT-3.30. LT 2.60 , LT 3.20 1 06 PR 940126/940223 LT 21.30 .LT 1.60 LT 2.80 LT 4.10 LT 4.40
; LT 3.50: LT 1.40 LT 2.30 LT 4.00 LT 5.10:
LT 6.80 06 PR 940223/940330 LT 13.90 LT 5.10 LT 2.40' LT 4.50 LT 2.50 LT 2.90. LT 1.90 LT 2.90 .LT 2.90 LT'4.80 LT~6.60 06 PR 940330/940427 LT 23.90 LT 3.60 LT 3.00 LT 2.60 LT 4.30. ! , LT 3.40 LT 4.10 LT 2.60 LT 4.10 LT 4.50 a LT 3.30 06 PR 940427/940525 LT 27.10. LT 2.90 LT 5.30 LT 6.10 LT 6.90 LT 9.40 LT 4.10 LT 2.70 ..LT 6.50 LT 4.10 LT 4.90 06 PR 940525/940629 LT 11.00 LT 2.70 LT'4.50: LT 3.20 LT 5.80 LT 7.40' LT 2.20 .LT 4.90 LT 6.00- LT 9.30 LT 3.70
- _ _ _ _ _ _ - _ _ __ . - , - - - . - . . - - - - - . - - , -- -. . - - - - a- - - - - , . . . . .. - . . . . . . . _ - - _ _ -
i] CLEVELAUD ELECTRIC ILLUMINATICC CO. --P3PP. GAMMA SPEC REPCET CF POS SAMPLE FRCCUSCCY IS M0;T2LT RESULTS-IN PCI/L +/- 2 SIGMA PRECIPITATION ETATION SAMPLE COLLECTION BA-140 CO-58 CO-60 CS-134 CS-137 LOCATION TTPE DATE FE-59 LA-140 MN-54 NS-95 En-65 ER-95 06 PR 940629/940727 LT 32.30 -LT 4.70 LT 3.40 LT 2.10 LT 2.30 LT 5.70 LT 3.80 LT 3.90 LT 3.40 LT 4.60 LT 3.50 06 PR 940727/940824 LT 12.90 LT 2.60 LT 3.70 LT 4.00 LT 3.70 LT 5.90 LT 1.50 LT 2.10 LT 2.90 LT 4.50 LT 4.30 06 PR 940824/940928 LT 25.70 LT 4.80 LT 2.00 LT 6.00 LT 5.40 LT 6.70 LT 5.20 LT 3.40 LT 7.40 LT 11.70 LT 18.90 06 PR 940928/941026 LT 16.80 LT 2.90 LT 2.50 LT 2.50 LT 3.40 LT 4.50 LT 4.00 LT 2.90 LT 2.70 LT 4.30 LT 3.20 06 PR 941026/941130 LT 21.40 LT 2.30 LT 3.00 LT 1.90 LT 4.20 LT 2.80 LT 2.80 LT 2.00 LT 3.40 LT 3.20 LT 8. 7 0 '. OS PR 941130/941228 LT 17.00 LT 1.60 LT 2.30 LT 2.30 LT 3.00 LT 5.20 LT 1.60 LT 3.30 LT 3.40 LT 2.70 LT 9.30 07 PR 931229/940126 LT 22.90 LT 3.00 LT 3.70 LT 6.70 LT 4.90 LT 3.90 LT 4.60 LT 3.90 LT 3.00 LT'6.00 LT 12.80 07 PR 940126/940223 LT 8.60 LT 2.40 .LT 2.80 LT 2.40 LT 1.$0 LT 2.50 LT 3.80 LT 2.60 LT 2.30 LT 4.40 LT 5.10 07 PR 940223/940330 LT 28.50 LT 5.00 LT 5.50 LT.5.00 LT 2.90 LT 5.00 LT 3.20 LT 3.00 LT 3.80 LT 5.20 LT 9.50 07 PR 940330/940427 LT 16.20 LT 2.40 LT 1.50 LT 3.20 LT 4.20 LT 2.30 LT 4.30 LT 1.50 LT 3.50 LT 4.40 LT 6.70 07 PR 940427/940525 LT 18.10 LT 2.60 LT 3.60 LT 4.30 LT 5.60 LT 7.60 LT 2.80 LT 2.40 LT 4.10 LT 9.00 LT 5.70 07 PR 940525/940629 LT 21.30 LT 2.00 LT 1.40 LT 3.10. LT 3.70 LT 6.20 LT 2.10 LT 2.80 LT 1.60 LT 3.10 LT 5.30 07 PR 940629/940727 LT 26.70 LT 4.20 LT 1.10 LT 4.80 LT 4.50 LT 9.50 LT 3.00 LT 1.70 LT 3.80' LT 2.50' LT 3.90 07 PR 940727/940824 LT 19.70 LT 2.20 LT 5.80 LT 2.60 LT 6.00 LT 7.80 LT 2.20 LT 4.40 LT 4.40 LT 5.40 LT 3.00 07 PR 940824/940928 LT 22.00 LT 3.80 LT 3.60 LT 4.70~ LT 2.70 LT 4.10 LT 2.50 LT 1.80- LT 4.60 LT 6.20 LT 6.30 _ _ . = _ _ - - . m-~ , w mm. e - - -e.e- v,-. . .
a e o e GAMMA SPEC EEP3RT CF PDS SAMPLE FRSGU3%CT IS: M3172LT LESULTS I3 PCI/L +/- 2 SICMA PRECTPTTATTON STATION SAMPLE COLLECTION BA-140 Co-58 Co-60 LOCATION TYPE CS-134 CS-137 DATE FE-59 LA-140 MN-54 NS-95 EN-65 ER-95 07 PR 940928/941026 LT 25.10 LT 3.70 LT 2.00 LT 2.50 LT 4.40 LT 6.70 LT 2.70 LT 3.10 LT 4.10 LT 8.00 LT 8.00 07 PR 941026/941130 LT 17.30 LT 4.60 LT 2.40 LT 5.20 LT 3.00 LT 4.40 LT 3.70 LT 3.30 LT 2.70 LT 7.60 LT 10.50 07 PR 941130/941228 LT 12.70 LT 3.00 LT 2.00 LT 4.70 LT 5.30 LT 4.00 LT 2.80 LT 2.80 LT 2.50 LT 6.10 LT 8.00 12 PR 931229/940126 LT 21.80 LT 5.00 LT 4.10 LT 4.50 LT 5.40 LT 6.70 LT 2.20 LT 3.60 LT 3.20 LT 2.80 LT 7.90 12 PR 940126/940223 LT 27.80 LT 1.60 LT 2.00 LT 4.10 LT 5.90 LT 5.40 LT 2.10 LT 3.00 LT 3.90 LT 5.30 LT 5.80 12 PR 940223/940330 LT 5.50 LT 2.00 LT 1.70 LT 1.30 LT 1.80 LT 3.10 LT 1.90 LT 1.60 LT 2.10 LT 2.80 LT 3.40 12 PR 940330/940427 LT 13.80 LT 2.80 LT 1.90 LT 6.70 LT 4.20 LT 10.40 LT 3.50 LT 5.90 LT 8.40 LT 11.60 LT 13.20 12 PR 940427/940525 LT 12.30 LT 2.20 LT 1.90 LT 1.50 LT 2.90 LT 3.10 LT 2.20 LT 2.00 LT 2.00 LT 3.60 LT 4.50 12 PR 940525/940629 LT 20.00 LT 2.70 LT 3.80 LT 2.10 LT 4.10 LT 6.90 LT 2.30 LT 1.90 LT 5.10 LT 4.90 LT 2.20 12 PR 940629/940727 LT 33.60 LT 5.00 LT 4.20 LT 4.10 LT 4.40 LT 11.50 LT 3.80 LT 5.10 LT 3.80 LT 5.50 LT 3.80 12 PR 940727/940824 LT 19.80 LT 5.90 LT 2.00 LT 7.60 LT 4.70 LT 5.00 LT 3.30 LT 6.90 LT 7.80 LT 16.80 LT 13.80 12 PR 940824/940928 LT 43.10 LT 4.00 LT 4.60 LT 6.80 LT 3.70 LT 3.80 LT 8.90 LT 4.50 LT 6.00 LT 12.20 LT 7.20 12 PR 940928/941026 LT 13.90 LT 1.70 LT 2.40 LT 4.20 LT 2.80 LT 8.20 LT 2.40 LT 1.50 LT 2.20 LT 5.50 LT 4.10 12 PR 941026/941130 LT 23.40 LT 5.40 l LT 5.40 LT 3.70 LT 4.10 LT 9.10 LT 3.30 LT 4.00 LT 4.80 t LT 5.30 LT 6.50 j 12 PR 941130/941228 LT 15.90 LT 4.30 l LT 5.10 LT 2.10 LT 2.90 LT 8.60 LT 5.50 LT 4.80 LT 7.10 l LT 7.10 LT 6.00 l 1
CLEVELAND ELECTRIC ILLUMINATING CO . . - PNPP. e } GAMMA SPEC REP 02T OF PC SAMPLE FREQUE CT IS: MO TELY RESULTS IN PCI/L +/- 2 SIGMA PRECTPTTATTON STATION SAMPLE COLLECTION BA-140 CO-58 Co-60 CS-134 LCCATION TYPE CS-137 DATE FE-59 LA-140 MN-54 35-95 EN-65 3R-95 l 35 PR 931229/940126 LT 21.70 LT 2.10 LT 3.30 LT 4.10 LT 3.00 LT 8.70 LT 2.60 LT 2.90 LT 4.40 LT 3.10 LT 8.10 35 PR 940126/940223 LT 11.90 LT 2.70 LT 3.30 LT 4.20 LT 3.20 LT 6.00 LT 3.80 LT 2.30 LT 3.50 LT 3.10 LT 7.10 35 PR 940223/940330 LT 20.30 LT 3.60 LT 2.80 LT 5.60 LT 4.80
- LT 6.40 LT 2.60 LT 4.30 LT 3.00 LT 7.50
- LT 7.10 i 35 PR 940330/940427 LT 12.80 LT 3.40 LT 3.60 LT 5.90 LT 5.30 LT 4.30 LT 2.70 LT 4.70 LT 2.90 LT 3.20 LT 9.30 1 35 PR 940427/940525 LT 22.50 LT 4.20 LT 4.60
' LT 3.60 LT 3.70 LT 4.90 LT 3.70 LT 3.70 LT 4.10 LT 5.60 LT 5.60 + 35 PR 940525/940629 LT 27.50 LT 2.30 LT 2.70 LT 2.60 LT 3.10 LT 5.30 LT 3.30 LT 2.20 LT 5.20 LT 3.20 LT 7.00 35 PR 940629/940727 LT 25.80 LT 5.40 LT 2.10 LT 2.80 LT 6.40 LT 10.50 LT 5.30 LT 4.40 LT 1.70 LT 6.40 LT 9.30 35 PR 940727/940824 LT 27.80 LT 2.80 LT 3.40 LT 2 70 LT 4.90 LT 6.20 LT,3.40 LT 3.30 LT 3.40 LT 6.60-LT 8.50 35 PR 940824/940928 LT 12.20 LT 3.70 LT 1.40 LT 2.00 LT 2.00
- LT 5.40 LT 2.40 LT 2.20 LT 4.40 LT 2.70 LT 4.90 35 PR 940928/941026 LT 32.70 LT 4.10 LT 2.00 LT 4.60 LT 1.80 LT 8.30 LT 5.00 LT 4.40 LT 5.60 LT 3.00 LT 4.10 35 PR 941026/941130 LT 38.80 LT 6.20 LT 3.80 LT 5.00 LT 3.80 LT 9.10 LT 4.00 LT 6.60 LT 4.70 LT 6.00 LT 13.60 35 PR 941130/941228 LT 26.20 LT 3.60 LT 4.40 LT 3.90 LT 3.40 LT 4.80 LT 4.90- LT 3.10 LT 4.30 LT 7.20 LT 13.70 E h
- . . _ - , ~ . - - - . _ _ - - - , = . - > - - , , , . ~ - ~ - .._,. - _ _-
v ~- - ~ ~ -- - - .--~~,,r--
*
- CELP T2ACKICG SYSTEM , y, CAMMA RFEC CEF@2? CF MLEI SAMPLE FIEt%EOCY IS: BI-MTCTOLT/ME%TOLY GESOLTS 10 PCI/L +/- 2 SIEMA MIIK IODINE s ..
STATION SAMPLE COLLECTION 1-131 LCCATION TYPE DATE 51 MILE 940107/940110 LT .50 51 MILE 940211/940214 LT .50 51 MILE 940311/940314 LT .40 51 MILK 940415/940418 LT .40 51 MILE 940506/940509 LT .20
$1 MILE 940520/940523 LT .20 51 MILK 940603/940606 LT .20 51 MILE 940617/940620 LT .30 51 MILE 940708/940711 LT .30 51 MILE 940722/940725 LT .20 51 MILE 940805/940808 LT .40 51 MILE 940819/940822 LT .40 51 MILE 940902/940906 LT .40 51 MILK 940916/940919 LT .40 51 MILK 941006/941010 LT .20 51 MILE 941021/941024 LT .20 51 MILK 941104/941107 LT .20 51 MILK 941202/941205 LT .40 61 MILE 940415/940418 LT .30 61 MILK 940506/940509 LT .20 61 MILE 940520/940523 LT .20 61 MILE 940603/940606 LT .20 61 MILK 940417/940620 LT .40 61 MILK 940708/940711 LT .30 61 MILE 940722/940725'LT .20 61 MILE 940805/940808 LT .40 61 MILK 940819/940822 LT .40 61 MILK 940902/940906 LT .30 61 MILK 940916/940919 LT .30 61 MILK 941006/941010 LT .10 61 MILK 941024/941027 LT .30 61 MILE 941104/941107.LT .30 71 M1LK 940107/940110 LT .40 71 MILE 940211/940214 LT .40 71 MILE 940311/940314 LT .40 71 MILE 940415/940418 LT .30 71 MILE 940506/940509 LT .20 71 MILE 940520/940523 LT .40 71 MILK 940603/940606 LT .20 71 MILK 940617/940620 LT .30 71 MILK 940708/940711 LT .30 71 MILK 940722/940725 LT .20 71 MILK 940805/940808 LT .40 71 MILE 940819/940822 LT .40
CLEVELAED ELECT 2fC ILLUMICATIEG CO.- - PEPP. , REMP TuACKIDS SYSTEM t GAMMA SPEC R3FSCT 4F MLEI ' SAMPL3 FCEYiEOCY IS: CZ-DCNTELY/MSOT3LY RESULTS IN FCI/L +/- 2 SIGMA MIIJC ICDINE CTATION' SAMPLE COLLECTION' I-131' LCCATION TYPE DATE , 71 MILE '940902/940906 LT .30 71 MILE 940916/940919 LT .40' i 71 MILE 941006/941010 LT .10
- 71 MILE 941021/941024 LT .20 71 MILE 941104/941107 LT .30 71 MILE 941202/941205 LT .20 i
l-1 i l
- - . . - . - ~ - - . . - - - --
a .A
- REMF TRACKIdG SYSTEM *-
ej GAMMA SPEC REFSGT 6F MLES SAMPLK FREST3tfCT IS* DI-MONT"LY/MONTELY RESULTS 10 FCI/L +/- 2 SIEMA MILK C"J7" SPfr' STATION SAMPLE COLLECTION BA-140 CS-134 CS-137 E-40 LA-140 LOCATION TTFE DATE 51 MILK 940197/94e110 LT 13.4 LT 4.9 LT 3.6 1528.0+/-209.8 LT 3.3 51 MILK 948211/940214 LT 9.2 LT 4.4 LT 3.4 1500.0+/-100.9 LT 9.9 51 MILE 940311/940314 LT 20.2 LT 6.9 LT 6.4 1480.9+/-180.0 LT 3.6 51 MILK 940415/940418 LT 9.9 LT 3.9 LT 4.1 1618.8+/-100.0 LT 1.6-51 MILK 948506/940509 LT 16.1 LT 5.1 LT 4.9 1478.S+/-120.0 LT 1.7 51 MILE 940520/940523 LT 12.1 LT 4.7 LT 3.4 1460.8+/-100.8 LT 2.1 51 MILE 940603/940606 LT 22.8 LT 6.2 LT 3.5 1440.0+/-150.8 LT 3.2 51 MILE -940617/940620 LT 15.0 LT 5.9 LT 4.9 1458.e+/-150.9 LT 4.9 51 MILE 949708/940711 LT 27.4 LT 6.3 LT 6.1 1470.e+/-170.0 LT 3.1 51 MILE 940722/940725 LT 13.8 LT 5.9 LT 4.4 1460.8+/-150.8 LT 2.5 51 MILK 940805/940808 LT 23.3 LT 2.7 LT 6.2 1358.0+/-150.0 LT 3.2 51 MILK 940819/940822 LT 7.8 LT 3.8 LT 3.8 1829.e+/-120.0 LT 1.6 51 MILE 940902/940906 LT 26.7 LT 7.5 LT 4.6 1320.S+/-180.9 LT 2.7 51' MILE 940916/940919 LT 40.6 LT 3.5 LT 7.4 1498.8+/-170.8 LT 3.5 t 51 MILK 941006/941010 LT 14.8 LT 3.0. LT 4.7 1418.0+/-120.0 LT 3.1 51 MILK 941021/941024.LT 27.8 LT 5.9 LT 4.6 1369.9+/-140.0 LT 8.2 51 MILK 941104/941107 LT 33.9 LT 6.1 LT 3.5 1550.0+/-200.0 LT 4.1 51 MILK 941202/941205 LT 12.4 LT 3.3 LT 4.2 1500.0+/-110.8 LT 2.6 61 MILE 940415/940418 LT 15.7 LT 2.9 LT 6.0 1780.e+/-160.0. LT 2.6 61 MILE 940506/940509 LT 19.8 LT 5.6 LT 5.8 1860.0+/-150.0 LT 1.7 61 MILK 940520/940523 LT 6.0 LT 2.3 LT 3.0 1928.9+/-99.0 LT 1.6 61 MILK 940603/940606 LT 33.4 LT 4.7 LT 7.7 1820.9+/-180.0 LT 2.6 61 MILE 940617/940620 LT 29.0 LT 5.0 LT 5.1 1859.S+/-168.8 LT 2.6 61 MILE 940708/940711 LT 15.6 LT 3.4 LT 5.3 1950.0+/-184.9 LT 3.2 61 MILE 940722/940725 LT 11.8 LT 3.4 LT 4.5 1860.0+/-138.9 LT 2.7 61 MILK 940805/940808 LT 34.8 LT 5.3' LT 6.3 1740.0+/-150.9 LT 7.0 61 MILK 940819/940822 LT 17.7 LT 3.7 LT 4.2 1450.0+/-129.9 LT 1.6 61 MILK 949902/940906 LT 18.1 LT 4.9 LT 5.1 1870.9+/-190.0 LT 6.5 61 MILK 940916/940919 LT 28.4 LT 5.6 LT 7.1 1780.0+/-190.0 LT 3.1 61 MILE 941006/941010 LT 15.3 LT 7.3 LT 6.1 1819.0+/-110.8 LT 2.6 i 61 MILE 941024/941027 LT 9.6 LT 3.0 LT 4.1 1850.0+/-120.0- LT 3.5 61 MILK 941104/941107 LT 25.2 LT 5.3 LT 5.5 1930.4+/-140.0 LT 1.8 71 MILK 940107/940110 LT 10.1 LT 5.6 LT 6.8 1400.9+/-160.0 . LT 2.8 71 MILK 948211/940214 LT 19.0 LT 5.5 LT 5.7 1280.0+/-140.0 LT 2.7 71 MILE 940311/940314 LT 13.7 LT 2.5 LT 6.7 1350.0+/-120.0 LT 2.3 71 MILK 940415/940418 LT 18.7 LT 8.9 LT 7.7 1280.0+/-160.8 LT 3.5 71 MILK 940506/940509 LT 18.8 LT 5.4 LT 5.7 '1210.0+/-160.0 .LT 2.9 11 MILK 940520/940523 LT 23.4 LT 5.2 LT 6.2' 1269.9+/-128.8 LT 6.6 , l 71 MILE 940603/940606 LT 24.7 LT 4.8 LT 6.1 1300.9+/-130.9 LT'2.0 ! 71 MILE 940617/940620 LT 14.0 LT 3.7 LT 3.7' 1248.0+/-100.8 LT 3.8 ( 71 MILE 940708/940711 LT 11.7 LT 3.7 LT 3.7 1220.0+/-119.8 LT 1.9 71 MILE 940722/940725 LT 25.4 LT 6.1 LT 6.1 1388.0+/-140.9 LT 2.7-71 MILK 940805/940808 LT 31.7 LT 8.0 LT 7.1 1419.e+/-179.s' .LT 3.8 71 MILE 940819/940822 LT 16.6 LT 2.4 LT 2.8 1290.0+/-140.9 LT 1.9
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, . REMP TCACKICG SYSTEM , ,
GAMMA SPEC REPCOT CF FP SAMPLE FR2CTEOCT ISI MrOT2LY CESULTS 13 FCI/ES(CET) +/- 2 SICMA M MM CJIMM RPW' STATION SAMPLE COLLECTION BE-7 Co-58 CO-60 CS-134 CS-137 LOCATION TYPE DATE I-131 E-40 62 BROCCOLI 940809/940805 LT 73.80 LT 12.50 LT 5.20 LT 11.40 LT 15.10 LT 8.20 3016.0+/-369.0 62 CABBAGE 940809/940809 LT 51.50 LT 11.80 LT 9.40 LT 10.40 LT 9.30-LT 15.50 2122.0+/-239.0 62 BROCCOLI 940913/940913 LT 88.00 LT 7.90 LT 5.10 LT 13.78 LT 10.50 LT 15.00 3644.0+/-296.0 62 BEET GREENS 940913/940913 LT 171.00 LT 15.90 LT 14.40 LT 16.20 LT .J.60 LT 32.50 7604.0+/-540.0 62 CABBAGE 940913/940913 LT 40.00 LT 3.20 LT 6.10 LT 8.30 LT 6.60 LT 14.60 1828.0+/-171.0 62 BEET GREENS 941014/941014 LT 192.00 LT 19.70 LT 25.20 LT 16.00 LT 12.20 LT 27.50 6356.0+/-557.0 62 CABBAGE 941014/941014 LT 88.00 LT 12.80 LT 8.30 LT 12.60 LT 10.50 LT 20.40 2032.0+/-263.0 70 CABBAGE 940728/940728 LT 73.50 LT 8.10 LT 6.30 LT 4.40 LT 10.00 LT 15.70 2232.0+/-227.0 70 BEET GREENS 940728/940728 200.0+/-107.0 LT 6.40 LT 10.60 LT 13.10 LT 16.20 LT 11.30 6172.0+/-423.0 70 BROCCOLI 940809/940809 LT 158.00 LT 16.10 LT 12.00 LT 8.50 LT 17.90 LT 20.90 3762.0+/-409.0 70 CABBAGE 940809/940809 LT 127.00 LT 4.10 LT 14.20 LT 17.50 LT 18.60 LT 24.80 2132.0+/-325.0 70 BEET GREENS 940809/940009 224.0+/-118.0 LT 12.30 LT 5.80 LT 12.40 LT 15.30 LT 19.40 4543.0+/-425.0 70 CABBAGE 940913/940913 LT 127.00 LT 4.80 LT 8.00 LT 7.10 LT 12.20 LT 21.20 1984.0+/-284.0 70 RED CA8BAGE 940913/940913 LT 115.00 LT 6.20 LT 10.40 LT 10.60 LT 5.50 LT 10.60 2839.0+/-321.0-70 CAULIFLowtR 940913/940913 LT 81.00 LT 5.50 LT 3.10 LT 10.50 LT 7.80 LT 13.70 3054.0+/-309.0 77 DILL 940728/940728 LT 115.00 LT 7.90 LT 13.60 LT 9.40 LT 13.30 LT 17.70 6089.0+/-375.0 77 TURNIP GREENS 940728/940728 LT 84.10 LT 3.10 LT 4.80 LT 8.30 LT 8.80 LT 13.60 4174.0+/-247.0 77 L"TTUCE 940728/940728 248.0+/-102.0 LT 8.70 LT 11.00 LT 10.80 LT 11.10 LT 13.70 3916.0+/-293.0 77 BEET GREENS 940809/940809 LT 133.00 LT 5.00 LT 9.60 LT 12.20 LT 11.50 LT 16.00 4819.0+/-403.0 77 TURNIP GREENS 940809/940809 LT 127.00' LT 14.60 LT 11.20 LT 14.60 LT 15.60 LT 14.70 6128.0+/-474.0 77 DILL 940809/940809 177.0+/-65.0 LT 5.10 LT 9.30 LT 7.60 LT 8.80 LT 5.00 3789.0+/-250.0 77 TURNIP GREENS 940913/940913 LT 119.00 LT 13.70 LT 16.50 LT 6.50 LT 13.50 LT 21.10 4541.0+/-393.0
. CLEVELAND ELECTRIC ILLUMIRATIEG CO. - PEPP. ~
REMP TRACKITG SYSTEM .4. v GA*.MA SPEC'2EP%il? 6F FP
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SAMPLE FREQUENCY I5 MONTNLT s RESULTS IN FCI/KG(WET) +/- 2 SIGMA M PRfvim (**_S. Rppr
- 5TATION SAMPLE: COLLECTION BE-7 CO-58 CO-69 C5-134 CS-137 LOCATION' TYPE DATE I-131 E-te 77 SEET GREENS 940913/940913 LT 176.00 LT 19.70 LT 11.50 LT 21.90' 'LT 22.99 LT 14.40 7741.0+/-579.9 17 DILL 948913/948913.334.8+/-144.8 LT 12.79 LT 12.89 LT 13.18 LT 7.00
- LT 25.10 4237.0+/-377.9 77 ' TURNIP GREENS 941014/941014 583.0+/-101.8 LT 5.30- LT.6.79 LT 5.38 .LT 7.79 LT 4.00 4750.e+/-249.0 '
77 BERT GREENS 941014/941014 471.0+/-156.8 LT 10.50- LT 12.70 LT 14.90 LT 15.30 LT 22.29 7429.0+/-420.9 . 77 DILL 941914/941014 602.9+/~190.8 LT 18.39 LT 11.29 . LT 19.30- LT 9.29 LT'23.48 4564.S+/-378.8
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'm' " "Tr CAMMA SPEC REPCGT.EF FP SAMPLE F2EQUETCT IS: MO2TCLT ESSELTS IN PCI/KG(WET) +/- . 2 S !tNA -
GULSS GN44A SPH' STATION SAMPLE COLLECTION BE-7 Co-58 Co-60 Cs-134 Cs-137 LCCATION .TTPE DATE I-131 K-40 06 GRASS 940516/940516 617.0+/-86.0 LT 6.50 LT 10.80 LT 7.50 LT 7.50 LT 6.00 4267.0+/-189.0 06 GRASS 940621/940621 1236.0+/-120.0 LT 9.10 'LT 9.70 . LT 7.10 LT 8.50 LT 12.20 5080.0+/-264.0 06 GRASS 940711/940711 4446.0+/-217.0 LT 9.50 LT 14.00 LT 12.40 LT 11.20 06 GRASS LT 18.80 4511.0+/-264.0 940816/940816 9074.0+/-555.0 LT 11.40 LT 27.20 LT 12.60 LT 27.10 GRASS LT 24.40 7192.0+/-674.0 06 940920/940920 1622.0+/-288.0 LT 16.10 LT 15.40 LT 17.70 LT 18.50 LT 31.30 5972.0+/-562.0 06 GRASS 941018/941018 4838.0+/-425.0 LT 16.50 LT 17.20 LT 27.20 LT 22.00 LT 22.30 6466.0+/-580.0 07 GRASS 940516/940516 3580.0+/-172.0 LT 4.70 LT 13.60 LT 6.30 LT 12.20 LT 11.80 4268.0+/-246.0 07 GRASS 940621/940621 2045.0+/-168.0 LT 9.30 LT 15.50 LT 11.30 LT 14.00 LT 15.10 5814.0+/-312.0 07 grass 940711/940111 3396.0+/-141.0 LT 6.60 LT 11.80 LT 10.10 LT 9.10 LT 13.70 5153.0+/-232.0 07 grass 940816/940816 4134.0+/-340.0 LT 19.20 LT 18.20 LT 11.60 LT 16.90 LT 31.20 -6786.0+/-534.0 07 GRASS 940920/940920 1015.0+/-227.0 LT 13.50 LT 7.20 LT 17.00 LT 9.30 07 LT 34.50 5387.0+/-532.0 GRASS 941018/941018 4192.0+/-340.0 LT 20.60 LT 14.80 LT 15.80 LT 18.90 LT 40.20 4637.0+/-521.0 35 GRASS 940516/940516 5167.0+/-149.0 LT 7.00 LT 8.80 LT 6.50 LT 7.00 LT 13.30 3674.0+/-153.0 35 grass 940621/940621 1553.0+/-211.0 LT 16.10 LT 15.10 LT 13.50 LT 19.50 LT 25.10 6317.0+/-418.0 35 GRASS 940711/940711 3163.0+/-234.0 LT 12.90 LT 14.40 LT 7.30 LT 14.50 LT 23.10 5839.0+/-354.0 35 GRASS 940816/940816 2901.0+/-276.0' LT 20.80 LT 10.40 LT 19.10 LT 15.40 LT 36.80 5909.0+/-478.0 35 GRASS 940920/940920 1495.0+/-487.0 LT 29.50 LT 40.90 LT 36.10 LT 29.90 LT 40.70 5043.0+/-787.0 35 GRASS 941018/941018 6674.0+/-471.0 LT 16.70 LT 16.50 LT 15.60 LT 32.60 LT 26.80 5820.0+/-593.0 l l _ . _ . ,. . _ _ . _ _ _ . . . _ _ _ _. _ . . . _ . .m . _
. . ~. . . . -.. . . CLEVELA2D ELECTRIC ILLUMIRATIEC Co. - PNPP. REMP TRACRING' SYSTEM ' ~ GAMMA SPEC REPCRT OF SOIL ^ SAMPLE FREQUERCY 25 SEM-A2CUAL ' f RESULTS-IN PCI/EGtDRY) +/- 2 SIGMA SOIL GAMMA SPEC STATION SAMPLE COLLECTION Co-58 Co-60 CS-134 CS-137 E-40 ' LCCATroN TYPE DATE RA-226
=
2 03 SOIL 940414/940414 LT 28.1 LT 24.3 LT 55.5 264.0+/-32.0 11352.0+/-621.0 1634.0+/-391.0 . r 93 SOIL 940914/940914 LT 40.5 LT 24.0 LT 50.1 263.0+/-37.0 10614.0+/-564.0 i 1187.0+/-357.0 04 soil 940414/940414 LT 24.8 LT 26.5 LT 59.9 79.0+/-25.0 13851.0+/-700.0 l 1635.0+/-399.0 04 SOIL 940914/940914 LT 22.1 LT 19.6 LT 43.4 65.0+/-21.0 13366.0+/-536.0 1358.0+/-245.0 06 SOIL 940414/940414 LT 17.1 LT 18.1 LT 53.0 218.0+/-32.0 .15048.0+/-782.0 $ 2269.0+/-470.0 06 SOIL 940914/940914 LT 24.0 LT 17.7 LT 31.8 215.0+/-30.0 15324.0+/-428.0 2140.0+/-262.0 07 SOIL 940414/940414 LT 33.7 LT 33.5 LT 38.4 422.0+/-47.0 12529.0+/-769.8 d 1358.0+/-428.0 07 soil 940914/940914 LT 19.3 LT 17.1 LT 26.7 413.0+/-29.0 11922.0+/-450.0 1459.0+/-250.0 09 soil 940414/940414 LT 30.7 . LT 17.6 LT 55.5 377.0+/-40.0 11664.0+/-717.0-1346.0+/-370.0 09 soil 940914/940914 LT 16.9 LT 20.8 LT 24.6 407.0+/-36.0 11857.0+/-608.0 1311.0+/-338.0
\
12 soil 940414/940414 LT 24.2 LT 24.7 LT 67.4 528.0+/-124.0 13765.0+/-1510. . 1638.0+/-486.0 12 soil - 540914/940914 LT 28.7' LT-25.6 LT 29.5 461.0+/-36.0 11076.0+/-586.0 1394.0+/-353.0 -t i 35 soil 940414/940414 LT 33.2 LT 23.3 LT 56.5 225.0+/-30.0 1' 19 6 0 . 0 +/- 6 6 3. 0 - 1381.0+/-361.0 35 soil 940914/940914 LT 24.8 LT 21.5 LT 50.0 199.0+/-29.0 11770.0+/-562.0 1157.0+/-293.0 ,
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DI SAMPL3 FCE!U30CY IS!' MONTHLY E2STLTS IS PCI/L +/- 2 SICMA WATER GROSS BETA COLLECTION PERIOD STATION LOCATTONS 28 34 36 59 60 g JAN 931230 TO 940127 2.30+/ .60 940127 TO 940127 4.80+/ .70 3.00+/ .60 FEB 940127 TO 940224 1.90+/ .60 2.50+/ .40 940224 TO 940224 2.70+/ .70 MAR 940224 TO 940331 2.50+/ .70 2.20+/ .60 2.60+/ .60 APR 940331 TO 940428 1.90+/ .60 2.30+/ .70 1.00+/ .70 940421 TO 940428 2.80+/ .60 3.00+/ .60 MAY 940428 TO 940526 2.20+/ .60 2.50+/ .60 2.60+/ .60 2.60+/ .60 1.90+/ .60 JUN 940526 TO 940630 2.10+/ .70 1.60+/ .70 1.60+/ .70 2.50+/ .70 2.50+/ .60 JUL 940630 TO 940720 2.00+/ .60 1.70+/ .70 2.00+/ .70 2.50+/ .60 1.60+/ .60 AUG 940728 TO 940825 3.00+/ .50 3.20+/ .60 2.70+/ .60 3.10+/ .60 3.60+/ .60 SEP 940825 TO 940929 1.50+/ .50 1.90+/ .60 2.10+/ .60 3.00+/ .60 940929 TO 940929 3.40+/ .70 , OCT 940929 TO 941027 1.30+/ .50 2.50+/ .60 2.30+/ .60 1.80+/ .50 941027 TO 941027 2.20+/ .60 NOV 941027 TO 941128 2.40+/ .30 2.20+/ .30 2.80+/ .30 3.80+/ .40 941128 TO 941128 2.90+/ .60 DEC 941128 TO 941229 2.30+/ .60 2.50+/ .60 3.00+/ .60 2.90+/ .40 941229 TO 941229 2.70+/ .60 l i l
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CLEVELAND ELECTRIC ILLUMINATING Co. - PNPP.
, REMP TRACKIBG SYSTEM i
GAMMA SPEC'REPO2T OF WTRG - SAMPLE FREQUENCY IS: MONTNLY RESULTS IN PC2/L +/- 2 SIGRA WATER 1 STATION SAMPLE COLLECTION BA-140 CO-5 8 ~ Co-60 Cs-134- CS-137 LOCATION TYPE DATE FE-59 LA-140 MW-54 Ns-95 55-65 1 ER-95 l i 28 WATER 940127/940121 LT 24.10 LT 2.90 LT 3.40 LT 3.20 LT 4.70' LT 3.80 LT 4.50 LT 4.60 LT 3.80 LT 4.10 i LT 7.20 28 WATER 940127/940224 LT 20.70 LT 2.90 LT 3.40 'LT 4.60 LT.4.40 LT 3.30 LT 1.80 LT 2.10 LT 4.10 LT 4.68 LT 3.30 28 WATER 940224/940331 LT 9.40 LT 3.00 LT 2.80 LT 2.50 LT 3.58 LT 4.10 LT 2.50 LT 1.00 LT.4.10 LT 3.59 LT 6.80 28 WATER 940331/940428 LT 31.40 LT 4.40 LT 3.10 LT 7.90 LT 8.48 LT 18.10 LT 3.80 LT 3.79 LT 7.90 LT 7.80 LT 4.80 28 WATER 940428/940526 LT 34.20 LT 3.00 LT 2.00 LT 3.50 LT 5.44 , LT 6.00 LT 6.30 LT 3.80 LT 4.70 LT 5.50-LT 4.00 28 WATER 940526/940630 LT 13.20 LT 2.50 LT 1.60 LT 4.90 LT 5.70 LT 8.40 LT 5.40 LT 4.60 LT 6.40 LT 10.00 LT 7.80 28 WATER 940639/940728 LT 21.50 LT 2.80 LT 1.80 LT 3.20 LT 2.60 LT 4.70 . LT 7.00 LT 2.20 LT 3.90 LT 4.90 LT 4.90 28 WATER 940728/940825 LT 18.20 LT 1.00 LT 3.80 LT 2.20 LT 1. 9 0 - LT 3.00 LT 2.00 LT 3.10 LT 4.20 LT 4.70 LT 5.90 ~ 28 WATER 940929/940929 LT 29.10 LT 5.70 LT 1.40 LT 3.10 . LT 4.10' LT 4.50 LT 2.60 LT 3.40 LT 5.00 .LT 8.70
' LT 10.00 28 WATER 941027/941027 LT 20.90 LT.7.90 LT 4.40 LT 5.40 LT 3.48 LT 4.20 LT 2.00 LT 4.40 LT 4.90 LT 5.60 LT 6.75 28 WATER 941120/941128 LT 12.80 LT 2.30 LT 2.20 LT 1.40' LT 3.50 LT 4.50 LT 3.16' LT 1.00 LT 3.10 LT 2.29
, LT 2.70 28 WATER 941229/941229 LT 23.20 LT 3.80 LT 1.60 LT 2.90 LT 5.48 LT 6.00 LT 5.88 LT 3.80 LT 3.30 LT 4.40 LT 8.30 34 WATER 931230/940127 LT 17.80. LT 2.56 LT 5.10 ' LT 3.06 'LT 2.38 LT 9.20 LT 4.20 LT 3.30 LT.3.80 LT 6.50 LT 8.19 34 WATER 940127/940224 LT 17.90 LT 3.80 , LT 1.60 LT 2.20. LT 4.19 LT 7.80 LT 3.70 LT 2.19 .LT 3.10 LT 3.60 LT 3.10 . . i 34 WATER 940224/940331 LT 23.50. LT 4.20 ' LT.1.Se LT 3.10 LT 5.89-LT 5.60- LT 4.19~ LT 5.00 .LT 3.30- LT 5.49 i LT 4.60 i _ _ _ _ _ _m- ____m_.-
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REMP TRACKIDG SYSTZM- * .- SAMMA SPEC RSPO2T OF WTOS SAMPLE FREQUECCT 15: MINT 2LY RESULTS IN PC1/L +/- 2 SIEMA VATER STATION SAMPLE COLLECTION BA-140 CO-58 Co-60 CS-134 CS-137 LOCATION TYPE DATE FE-59 LA-140 MN-54 MB-95 SN-65 2R-95 34 WATER 940331/940428 LT 13.20 LT 2.20 LT 2.70 LT 2.30 LT 2.70 LT 4.00 LT 1.80 LT 2.50 LT 2.10 LT 2.70 LT 5.80 34 WATER 940428/940526 LT 37.50 LT 4.70 LT 6.50 LT 6.60 LT 5.20 LT 4.30 LT 3.70 LT 5.50 LT 7.60 LT 11.70 LT 4.30 34 WATER 940526/940630 LT 19.50 LT 1.70 LT 1.10 LT 3.30 LT 3.50 LT 1.60 LT 1.80 LT 2.40 LT 3.20 LT 2.90 LT 2.40 34 WATER 940630/940728 LT 22.00 LT 1.70 LT 2.60 LT 3.70 LT 4.60 LT 4.30 LT 4.00 LT 2.30 LT 3.90 LT 5.00 LT 6.40 31 WATER 940728/940825 LT 10.70 LT 1.80 LT 3.00 LT 2.50 LT 2.80 LT 4.00 LT 1.80 LT 1.20 LT 2.90 LT 2.40 LT 5.40 34 WATER 940825/940929 LT 11.90 LT 1.80 LT 1.10 LT 3.10 LT 1.90 LT 7.30 LT 2.20 LT 1.50 LT 2.80 LT 5.10 LT 3.00 34 WATER 940929/941027 LT 14.80 LT 3.60 LT 2.50 LT 1.60 LT 4.80 LT 1.60 LT 2.10 LT 3.40 LT 3.40 LT 4.30 LT 2.60 34 WATER 941027/941128 LT 19.90 LT 3.90 LT 1.50 LT 2.10 LT 4.20 LT 2.50 LT 2.30 LT 1.90 LT 6.20 LT 4.10 LT 5.20 34 WATER 941128/941229 LT 21.40 LT 1.60 LT 4.20 LT 3.90 LT 4.10 LT 7.30 LT 2.40 LT 3.50 LT 1.70 LT 7.80 LT 8.20 36 WATER 940127/940127 LT 11.90 LT 3.20 LT 4.00 LT 3.10 LT 4.40 LT 3.80 LT 3.00 LT 2.50 LT 3.90 LT 4.00 LT 6.60 36 WATER 940224/940224 LT 26.90 LT 4.30 LT 3.60 LT 5.10 LT 2.70 LT 11.10 LT 5.00 LT 4.40 LT 5.20 LT 9.00 LT 7.20 36 WATER 940224/940331 LT 14.00 LT 1.80 LT 2.20 LT 2.60 LT 2.80 LT 4.80 LT 2.00 LT 1.50 LT 2.80 LT 3.10 LT 2.00 36 WATER 940331/940428 LT 16.50 LT 3.30 LT 2.70 LT 4.10 LT 4.20 LT 6.10 LT 5.00 LT 2.40 LT 1.70 LT 4.50 LT 5.10 36 WATER 940428/940526 LT 24.60 LT 3.60 LT 4.60 LT 4.50 LT 3.00 LT 4.00 LT 3.10 LT 3.80 LT 1.90 LT 4.50 LT 5.20 36 WATER 940526/940630 LT 16.50 LT 3.00 LT 3.00 LT 4.00 LT 4.60 LT 4.20 LT 1.90 LT 3.50 LT 2.00 LT 5.50 LT 5.50
. . . , . - - . - . .,. ~ , . ,- .. -. , . -. .. , . - - . . - , - - . . -
.3 CLEVELAND ELECTRIC ILLUMICATICC CO. - FCPP.
REMP TRACKICG SYSTEM CAMMA SPEC 1lt0POOT CF WTCS SAMPLE FREQUENCT IS: MONTMLT RESULTS IN PCI/L +/- 2 SIGMA MATFR STATION SAMPLE COLLECTION OA-140 Co-58 CO-60 Cs-134 CS-131 L8 CATION TYPE DATE FE-59 LA-140 MN-54 NB-95 15-65 3R-95 36 WATER 940630/940728 LT 24.20 LT 4.40 LT 3.40 LT 3.80 LT 2.20 LT 2.10 LT 6.40 LT 4.00 LT 2.10 LT 5.30 LT 4.20 36 WATER 94072ff940825 LT 34.60 LT 4.80 LT 1.90 LT 2.80 LT 4.00 LT 9.10 LT 3.40 LT 4.90 LT 6.00 LT 8.40 LT 7.90 36 WATER 940825/940929 LT 15.60 LT 3.40 LT 3.60 LT'2.00 LT 4.50 LT 7.50 LT 3.60 LT 2.80 LT 5.60 LT 7.50 LT 4.20 36 WATER 940929/941027 LT 23.90 LT 6.30 LT 2.50 LT 4.70 LT 4.80 LT 3.10 LT 5.30 LT 2.70 LT 1.90 LT 8.40 LT 3.10 36 WATER 941027/941128 LT 7.70 LT 1.80 LT'3.40 LT 2.60 LT 2.20 LT 6.10 LT 2.50 LT 2.30 LT 3.90 LT 1.70 LT 6.50 36 WATER 941128/941229 LT 7.80 LT 3.40 LT 5.10 LT 2.10 LT 2.90 LT 7.00 LT 2.70 LT 4.70 LT 5.50 LT 5.80 LT 6.20 59 WATER 940421/940428 LT 25.70 . LT 6.40 LT 3.90 LT 7.60 LT 3.90 LT 13.30 LT 4.60 LT 7.10 LT 4.90 LT 7.30 LT 10.00 59 WATER 940428/940526 LT 9.80 LT 2.10 LT 3.00 LT 2.40 LT 3.60
.LT 4.00 LT 1.60 LT 2.00 LT 3.10 LT 4.60 LT 2.70 59 WATER 940526/940630 LT 17.20 LT 2.90 LT 4.70 LT 5.10 LT 2.50 LT 7.00 LT 3.20 LT 3.60 LT 5.40 LT 5.60 LT 4.90 59 WATER 940630/940728 LT 40.50 LT 3.50 LT 2.00 LT 5.00 LT 2.80 LT 8.00 LT 4.90 LT 4.70 LT 6.10 LT 5.70 LT 4.40 59 WATER 940728/940825 LT 16.60 LT 2.90 LT 3.50 LT 2.00 LT 3.80 LT 5.70 LT 2.10 LT 3.20 LT 4.20 LT 6.40 LT 5.90 59 WATER 940825/940929 LT 34.30 LT 5.10 LT 3.30 LT 4.40 LT 4.00 LT 4.30 LT 3.30 LT 3.30 LT 2.60 LT 3.50 LT 10.40 59 WATER 940929/941027 LT 25.20 LT 4.10 LT 3.40 LT 4.80 LT 3.20 LT 7.20 LT 2.60 LT 3.10 LT 2.40 LT 6.70 LT 11.90 59 WATER 941027/941128 LT 10.30. LT 3.30 LT 3.20 LT 2.90 . LT 3.90 LT 4.70 LT 2.60 LT 3.70 LT 2.60 LT 5.80 LT 9.80 59 WATER 941128/941229 LT 23.50 LT 2.10 LT 2.60 LT 3.00 . LT 2.80 LT 5.10 LT 3.80 LT 1.40 LT 1.60 LT 5.20 LT 5.90
_ _ -.._m-m.._m. __.c . -,-.w. , , , . , , , , , _ _ . . . . . ,-e, , . - . , . ,m,e. , , ,c._.,,.,, , , , ,, .. _ , _ , , , ,, ,
._- ~ . . -. . . .
* * 'LEMP TEACKI%G SYSTEM '.- -_g SAMMA SPEC E2PTCT GF WT32 SAMPLE FO3*aUE2CY ISt MOOTHLY RESULT 5 ID PCs/L +/- 2 SICMA UtfFD STATION SAMPLE COLLECTION BA-140 co-58 co-60 cs-134 cs-137 LOCATION TYPE DATE FE-59 LA-140 MN-54 N8-95 EN-65 ER-95 60 WATER 940421/940428 LT 23.00 LT 1.80 LT 1.30 LT 3.50 LT 4.10 LT 6.30 LT 4.10 LT 2.70 LT 3.80 LT 4.20 LT 7.00 60 WATER 940428/940526 LT 31.40 LT 4.10 LT 2.70 LT 3.40 LT 4.00 LT 3.70 LT 4.10 LT 1.90 LT.4.10 LT 4.40 '
LT 4.60 60 WATER 946526/940630 LT 17.90 LT 3.00 LT 4.10 LT 4.30 LT 4.10 LT 6.70 LT 2.80 LT 3.20 LT 3.20 LT 6.90 LT 5.20 60 WATER 940630/940728 LT 15.90 LT 3.30 LT 4.10 LT 3.80 LT 4.90 LT 4.10 LT 2.40 LT 3.30 LT 4.10 LT 4.40 LT 4.20 60 WATER 940728/940825 LT 9.70 LT 1.50 LT 4.00 LT 3.90 LT 4.20 LT 4.80 LT 2.50 LT 2.50 LT 2.10 LT 4.90 LT 6.00 60 WATER 940825/940929 LT 21.30 LT 2.60 LT 1.70 LT 3.80 LT 1.90 LT 6.70 LT 2.30 LT 1.20 LT 3.20 LT 7.00 LT 4.90 60 WATER 940929/941027 LT 16.10 LT 1.90 LT 3.50 LT 1.80 LT 4.90 LT 6.40 LT 2450 LT 3.70 LT 1.80 LT 2.40 LT 4.30 60 WATER 941027/941128 LT 12.10 LT 3.40 LT 2.90 LT 3.60 LT 2.10 LT 5.50 LT 2.80 LT 3.90 LT 4.30 LT 6.80 LT 4.60 60 WATER 941128/941229 LT 22.10 LT 2.60 LT 2.40 LT.1.70 LT 3.70
- LT 4.30 LT 2.90 LT 2.10 LT 4.30 LT 4.30 LT 4.80
_ _ _ _ _ . _ _ _ _ _ _ . _ _ _ _ _ _ _ _ _ _ _ _ _ _.__..__.._._____.________.________m ._.m_ _ _ , _ . . - -. . _ . . . _ ._ . , _-
l ; ili 7 , s P P N F O C G C I T T A LA g - RM I, MEG M TTI C TRS L A L FU2 I OQ C T:/ 0 0 00 000 000 I 25+ M 0 0 00 000 000 D O1 U 743 T P L I 2 8 93 928 C ET/ T 9 8 88 088 8s9 E RCI I 000 - 0 00 0 - - 0 - - - - - -
- L E NC R CEP T
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++ + + ++
EU 2690 2096 2009 000 000 D PQN 9540 46 5 000 000 N CEI R 111 9 0.1 1 1 9 0 0.1 1 A R E 3 3 29 124 637 / L AFS T 3 TTT7 T 5 T T' T82T 810 140 E M T A N LLL1 L2LL L22L 222 222 V E MEL W ALU 1099 1099 1099 099 099 L 4PS 3322 3322 3322 322 322 C ME 3692 3692 3692 692 692 AR N 0001 0001 0001 001 001 444 S O 4444 4444 4444 444 I 9999 9999 9999 999 999 T //// //// //// /// /// CE 7107 0109 7109 109 109 ET 2332 3332 2332 232 232 LA 1360 2369 1369 469 469 LD 0001 1000 0000 000 000 O 4444 3444 4444 444 444 C 9999 9999 9999 999 999 m E LE PP - MY AT RRRR RRRR RRRR RRR RRR S EEEE EEEE EEEE EEE EEE TTTT TTTT TTTT TTT TTT N AAAA AAAA AAAA AAA AAA NO WWWW WWWW WWWW WWW WWW OI IT TA AC 8888 4444 6666 999 000 TO 2222 3333 3333 555 666 SL
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REMP TRACKING SYSTEM * *
~-- 7' GAMMA SPEC REPORT OF SED SAMPLE FREQUENCY IS: SEM-ANNUAL RESULTS IN PCI/KG(DRY) +/- 2 SIGMA REDTMFMT STATION SAMPLE COLLECTION Co-58 Co-60 CS-134 CS-137 E-40 LOCATION TYPE DATE 25 SEDIMENT 940523/940523 LT 22.1 LT 12.9 LT 45.3 43.7+/-17.9 18206.0+/-502.0 25 SEDIMENT 941006/941006 LT 25.9 LT 20.5 LT 26.4 98'.7+/-19.5 14087.0+/-510.0 26 SEDIMENT 940523/940523 LT 17.3 LT 22.7 LT 41.6 261.1+/-29.7 18396.0+/-550.0 26 SEDIMENT 941006/941006 LT 19.0 LT 31.1 LT 31.6 478.0+/-45.0 22335.0+/-977.0 27 SEDIMENT 940523/940523 LT 9.3 LT 17.0 LT 45.9 370.0+/-27.0 18293.0+/-506.0 27 SEDIMENT 941006/941006 LT 20.5 LT 25.9 LT 20.5 209.0+/-25.0 16822.0+/~614.6 32 SEDIMENT 940523/940523 LT 25.6 LT 21.3 LT 45.7 324.0+/-29.0 17234.0+/-523.0 32 SEDIMENT 941006/941006 LT 39.7 LT 25.3 LT 30.5 223.0+/~32.0 12865.0+/-601.0 63 SEDIMENT 940527/940527 LT 8.0 LT 16.7 LT 32.2 LT 23.7 11972.0+/-529.0 63 SEDIMENT 941010/941010 LT 44.1 LT 14.6 LT 48.7 LT 18.9 9524.0+/-590.0 64 SEDIMENT 940527/940527 LT 18.2 LT 18.7 LT 35.0 LT 17.0 7590.0+/-395.0 64 SEDIMENT 941010/941010 LT 30.4 LT 34.5 LT 29.0 LT 18.5 9647.0+/-670.0 65 SEDIMENT 940527/940527 LT 24.9 LT 20.4 LT 44.5 LT 25.4 11015.0+/-616.0 65 SEDIMENT 941010/941010 LT 37.7 LT 18.3 LT 33.0 LT 29.3 12529.0+/-692.0 i
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CLEVELAND ELECTRIC'ILLUMINATIEG CO . - ~ ~ PNPP. , s. REMP TRACKING SYSTEM GAMMA SPEC REPO%T OF FSS SAMPLE FREQUENCT'IS: SEM-ANNUAL RESULTS IN FCI/KG(WET) +/- 2 SIGMA FTRH STATION SAMPLE COLLECTION CO-58 CO-60 CS-134 CS-137 FE-59 , LOCATION TYPE DATE K-40 MN-54 EN-65 i 25 DRUM 940523/940524 LT 20.6 LT 18.7 LT 15.6 LT 26.1 LT 13.2 3 1692.0+/-367.0 LT 11.1 LT 31.1 25 WNITE SUCRER 940523/940524 LT 19.5 LT 24.9 LT 7.4 LT 19.6 LT 55.4 j 4 2228.0+/-460.0 LT 16.2 LT-27.9 ' 25 WWITE PERCH 940523/940524 LT 14.5 LT 14.3 LT 22.3 LT 26.8 LT 15.8 2792.0+/-646.0 LT 8.8 LT 41.9 25 WALLEYE 940523/940524 LT 21.7 LT 13.8' LT 17.9 LT 29.6 LT 46.7 3017.0+/-483.0 LT 12.3 LT 42.7 25 SMALL MOUTN BASS 940523/940524 LT 16.6 LT 23.2 LT 15.2 LT 18.1 LT 12.8 2606.0+/-383.0 LT 15.2 LT 30.5 25 YELLOW FERCN 940523/940524 LT 18.8 LT 26.2 LT 31.8 LT 21.8 LT 32.9 1973.0+/-446.0 -LT 16.6 LT 48.7 25 REDNORSE SUCKER 940523/940524 LT 17.5 LT 25.4 LT 28.1 LT 26.2 LT 49.7 1853.0+/-454.0 LT 11.2 'LT 44.3 25 SMALL MOUTM BASS 941006/941007 LT 14.9 LT 20.7 LT 9.7 LT 15.0 LT 51.6 2426.0+/-434.0 LT 14.9 'LT 19.6 25 DRUM 941006/941007 LT 14.0 LT 8.9 LT 28.4 LT 26.3 LT 23.0 1426.0+/-406.0 LT 17.7 LT 35.6. 25 REDMORSE SUCKER 941006/941007 LT 28.8 . LT 18.6 LT 20.1 LT 16.6 LT 24.5 2506.0+/-465.0 LT 11.7 LT 39.3 25 WWITE SUCRER 941006/941007 LT 19.4 . LT 11.4 LT 14.1 LT 14.7 LT 26.8 2318.0+/-344.0 LT 12.2 LT 19.6 25 ROCK BASS 941006/941007 LT 34.5 LT 30.2 LT 30.9 LT 32.4 LT 71.1 1582.0+/-473.0 LT 17.8 LT 46.7 25 WALLEYE 941006/941007.LT 23.5 LT.7.9 LT 16.6 LT 23.8 LT 22.1 2369.0+/-384.0 LT 13.7 LT 30.2 32 WWITE PERCN 940523/940524 LT 7.7 LT 9.3 LT 11.0 LT 13.2 LT 12.9 2490.0*/-369.0 LT 9 . 5 - LT 16.7 32 WNITE SUCRER 940523/940524 LT.11.2 LT 10.6 LT 26.4 LT 20.7 LT 32.4 2525.0+/-202.0 .LT 16.4 LT 40.6 + 32 DRUM 940523/940524 LT 12.0 LT 20.0 LT 1.4 LT 18.9 LT 21.7-2200.0+/-369.0- LT 17.1 LT 36.5 32 WALLEYE 940523/940524 LT 14.0 .LT 23.3 LT 22.7 LT 32.3 LT 39.9 2355.0+/-648.0 LT 13.9 LT 15.5
- 32 YELLOW FERCN 940523/940524 LT 16.8 LT 13.3 LT 11.7 LT 15.0 LT 31.0 2448.0+/-363.0 LT 8.4 LT 29.4 32 ROCK BASS 940523/940524 LT 4.0 LT'5.6 LT 11.8 LT 16.1 LT 9.8 1328.0+/-240.0 LT 7.7' LT 9.8 i 32 CARP 941006/941007 LT 8.1 LT 9.4 LT 17.0 LT 14.0 LT 16.2 1681.0+/-268.0 LT 5.6 LT 10.2
! 32 WNITE SUCKER 941006/941007 LT 5.8 LT 18.2 LT 10.0 LT 17.0 LT 23.2 2384.0+/-380.0 LT 10.7 LT 24.3 32 SMALL MOUTH DASS 941006/941007 LT 24.7 - LT 12.7 LT 20.5 LT 17.9 LT 27.5
- 1722.0+/-421.0 LT 23.1 LT 42.7 32 WALLEYE 941006/941007 LT 4.0 . -LT 16.4- LT 21.4 LT 23.5 LT 49.7-3370.0+/-444.0 -LT 23.7 -LT 36.8 a;.-, . --- -~,.-.-..e-,v ., -,.,-.n-,z ~ < ~ , . - .w e ,n ae ,,n- e n <. - r~ --
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~* . *
'R3MF TRACK!OS-SYST3M
~
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SAMMA 5FSC Y.EFMT CF.FS3
. SAMPLE FRS$33ECY IS SEM-ATUAL -
'EESULTS ED ' FC1/K3 tL*ET ) +/- 2 SitMA ' <~ -
'FTRH ...y ;.
' STATION SAMPLE COLLECTION Co 1 Co-60 CS-134 CS-137 FE-59: ..
LOCATION- TYPE DATE K-40 MN-54 EN-65. 32 YELLOW FERCN 941006/941007 LT 30.6 LT 30.2 LT 46.4 .LT 43.1 LT 38.9 ~ 2360.0+/-642.0 LT 38.5 'LT 76.6 32 REDNORSE SUCKER 941006/941007 LT 22.0 LT 8.7 LT 20.9 LT 21.2 LT 60.6 2056.0+/-406.0 LT.13.4 LT 22.4 1 i 4 s__ ____._ _ . _ _ _ _ _ _ _ _ _ _ _ . . . . . ~ . .,,s._,.. , , , , .ml._.m.s.. . , _ _ , ,y ,
,v CLEVELA%8 ELECT 2IC ILLUMICATICG CO. - P2PP. t .
REMP TCACKIDS SYSTEM G AM."A SPEC-REP 3"JT GF TL3 SAM 7LE F12QU20CT IST Q! ALT 3CLT RESULTS IN 91 DAYS +/- 2 SIGMA
'fT D STATION SAMPLE COLLECTION DIRECT LOCATION TYPE DATE 01 TLD 940106/940401 9.50+/ .10 01 TLD 940401/940707 14.10+/ .20 01 TLD 940707/941004 10.90+/ .50 01 TLD 941004/950106 11.90+/ .20 02 TLD 940106/940401 0.70+/ .10 62 TLD 940401/940707 14.00+/ .30 ,
02 TLD 940707/941004 10.60+/ .10 02 TLD 941004/950106 11.50+/ .20 03 TLD 940106/940401 11.00+/ .10 03 TLD 940401/940707 16.60+/ .50 03 TLD 940707/941004 12.90+/ .20 03 TLD 941004/950106 14.40+/ .20 04 TLD 940106/940401 10.90+/ .10 04 TLD 940401/940707 16.10+/ .20 04 TLD 940707/941004 12.00+/ .10 04 TLD 941004/950106 14.50+/ .20 05 TLD 940106/940401 10.60+/ .20 05 TLD 940401/940707 13.50+/ .30 05 TLD 940707/941004 13.40+/ .10 05 TLD S41004/950106 12.20+/ .10 06 TLD 940106/940401 11.70+/ .30 06 TLD . 940401/940701 15.00+/~.30 06 TLD 940707/941004 14.10+/ .20 06 TLD 941004/950106 13.60+/ .10 07 TLD 940106/940401 11.30+/ .30 07 TLD 940401/940707 17.60+/ .20 07 TLD 940707/941004 13.50+/ .10 07 TLD 941004/950106 14.90+/ .30 00 TLD 940106/940401 9.20+/ .10 00 TLD 940401/940707 13.40+/ .40 00 TLD 940707/941004 11.40+/ .20 00 TLD 941004/950106 11.20+/ .20 09 TLD 940106/940401 9.00+/ .10 Of TLD 940401/940707 13.40+/ .10 09 TLD 940707/941004 11.10+/ .20 09 TLD 941004/950106 11.20+/ .20 10 TLD - 940106/940401 9.40+/ .10 w, ,- r -- , e-- , - - , , . - . - y vs,-.- -+ --, ,,,- -- ,-, v.,,-.- n%v-- - . r.,, , . m.m,, .,
7- .v .m. _ ,- ,-. . - - . - u..
- 2* ~ BEMF TRACKICC SYST3M _ . ~ .*?
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'4AMMA SP2C EEPDCT'6F TLD s
~
SAMPLE FSEEU3ECT IS: CTART38LT , G35ULTS 12 91 CAYS.+/- 2 SICMA TLD STATION SAMPLE COLLECTION DIRECT L CATION TYPE DATE 10 TLD 940401/940707 17.70+/~.20 10 TLD 940707/941004 12.20+/ .10 le TLD 941004/950106 15.70+/ .40 11 TLD 940106/940401 11.70+/ .30 11 TLD 940401/940707 14.40+/ .10 11 TLD 940707/941004 13.40+/ .20 11 TLD 941004/950106 11.60+/ .20 12 TLD 940106/940401 10.90+/ .30 12 TLD 940401/940707 15.50+/ .20 12 TLD 940707/941004 12.70+/ .10 12 TLD 941004/950106 13.60+/ .20 13 TLD 940106/940401 9.00+/ .20 13 TLD 940401/940707 14.20+/ .30 13 TLD 940707/941004 10.10+/ .20 13 TLD 241004/950106 11.70+/ .30 14 TLD 940106/940401 0.00+/ .10-14 TLD 940401/940707 14.90+/ .10 14 TLD 940707/941004 10.10+/ .10 14 TLD 941004/950106 11.00+/ .50 15 TLD 940106/940401 9.00+/ .10 15 TLD 940401/940707 14.60+/ .10 15 TLD 940707/941004 11.10+/ .20 15 TLD 941004/950106 11.20+/ .30 16 TLD 940106/940401.11.90+/ .20 16 TLD 940401/940707 19.50+/ .20 16 TLD 940707/941004 14.40+/ .10 16 TLD 941004/950106 15.00+/ .40 17 TLD 940106/940401 11.70+/ .20 17 TLD 940401/940707 20.00+/ .20 17 TLD 940707/941004 14.50+/ .20 17 TLD 941004/950106 17.60+/ .10 10 TLD 940106/940401 10.10+/ .10 10 TLD 940401/940707 24.20+/ .20 le TLD 940707/941004 20.00+/ .10 10 TLD 941004/950106 22.20+/ .30 19 TLD 940106/940401 10.90+/ .10 19 TLD 940401/940707 10.20+/ .30 _ ~ . - . , - - _ . - . , - . _ . - . . - . .. - - .~. . . . , . . . . , .
~- ,, . -- .
CLEV E LADD ELECT 2IC ILLUMICATIEG C0& - FCFF. 7(:; REMF'T2ACRIEC SYSTEM 6AMMA SP3C C2FECT EF TL3 ' S AMPLE FREQUEBCT IS2 99ARTERLY _ RESULTS IN 91 DAYS +/- 2 SIGRA TT f1 ' ' STATION SAMPLE COLLECTION ' DIRECT i LCCATION TYPE DATE i 19 TLD' 940707/941004 13.69+/ .29 19 TLD 941604/950196 15.88+/ .30 20 TLD 940186/940401 11.70+/ .40 29 TLD 940481/940787 18.10+/ .20 28 TLD 940797/941004 13.89+/ .20 20 TLD 941094/950106 15.80+/ .30 21 TLD 940186/940481 13.50+/ .10 21 TLD 940491/940707 20.30+/ .20 21 TLD 940797/941094 15.70+/ .25 21 TLD 941004/950106 15.80+/ .28 22 TLD 940106/940481 12.20+/ .30
'22 TLD 940787/941004 14.00+/ .18 22 TLD 941094/950186 12.30+/ .10 23 TLD 940196/940401 13.60+/ .10 23 TLD 940491/940797 16.78+/ .30 23 TLD 940797/941094 15.60+/ .30 23 TLD 941004/950186 13.40+/ .20 24 TLD 940106/940401 11.88&/ .40 24 TLD 948481/940707 17.78+/ .29 24 TLD 940707/941st4 14.19+/ .20 24 TLD 941884/950196 14.5S+/ .25 29 TLD 940196/940401 12.20+/ .10 29 TLD 940481/948787 19.10+/ .10 29 TLD 949787/941084 14.80+/ .48 29 TLD 941994/958106 15.68+/ .30 30 TLD 948196/940481 9.78+/ .28 .
38 TLD 940481/948707 15.10+/ .10 30 TLD 940797/941004 11.60+/ .19 30 TLD 941004/950106 12.10+/ .18 31 TLD 940186/940491 11.80+/ .29 31 TLD 940401/940707 17.79+/ .20 31 TLD 940707/941984 14.10+/ .20 31 TLD 941004/950186 14.30+/ .28 33 TLD 940196/940481 13.3s+/ .10 33: TLD 940401/940707 18.20+/ .20 33 TLD 940707/941094 14.19+/ .20 33- TLD 941004/950106 15.20+/ .38
, CLEVELAND ELECTDIC~ ILLUMICATILG'CO.'- ' PsPP.
~ ~ ' - ~
REMP T2ACK!CS SYST3M GAMMA SPEC CEP@;T CF TL3 p.} SAMPLE FCE&T33CY IS: (T ACTEZLY RESYLTS IQ 91 EAYS +/- 2 SICMA TID STATION 5 AMPLE COLLECTION DIRECT LCCAT10N TYPE DATE 35 TLD 940106/940401 9.50+/ .10 35 TLD 940401/940707 15.20+/ .10-35 TLD 940707/941004 11.10+/ .20 35 TLD 941004/950106 12.00+/ .10
'36 TLD 940106/940401 13.20+/ .10 36 TLD 940401/940107 19.10+/ .10 36 TLD 940707/941004 14.90+/ .20 36 TLD 941004/950106 17.10+/ .20 41 TLD 940106/940401 9.20+/ .10 41 TLD 940401/940707 16.00+/ .30 41 TLD 940707/941004 13.20+/ .10 41 TLD 941004/950106 14.50+/ .20 42 TLD 940106/940401 11.00+/ .20 42 TLD 940401/940707 15.60+/ .20 42 TLD 940024/941004 14.70+/ .20 42 TLD 941004/950106 12.30+/ .10 43 TLD 940106/940401 10.10+/ .10 43 TLD 940401/940707 16.30+/ .10 43 TLD 940707/941004 11.10+/ .10 43 TLD 941004/950106 12.90+/ .20 45 TLD 940106/940401 9.60+/ .10 45 TLD 940401/940707 15.90+/ .20 45 TLD 940707/941004 10.60+/ .10 45 TLD 941004/950106 13.30+/ .30 53 TLD - 940106/940401 10.10+/ .20 53 TLD 940401/944707 15.40+/ .10 53 TLD 940707/941004 11.40+/ .10 'i 53 TLD 941004/950106 12.90+/ .10 54 TLD 940106/940401 9.70+/ .20 54 TLD 940401/940707 16.20+/ .20 54 TLD 940707/941004 10.50+/ .20 54 TLD 941004/950106 13.20+/ .10 SS TLD 940106/940401 9.50+/ .20 55 TLD 940401/940707'16.40+/ .20 55 TLD 940707/941004 10.90+/ .20 55 TLD 941004/950106 13.50+/ .20 56 TLD 940106/940401 10.40+/ .20 d .__ ._.. ._.__._____m__ ._._______m _.______w. , ,
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_ F' F _ E P O C G E _ I A T' YR A" LG CM CI IE S2S - MT - LT - US T;2 LY k LS FT-I 4C/ G + CC Tt II CSS RK SIY TC P A 009 0988 CA CYS 321 1221 ER CC LT 1 - - - - - - - - E C29 - /// //// P ET T +++ + + ++ DM PCR C O08 O988 NE SSI E 312 3553 AR R R L AFS I 218 1512 E M T D 111 1111 V- MEL E ALU 746 1746 L '- GPS 990 0880 - C ME 791 4701 - AR N 010 8018 S~ O 445 4445 . I 999 9999 T /// //// CE 174 6174 ET 089 0850 LA 470 1478 - LD 591 0091 . O 444 4444 C 999 9999 E D LE T PF T MT AT S' DDD DDDD N LLL LLLL NO TTT TTTT OI IT TA AC 666 8088 TO 555 5555 SL
" * * . n' '
REMP.TRACKILG SYST3M (- 4 g g. , CAMMA SPEC CEFSOT CF'TLD'
.5 AMPLE FQ20T33CY.15: QOACTCSLY2 GESELT5 ID M2/91 EAYS +/- 2 51EMA
' TID STATIOS SAMPLE- COLLECTIOJ DIRECT LSCATIOS TYPE DATE 01 TLS 940106/940401 9.90+/ .20 01 TLs 940401/940707 13.00+/ .10 01 TLs 940707/941004 13.00+/ .30 i 61 TLs 941004/950106 11.00+/ .10 02 TLs 940106/940401 10.40+/ .20 02 TLE 940401/940707 13.60+/ .20 02 TLS 940707/941004 12.00+/ .30 02 TLs 941004/950106 11.40+/ .30 93 TLB 940106/940401 12.20+/ .40, 03 TLs 940401/940707 16.00+/ .20 03 TLs 940707/941004 14.60+/ .10
.03 TLs 941004/950106 14.20+/ .20 04 TLB 940106/940401 11.00+/~.20 64 TLs 940401/940707 16.00+/ .10 04 TLs 940707/941004 14.70+/ .10 04 TLs 941004/950106.14.20+/ .20 05 TLs 940106/940401 12.20+/ .20 05 TLs 949401/940707 13.20+/ .30 05 TLs 940707/941004 14.20+/ .10
- 05 TLB 941004/950106 12.00+/ .10' 06 TLs 940106/940401 12.60+/ .20 06 TLB 940401/940707 15.60+/ .30 06 TLB 940701/941004 15.00+/ .20:
06 TLB 941004/950106 13.90+/ .20 07 TLs 940106/940401 12.30+/ .30 07 TLs 940401/940707 16.40+/ .20 07 TLB 940707/941004 15.30+/ .10 07 TLs 941004/950106 13.90+/ .20 00 TLs 940106/940401 9.00+/ .20' , 80 TLs 940401/940707 12.90+/ .50 00 TLs 940707/941004 12.40+/ .10 00 TLB 941004/950106 11.20+/ .30 09 TLs 940106/940401 9.00+/ .20 09 TLs 940401/940707 13.20+/~.30 09 TLs 940707/941004 12.60+/ .20 09 TLs 941004/950106 11.10+/ .30 10 TLS 940106/940401 12.50+/ .20-
._ _ _ . . . . . ~ . . . - - . . . . - . . , . . , . . . _ _ . ., .- -- _- -. _ . . . . _ _ . _ . - _ - _ . _ _ - .. . . _ - - _ . _ - _ . _ . _ _ _ _ . - - . _ _ ..- - _ - - _ . .
- p CLEVELAND ELECT 21C ILLUMICATICG C@. - 'PEPP.
-REMP T2ACEICS SYST3M
~
SAMMA SP3C CSPTOT CF TL3 SAMPLE FaEOCEOCT'152 QYART3 GLY 2
'RESULTS IN MR/91 DAYS +/- 2 SIGMA iTI)
STATION SAMPLE COLLECTION DIRECT LOCATION TYPE DATE 10 TLS 940401/940707 17.10+/ .30 10 TLB 940707/941004 16.60+/ .10 10 TLB 941004/950106 16.40+/ 10 11 TLB 940106/940401 12.60+/ .20 11 TLB 940401/940707 13.70+/ .30 11 TLB 940707/941004 16.00+/ .20 11 TLB 941004/950106 12.40+/ .10 12 TLs 940106/940401 12.20+/ .30 12 TLB 940401/940707 15.10+/ .30 12 TLs 940707/941004 15.30+/ .20 12 TLB 941004/950106 13.70+/ .30 13 TLB 940106/940401 12.50+/ .20 13 TL8 940401/940707 13.70+/ .40 13 TLB 940701/941004 15.30+/ .20 13 TLB 941004/950106 11.30+/ .40 14 TLB 940106/940401 12.40+/ .20 14 TLB 940401/940707 14.50+/~.10 14 TLB 940707/941004 14.90+/ .20 14 TLs -941004/950106 11.60+/ .50 15 TLB 940106/940401 11.60+/ .20 15 TLB 940401/940707 13.00+/ .40 15 TLa 940707/941004 13.10+/ .30 15 TLB 941004/950106 11.10+/ .40 16 TLB 940106/940401 15.70+/ .20 16 TLB 940401/940707 19.00+/ .10 16 TLB 940707/941004 19.2S+/ .10 16 TLB 941004/950106 15.00+/ .20 17 TLB 940106/940401 14.70+/ .20 17 TLB 940401/940707 17.60+/ .30 17 TLB 940707/941004 10.20+/ .10 17 TLs 941004/950106 17.60+/ .20 la TLa 940106/940401 19.50+/ .20 13 TLB 940401/940707 23.70+/ .20 10 TLB 940707/941034 22.50+/ .10 10 TLs 941004/950106 22.20+/ .40 19 TLB 940106/940401 11.70+/ .20 19 TLB 940401/940707 17.70+/ .20
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.SAMMA SPEC CEFEGT GF TL3 SAMPLE FRSCTE"CY.IS: CTALTJCLT2 23SELTS 13 M2/91 CAYS +/- 2 SIEMA TLD STATION SAMPLE COLLECTION DIRECT L@ CATION TYPE DATE 19 TLB 940707/941004 15.10+/ .20 19 TLB 941004/9501d6 15.70+/ .30 20 TLB 940106/940401 12.40+/ .20 20 TLa 940401/940707 17.50+/ .30 20 TL5 940707/941004 15.00+/ .20 20 TLS 941004/950106 15.50+/ .30 21 TLB 940106/940401 14.20+/ .20 21 TLs 940401/940707 17.50+/ .30 21 TLB 940707/941004 16.60+/ .10 21 TLB 941004/950106 15.00+/ .10 22 TL5 940106/940401 13.00+/ .20 22 TLs 940707/941004 15.20+/ .20 22 TLS 941004/950106 12.50+/ .10 23 TLa 940106/940401 14.60+/ .20 23 TLS 940401/940707 16.30+/ .20 23 TLs 940707/941004 17.3O+/ .40 23 TLs 941004/950106 15.40+/ .40 24 TLB 940106/940401 12.50+/ .20 24 TLB 940401/940707 17.00+/ .20 24 TLB 940707/941004 15.10+/ .20 24 TLB 941004/950106 15.60+/ .40 29 TLB 940106/940401 14.10+/ .20'-
29 TLs 940401/940707 13.20+/ .30 29 TLB 940707/941004 17.40+/ .40 29 TLB 941004/950106 16.60+/ .10 30 TLB 940106/940401 10.30+/ .20 30 TLs 940401/940707 17.50+/ .10 30 TL5 940707/941004 14.10+/ .10 30 TLs 941004/950106 12.70+/ .10 31 TL5 940106/940401 12.60+/ .30 31 .T Ls 940401/940707 14.00+/ .50 31 TLS 940707/941004 15.40+/ .30 31 TLs 941004/950106 14.30+/ .30 33 TLs 940106/940401 14.10+/ .20 33 TLB 940401/940707 17.50+/ .40 33 TLs 940707/941004'15.90+/ .20 33 TLS 941004/950106 15.80+/ .20
. . . . - . , , - . -. . . , - . . . - ~ . . . .,
CLEVELAND ELECTRIC ILLUMINATIEQ CU. - FSFP. REMP TRAC 3XC4 SYSTEM-CAMMA SPEC R3POCT SF TLS , SAMPL3 FCEOO3"CY IC: CCASTOGLY2 RESULTS IN MR/91 DAYS +/- 2 SIGRA TID STATION SAMPLE CO LLE CTION DIRECT L& CATION TYPE DATE 35 TL5 940106/940401 10.70+/ .20 35 TLs 946401/940707 13.20+/ .20 35 TLs 940707/941004 13.20+/ .20 35 TLs 941004/950106 11.60+/ .20 36 TLs 940106/940401 14.00+/ .20 36 TLs 940401/940107 19.50+/ .10 36 TLE 940707/941004 17.90+/ .40 36 TLs 941004/950106 17.99+/ .10 41 TLE 940106/940401 11.30+/ .20 41 TLs 940401/940707 15.60+/ .20 41 TLs 940707/941004 14.00+/ .20 42 TLs 940106/940401 12.20+/ .20 42 TLB 940401/940707 13.70+/ .10 42 TLE 940024/941004 13.30+/ .20 42 TLs 941004/950106 12.20+/ .10 43 TLs 940106/940401 12.00+/ .20 43 TLs 940401/940707 13.00+/ .30 . 43 TLE 940107/941004 14.40+/ .10 43 TLs 943004/950106 12.60+/ .10~ 45 TLs 940106/940401 11.40+/ .20 45 TLs $40401/940707 15.40+/ .20 45 TLs 940107/941004 14.10+/ .10 45 TLs 941094/950106'12.50+/ .10 53 TLs 940106/940401 11.40+/ .20 53 TLs 940401/940707 15.00+/ .10 53 TLB 940707/941084 14.00+/ .10 53 TLs 941004/950106 14.00+/ .20 54 TLB 940106/940401 9.60+/ .20 54 TLs 940401/940707 15.20+/ .30 54 TLs 940707/941004 12.30+/ .10 54 TLs 941004/950106 13.20+/ .10 55- TLs 940106/940401 12.10+/ .40 55 - TLs 940401/940707 17.20+/ .40 55 TLs 940707/941004 15.20+/ .20 55 TLB 941004/950106 14.90+/ .70 56 TLB 940106/940401 10.70+/ .30
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GAMMA SPCC Q2FT/CT nF TL2 - ' SAMPLS F33COCCCT IS COAIT3ELY2.' ~ 2250LTS 20 M3/91 RAYS +/- 2 St(MA .. _ iTD STATION SAMPLE COLLECTION DIRECT LiCATION TYPE DATE . 56 TLB 940401/940707 13.00+/ .10 56 TLB 940707/941004 13.10+/ .20 56 TLB 941004/950106 10.90+/ .10 l-
.50 TLs 940106/940401 12.00+/ .20 50 TLS 940401/940707 13.00+/ .10 50 TLB 940107/941004 13.00*/ .20 50 TLB 941004/950106 12.20+/ .10-h 4
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'SAMPL2 FCE@%EICT IS AOOTAL RESULTS IN MR/365 DAYS +/- 2 SIGMA TTD ~~
~
STATION SAMPLE COLLECTION DIRECT + LCCATION TYPE DATE
.61 TLA 940106/950106 53.10+/ .40 02- TLA 940106/950106 45.00+/ .70 93 TLA 940106/950106 49.50+/ .40 04 T LA 940106/950106 49.50+/ .00 05 T LA 940106/950106 39.00+/-2.00 86 TLA 940106/950106 52.30+/-1.60 07 TLA 940106/950106 35.90+/-1.00 Se TLA 940106/950106 43.40+/ .30 09 TLA 940106/950106 43.90+/ .90 10 TLA 940106/950106 62.90+/ .00 11 TLA 940106/950106 46.70+/ .30 12 TLA 940106/950106 52.30+/ .30 13 TLA 940106/950106 49.20+/ .60 14 TLA 940106/950106 47.60+/-1.10 15 T LA 940106/950106 45.10+/ .60 16 TLA 940106/950106 6 2. 6 0 +/-4' . 0 0 17 TLA 940106/950106 57.70+/ .30 10- TLA 940106/950106-79.10+/ .60 19 TLA 940106/950106 54.40+/ .70 20 TLA 940106/950106 40.40+/ .50 21 TLA 940106/950106 57.30+/ .70 22 TLA 940712/950106 23.40+/ .60 23 TLA 940106/950106,52.70+/ .30 24 TLA 940106/950106 49.40+/-1.00 .++ ,m- , - - , , m - ,
- s se . CLEVELA33 ELECT 2IC ILLUM152CC9CB-d59. - CCCC. -"
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STATION SAMPLE COLLECTION DIRECT LOCATION TYPE DATE 29 TLA 94a106/950106 64.20+/-1.30 I 30 'TLA 940106/950106 47.60+/ .30 31 TLA ' 940106/950106 57.40+/ .30 33 TLA 910106/950106 62.30+/ .80 35 TLA 940106/950106 45.20+/ 40 36 TLA 940106/950106 64.90+/ .90 41 TLA 940106/950106 50.00+/ .30 42 TLA 940106/950106 54.90+/ .30 43 TLA 940106/950106 49.30+/ .50 45 TLA 940106/950106 48.70+/ .60 53 TLA 940106/950106 52.50+/ .40-54 TLA 940106/950106 45.00+/ .70 940106/950106 56.40+/ .40 55 TLA 56 TLA 940106/950106 44.70+/ .30 58 TLA 940106/950106 44.50+/ .60 i
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