ML021200067
| ML021200067 | |
| Person / Time | |
|---|---|
| Site: | Perry  |
| Issue date: | 04/16/2002 |
| From: | Campbell G FirstEnergy Nuclear Operating Co |
| To: | Document Control Desk, Office of Nuclear Reactor Regulation |
| References | |
| PY-CEI/NRR-2630L | |
| Download: ML021200067 (148) | |
Text
FEN O C Perry Nuclear Power Plant FENOC10 Center Road Perry, Ohio 44081 FirstEnergy Nuclear Operating Company Guy G. Campbell 440-280-5224 Vice President - Nuclear Fax. 440-280-8029 April 16, 2002 PY-CEL/NRR-2630L United States Nuclear Regulatory Commission Document Control Desk Washington, D.C. 20555 Perry Nuclear Power Plant Docket No. 50-440 Annual Environmental and Effluent Release Report Ladies and Gentlemen:
Enclosed is the Annual Environmental and Effluent Release Report for the Perry Nuclear Power Plant, Unit 1, for the period of January 1, 2001 through December 31, 2001. This document includes the radiological environmental operating report, radioactive effluent release report, and the non-radiological environmental operating report which satisfies the requirements of the PNPP Technical Specifications, the Offsite Dose Calculation Manual, and the Environmental Protection Plan, Appendix B of the PNPP Operating License.
Also enclosed are the current Offsite Dose Calculation Manual and the Process Control Program which refelect the changes that were described within the Annual Environmental and Effluent Release Report.
If you have any questions or require additional information, please contact Michael E. Doty at (440) 280-5599.
Very truly yours,
Enclosures:
- 1. Annual Environmental and Effluent Release Report
- 2.
Offsite Dose Calculation Manual
- 3. Process Control Program cc: NRC Project Manager NRC Region III NRC Resident Inspectors Office
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2001 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT for the Perry Nuclear Power Plant PREPARED BY:
RADWASTE, ENVIRONMENTAL, AND CHEMISTRY SECTION PERRY NUCLEAR POWER PLANT FIRSTENERGY NUCLEAR OPERATING COMPANY PERRY, OHIO MARCH, 2002
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT TABLE OF CONTENTS I
EXECUTIVE SUM M ARY.......................................................
.................................................... I Radioactive Effluent Releases..........................................................................................................
1 Radiological Environm ental M onitoring...................................................................................
2 Land U se Census..............................................................................................................................
3 Clam /M ussel M onitoring........................................................................................................
3 Herbicide U se...................................................................................................................................
3 Special Reports.................................................................................................................................
3 IN TRODUCTION................................................................................................................................
4 Radiation Fundam entals..........................................................................................................
41 Radiation and Radioactivity.......................................................................................................
4 Units of M easure...............................................................................................................................
5 Lower Lim it of Detection........................................................................................................
5 5 Background Radiation......................................................................................................................
6 RADIOACTIVE EFFLUENT RELEASES........................................7 Introduction 7I Regulatory Lim its.............................................................................................................................7 Release Sum m ary.............................................................................................................................
9 M eteorological Data.......................................................................................................................
14 Dose A ssessm ent........................................................................................................................
14 1
Abnorm al Releases.........................................................................................................................
16 N on-Com pliances...........................................................................................................................
18 Offsite Dose Calculation M anual Changes...............................................................................
18 Process Control Program Changes............................................................................................
18 RADIOLOGICAL ENVIRONMENTAL MONITORING...........................................................
19 Introduction....................................................................................................................................
19 Sam pling Locations........................................................................................................................
19 2001 Sam pling Program.................................................................................................................
25 Inter-Laboratory Cross-Check Com parison Program................................................................
32 Land U se Census............................................................................................................................
33 CLAM /M U SSEL M ON ITORING..............................................................................................
36 Introduction....................................................................................................................................
36 Corbicula Program..........................................................................................................................
36 Dreissena Program..........................................................................................................................
37 Conclusions....................................................................................................................................
37 HERBICID E APPLICATION S....................................................................................................
38 SPECIAL REPORTS.........................................................................................................................
39 Non-Com pliances...........................................................................................................................
39 Unreviewed Environm ental Questions..................................................................................... 39 N on-Routine Reports......................................................................................................................
39 Appendix A: 2001 Inter-Laboratory Cross-Check Comparison Program Results....................... 40 Appendix B: 2001 REM P Data Sum m ary Reports.....................................................................
42 Appendix C: 2001 REM P DetailED Data Reports......................................................................
43 1
Appendix D: 2001 Abnormal Gaseous Release Dose Summary and Meteorological Data......
44 Appendix E: Corrections to 2000 AEERR.
56 Table of Contents Page i
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT EXECUTIVE
SUMMARY
The Annual Environmental and Effluent Release Report (AEERR) details the results of environmental and effluent monitoring programs conducted at the Perry Nuclear Power Plant (PNPP) from January 01 through December 31, 2001. This report meets all of the requirements in PNPP Technical Specifications, the Environmental Protection Plan (EPP), and Regulatory Guide 1.2 1. It incorporates the requirements of the Annual Radioactive Effluent Release Report (ARERR),
the Annual Radiological Environmental Operating Report (AREOR) and the Annual Environmental Operating Report (AEOR). Report topics include radioactive effluent releases, radiological environmental monitoring, land use census, clam/mussel monitoring, herbicide use, and special reports. The results of the environmental and effluent programs, for 2001, indicate that the operations of the Perry Nuclear Power Plant did not result in any significant environmental impact.
RADIOACTIVE EFFLUENT RELEASES During the normal operation of a nuclear power plant, small quantities of radioactivity may be released to the environment in liquid and gaseous effluents. Radioactive material may also be released as solid waste. PNPP maintains a comprehensive program to control and monitor the release of all radioactive materials from the site in accordance with all Nuclear Regulatory Commission (NRC) release regulations.
The dose to the general public from the plant's liquid and gaseous effluents was below the applicable regulatory limits. The calculated hypothetical maximum individual whole body dose potentially received by an individual resulting from PNPP liquid effluents was 2.3 IE-03 mrem (0.077 % of the applicable limit). The calculated hypothetical maximum individual whole body dose potentially received by an individual resulting from PNPP gaseous effluents was 6.16E-03 mrem (0.12% of the applicable limit). The summation of the hypothetical maximum individual dose from effluents in 2001 is equivalent to < 0.1 % of the total dose an individual living in the PNPP area receives from all sources of radiation.
Shipments of solid waste consisted of waste generated during water treatment; radioactive material generated during normal daily operations and maintenance, and irradiated components. PNPP complied with all regulations governing radioactive shipments in 2001, making shipments of solid radioactive waste to a licensed burial site.
During 2001, there were two (2) ODCM Controls non-compliance conditions and two (2) abnormal releases:
On March 15, 2001, the liquid radwaste discharge high flow monitor was inoperable for greater than 30 days as a result of a bad micrometer switch connector. Since this connector was not expected to fail, it was not maintained as a spare part. The monitor was out of service for 34 days. Compensatory measures, as required by ODCM Table 3.3.7.9-1, Action 112, were implemented, until the flow monitor was returned to service on March 22, 2001.
On June 02, 2001, the Emergency Service Water total flow monitor, 1P45-N0271, was out of service for greater than 30 days. Erratic flow indications resulted in the monitor being out of service for 48 days. Compensatory measures, as required by ODCM Table 3.3.7.9-1, Action 113, were implemented, until the flow monitor was returned to service on June 19, 2001.
On August 20, 2001, tritium was detected in the Turbine Building I-VAC (M35) condensate drains system effluent. The most probable cause for this abnormal release was the recycling of radioactive gaseous treatment system effluent vent discharges back into the M35 system via the air intake. There was minimal dose consequence to the any member of the general public.
Executive Summary Page 1
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT On December 03, 2001, a Unit I containment vacuum breaker was inadvertently opened during the performance of a surveillance. The inadvertent opening of the vacuum breaker resulted in a potential airborne radioactive effluent release to the environment. The dose contribution as a result of this abnormal release had minimal consequence to any member of the general public.
RADIOLOGICAL ENVIRONMENTAL MONITORING The Radiological Environmental Monitoring Program (REMP) was established in 1981 to monitor the radiological conditions in the environment around PNPP. The REMP is conducted in accordance with PNPP Technical Specifications and the Offsite Dose Calculation Manual (ODCM). This program includes the collection and analysis of environmental samples and evaluation of results.
The REMP was established at PNPP six (6) years before the plant became operational. This pre operational program was designed to provide data on background radiation and radioactivity 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, water and sediment, as well as by measuring radiation directly.
[
Of the 1376 radiological environmental samples collected in 2001, there were approximately 3300 radioactivity analyses performed. The results of the REMP indicate the adequacy of the control of the release of radioactivity in the effluents from PNPP. These results also demonstrate that PNPP complies with all applicable federal regulations. The REMP results are divided into four sections:
atmospheric monitoring, terrestrial monitoring, aquatic monitoring, and direct radiation monitoring:
- Samples of air were collected to monitor the radioactivity in the atmosphere. The 2001 results were similar to those observed for the pre-operational and operational programs from prior years. Only natural background environmental radioactivity was detected.
Terrestrial monitoring included the analysis of milk, produce, and vegetation. The PNPP ODCM does not require vegetation or soil samples to be included in the monitoring program.
The results of the sample analyses in 2001 indicated concentrations of radioactivity similar to that found in previous years. Analyses of other terrestrial samples also detectedL concentrations of radioactivity similar to those observed in previous years, and indicated no build-up of radioactivity attributable to the operation of PNPP.
I Aquatic monitoring included the collection and analyses of water, fish, and shoreline sediments. The 2001 analytical results for water and fish sample showed normal background radionuclide concentrations. The results of sediment sample analyses indicated that the cesium radioactivity was similar to previous years. The average concentration of cesium-137 I
in the sediment was 611.91 pCi/kg, which is within the maximum value of 864 pCi/kg established since 1981. In 1999, a sediment sample of the northwest drain impoundment (sampling location #64) was analyzed to contain 62 pCi/kg of cobalt-60. During 2001, I
enhanced monitoring activities continued within the boundaries of the impoundment. The cobalt-60 remained centered within the organic material located at the top of the spillway, with little or no activity found farther upstream.
Direct radiation measurements showed no change from previous years. The indicator locations averaged 56.26 mrem/year and control locations averaged 54.92 mrem/year. In 2001, radiation dose in the area of PNPP was statistically similar to the radiation dose I
measured at locations greater than ten (10) miles away from the Plant.
Based on these results, during 2001, the operation of the PNPP resulted in no significant increase in the radionuclide concentrations observed in the environment.
L Executive Summary Page 2
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT 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 (5) mile radius of the plant to locate key radiological 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.
CLAMIMUSSEL 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. The monitoring is 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, in 1989. Since no Corbicula have ever been found at PNPP, routine Corbicula monitoring will provide early detection capability, when this pest species arrives at 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.
HERBICIDE USE The use of herbicides on the PNPP site is monitored to ensure compliance with Ohio Environmental Protection Agency (OEPA) requirements and to protect the site's natural areas. Based on the results of on-site herbicide applications, and weekly general site inspections, herbicide use has not had a negative impact on the environment around the plant.
SPECIAL REPORTS Significant environmental events (for example, spills, releases), noncompliance with environmental regulations [e.g., Ohio Environmental Protection Agency (OEPA) discharge limits], and changes in plant design or operation that affect the environment are reported to regulatory agencies as they occur. These special reports are also summarized annually in this report.
On February 19, 2001, the OEPA was notified of a leak from the Circulating Water (CW) system.
This leak was in an underground pipe, which released approximately 15,000 gallons to the environment. This water contained Ferroquest LP7202 at concentrations greater than the discharge limits. The CW system was shut down for repairs and the Ferroquest LP7202 was neutralized to meet Permit limits.
On October 02, 200 1, the OEPA was notified that the permitted discharge limit for Clam-Trol was exceeded during a planned zebra mussel chemical treatment. The chemical injection rate was reduced and detoxification was increased to return the Clam-Trol to within the Permit limit. The zebra mussel chemical treatment test procedure was revised to improve the detoxification method and to require more detoxification chemical during future treatments.
Executive Summary Page 3
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT INTRODUCTION Nuclear energy provides an alternative energy source, which is readily available and has very limited impact upon the environment. To more fully understand nuclear energy as a source of generating I
electricity, one must understand basic radiation concepts and its occurrence in nature.
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 particles are called protons, electrons, and neutrons, respectively. The relatively large protons and neutrons are packed together in the center of the atom called the nucleus. Orbiting around the nucleus are one or more smaller electrons. In an electrically neutral atom, the positively-charged protons in the nucleus balance the negatively charged electrons. Due to their dissimilar charges, the protons and electrons have a strong attraction for each other, which helps hold the atom together. Other attractive forces between the protons and neutrons keep the densely packed protons from repelling each other, and preventing the nucleus from breaking apart.
Atoms with the same number of protons in their nuclei make up an element. The number of neutrons in the nuclei 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 non-radioactive. 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.
L Radioactive atoms attempt to reach a stable, non-radioactive 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 its half-life. Half life is defined as the time required for a radioactive substance to lose half its activity through the process of radioactive decay. Half-lives vary from millionths 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 radioactive decay occurs within the nucleus. This section includes a discussion on the three (3) primary forms of radiation produced by radioactive decay.
[
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 (less than 4 inches, 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 free electrons, which usually carry a negative electrical charge. They L
are much smaller than alpha particles and travel at nearly the speed of light. Thus they can travel for longer distances than alpha particles. External beta radiation primarily affects the skin. Because of their electrical charge, paper, plastic or thin metals can stop beta particles.[
Radiological Effluent Releases Page 4
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Gamma Rays 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. Gamma rays 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 ion and the radiation is called ionizing radiation.
UNITS OF MEASURE Some of the units of measure used in this report require 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 (Ci) 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 (taCi), one millionth of a curie, and the picocurie (pCi), one trillionth of a curie. The mass, or weight, of radioactive material, which would result in one (1) curie of activity, depends on the disintegration rate. For example, one gram of radium-226 is equivalent to one (1) curie of activity. It would require about 1.5 million grams of natural uranium, however, to equal one (1) curie.
Dose Biological damage due to alpha, beta, and gamma radiation may result from the ionization caused by these types of radiation. Some types of radiation, especially alpha particles, which causes dense local ionization, can result in much more biological damage for the same energy imparted than does gamma or beta radiation. Therefore, a quality factor must be applied to account for the different ionizing capabilities of various types of ionizing 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 type of ionizing radiation. The dose equivalent is measured in terms of the Roentgen Equivalent Man (rem). When discussing environmental radiation effects, the rem is a large unit. Therefore, a smaller unit, the millirem (mrem) is often used. One mrem is equivalent to 1/1000 of a rem.
LOWER LIMIT OF DETECTION Sample results are often reported as below the Lower Limit of Detection (LLD). The LLD for an analysis is the smallest amount of radioactive material that will show a positive result for which there can be a 95% 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
(<LLD), it means that no radioactivity was detected. Had radioactivity been present at (or above) the stated LLD value, it statistically would have been detected. The NRC has established LLD values for environmental and effluent sample analyses.
Radiological Effluent Releases Page 5
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT BACKGROUND RADIATION Background radiation is a natural part of nature. Natural radioactive decay also occurs in the soil, water, air, and space. Common sources of radiation that contribute to the natural 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-occurring radioactive isotopes in the human body like potassium-40, the decay of radioisotopes used in medical procedures, man-made phosphate fertilizers (phosphates and uranium are often found together in nature), fallout fo nuclear weapons testing, and even household items like smoke detectors. In the United States, a person's average annual exposure from background radiation is 360 mrem, and is due to the sources shown in Figure 1 [Source: National Council on Radiation Protection and measurements].
I Figure 1: Sources of Background Radiation I
Terresal.
MedcalX-Ray Nudes, Fuel Cyde 0%
2%
Fell-O6 t
<0 1%
Nudear Medicine 4,0%
0.10%
28%%
-Ohmer I
-0,7%I Radon Oavpaoonal Sources 54.7%
030%
Many radionuclides are present in the environment due to sources such as cosmic radiation 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:
Beryllium-7, present as a result of the interaction of cosmic radiation with the upper atmosphere, I
Potassium-40, a naturally occurring radionuclide normally found in humans and throughout the environment, and 3
Radionuclides from nuclear weapons testing fallout, 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 naturallyU occurring and are expected to be present, positive results for these radionuclides are not discussed in the section on the 2001 Sampling Program results. These radionuclides are included, however, in Appendix A, 2001 Inter-Laboratory Cross-Check Comparison Program Results.
U CQI Radiological Effluent Releases Page 6
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT RADIOACTIVE EFFLUENT RELEASES INTRODUCTION The source of radioactive material in a nuclear power plant is the generation of fission products (e.g., noble gas, iodine, and particulate) or neutron activation of water and corrosion products (e.g., tritium and cobalt). The majority of the fission products generated remain within the nuclear fuel pellet and fuel cladding. Fission products that escape from the fuel cladding, as well as the majority of the activated corrosion products, are removed by plant processing equipment.
During the normal operation of a nuclear power plant, small amounts of radioactive material are released in the form of solids, liquids, and gases. PNPP was designed, and is operated in such a manner as to control and monitor these effluent releases. Effluents are controlled to ensure any radioactivity released to the environment is minimal and within all regulatory limits. Effluent release programs include the operation of monitoring systems, in-plant sampling and analysis, quality assurance, and detailed procedures covering all aspects of effluent monitoring.
The liquid and gaseous radioactive waste treatment systems at PNPP are designed to collect and process these wastes in order to remove most of the radioactivity. Effluent monitoring systems are used to provide continuous indication of the radioactivity present and are sensitive enough to measure several orders of magnitude lower than the applicable release limits. This monitoring equipment is equipped with alarms and indicators in the plant control room. The alarms are set to provide warnings to alert plant operators when radioactivity levels reach a small fraction of actual limits. The waste streams are sampled and analyzed to identify and quantify the radionuclides being released to the environment.
Gaseous effluent release data is coupled with on-site meteorological data in order to calculate the dose to the general public. Devices are maintained at various locations around PNPP to 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. The REMP program is described in detail in the next section.
Generation of solid waste is carefully monitored to identify opportunities for minimization. Limiting the amount of material taken into the plant, sorting material as radioactive or non-radioactive, shredding and compacting, or incinerating waste once it is identified help to lower the volume of radioactive solid waste generated. Solid waste is shipped to a licensed burial site.
REGULATORY LIMITS The Nuclear Regulatory Commission has established limits for liquid and gaseous effluents that comply with:
Title 10 of the Code of Federal Regulations, Part 20 (Standards for Protection Against Radiation)
[10CFR20], Appendix B; Title 10 of the Code of Federal Regulations, Part 50 (Domestic Licensing of Production and Utilization Facilities) [IOCFR50], Appendix I; and Title 40 of the Code of Federal Regulations, Part 190 (Environmental Radiation Protection Standards for Nuclear Power Plants) [40CFR 190].
These limits were incorporated into the PNPP Technical Specifications, and subsequently into the PNPP Offsite Dose Calculation Manual (ODCM). The ODCM prescribe the maximum doses and dose rates due to radioactive effluents resulting from the operation of PNPP. These limits are defined in several ways to limit the over-all impact on persons living near the plant. Since there are Radiological Effluent Releases Page 7
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT no other fuel cycle sources near the PNPP the 40CFRl190 limits, which are described below, were not exceeded in 2001.
The 40CFR190 limit for total direct-radiation dose is 25 mrem. For 2001, the total whole body dose to a member of the general public, considering all sectors, was 4.3E-01 mrem. This value was determined by summing the annual whole body doses from liquid and gaseous radioactive effluents, the annual gaseous organ dose (refer to Table 8) and the maximum, direct-radiation dose. Since the direct radiation dose, as determined by TLD, was indistinguishable from natural background (refer to Figure 8), it was not included in the calculation.
Liquid Effluents The concentration of radioactive material released in liquid effluents to unrestricted areas shall be limited to the concentrations specified in 10CFR20, Appendix B, Table 2, Column 2 for radionuclides other than dissolved or entrained noble gases, as required by the ODCM. For dissolved or entrained noble gases, the concentration shall be limited to 2.OE-04 gCi/mL of total activity. These values are the maximum effluent concentrations.
The dose or dose commitment to a member of the public from radioactive materials in liquid effluents released to unrestricted areas shall be limited to the following:
During any calendar quarter:
Less than or equal to 1.5 mrem to the whole body, and Less than or equal to 5 mrem to any organ.
During any calendar year:
Less than or equal to 3 mrem to the whole body, and[
Less than or equal to 10 mrem to any organ.
Gaseous Effluents Dose rate due to radioactive materials released in gaseous effluents from the site to areas at and beyond the site boundary shall be limited to the following:
Noble gases:
Less than or equal to 500 mrem per year to the whole body, and Less than or equal to 3000 mrem per year to any organ.'
Iodine-13 1, iodine-133, tritium, and all radionuclides in particulate form with half lives greater than eight days:
Less than or equal to 1500 mrem per year to any organ Air dose due to noble gases to areas at, and beyond the site boundary, shall be limited to the following:
L During any calendar quarter:
Less than or equal to 5 mrad for gamma radiation, and Less than or equal to 10 mrad for beta radiation.
L During any calendar year:
Less than or equal to 10 mrad for gamma radiation, and Less than or equal to 20 mrad for beta radiation.
Radiological Effluent Releases Page 8
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Dose to a member of the public from iodine-131, iodine-133, tritium, and all radionuclides in particulate form with half lives greater than eight days in gaseous effluents released to areas at and beyond the site boundary shall be limited to the following:
Less than or equal to 7.5 mrem to any organ per any calendar quarter, and Less than or equal to 15 mrem to any organ per any calendar year.
The PNPP ODCM does not contain a concentration reference for gaseous effluents. For this reason, effluent concentrations are not used to calculate maximum release rates for gaseous effluents.
RELEASE
SUMMARY
Effluents are sampled and analyzed to identify both the type and quantity of radionuclides present.
This information is combined with effluent path flow measurements to determine the composition, concentration, and dose contribution of the radioactive effluents.
Liquid Effluents The PNPP liquid radioactive waste system is designed to collect and treat all radioactive liquid waste produced in the plant. The treatment process used for radioactive liquid waste depends on its physical and chemical properties. It is designed to reduce the concentration of radioactive material in the liquid by filtration to remove suspended solids and demineralization to remove dissolved solids. Normally, the effluent from the liquid radioactive waste system is returned to plant systems.
To reduce the volume of water stored in plant systems, however, the processed liquid effluent may be discharge from the plant via a controlled release. In this case, effluent activity and dose calculations are performed prior to, and after discharging this processed water to Lake Erie to ensure regulatory compliance and dose minimization principals are maintained. This section does not include information on the abnormal tritium release related to the Turbine Building HVAC Condensate Drains (M3 5) System. The abnormal release is fully discussed under the "Special Reports" section.
Liquid radioactive waste system effluents may be intermittently released, which are considered to be "batch" releases. Table I provides information on the number and duration of these releases for 2001.
Table 1: Liquid Batch Releases QUARTER I QUARTER 2 QUARTER 3 QUARTER 4 TOTAL Number of batch releases 13 21 23 2
59 Total time period for batch releases, min 3.08E+03 4.77E+03 1.54E+04 4.48E+02 2.37E+04 Maximum time for a batch release, min 2.74E+02 2.45E+02 1.04E+04 2.25E+02 1.04E+04 Average time period for a batch release, min 2.37E+02 2.27E+02 6.71E+02 2.24E+02 4.02E+02 Minimum time for a batch release, min 2.19E+02 2.19E+02 2.07E+02 2.23E+02 2.07E+02 Average stream flow during periods of effluent 2.08E+05 2.33E+05 8.02E+04
- 1. 12E+05 1.58E+05 release into a flowing stream, L/min Table 2 provides information on the nuclide composition for the liquid radioactive waste system effluent releases. If a radionuclide was not present at a level "greater than or equal to the LLD"
(>_LLD), then the value is expressed as "less than the LLD" (<LLD). In each case, LLDs-were met, or were below the levels required by the ODCM.
Table 3 lists the total number of curies (Ci) of each radionuclide present in liquid effluent releases for each quarter. If a radionuclide was not present at a level "greater than or equal to the LLD"
(>_LLD), then the value is expressed as "less than the LLD" (<LLD). In each case, the LLDs were either met, or were below the levels required by the ODCM.
Radiological Effluent Releases Page 9
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Table 2: Summation of All Liquid Effluent Releases QUARTER QUARTER QUARTER QUARTER EST. TOTAL 1
2 3
4 ERROR, %
A.
Fission and Activation Products
- 1. Total Released, Ci 1.06E-02 1.72E-03 3.56E-03 2.74E-05 1.00E+01 (excluding tritium, gases, alpha)
- 2.
Average Diluted Concentration, pCi/mL 3.43E-10 4.99E-11 8.90E-I I L.O0E-12
- 3.
Percent of Applicable Limit, %
N/A N/A N/A N/A B.
- 1. Total Released, Ci 8.49E+00 1.29E+01 1.29E+01 1.65E+00 1.00E+01
- 2.
Average Diluted Concentration, paCi/mL 2.75E-07 3.74E-07 3.23E-07 6.04E-08
- 3.
Percent of Applicable Limit, %
2.8E-02 3.7E-02 3.2E-02 6.OE-03 C.
Dissolved and Entrained Gases
- 1. Total Released, Ci 4.44E-04 6.63E-04 9.80E-05
<LLD 1.00E+01
- 2.
Average Diluted Concentration, I.Ci/mL 1.44E-I I 1.92E-11 2.45E-12
<LLD
- 3. Percent of Applicable Limit, %
7.2E-06 9.6E-06 1.2E-06
<LLD D.
Alpha Activity, Ci
<LLD
<LLD
<LLD
<LLD 1.00E+01 E.
Waste Volume Released, Liters (prior to 1.68E+06 2.73E+06 2.81E+06 2.58E+05 1.GOE+00 dilution)
F.
Dilution Water Volume Used, Liters 3.09E+10 3.45E+!0 4.OOE+10 2.73E+10 2.8E+01
<LLD - Less than the lower limit of detection N/A - Not Applicable, the ODCM does not have a limitfor fission and activation products.
Table 3: Radioactive Liquid Effluent Nuclide Composition QUARTER QUARTER QUARTER QUARTER ANNUAL UNIT 1
2 3
4 TOTAL Tritium Ci 8.49E+00 1.29E+01 1.29E+01 1.65E+00 3.59E+01 Chromium-51 Ci
<LLD 5.39E-05
<LLD
<LLD 5-39E-05 Manganese-54 Ci 1.65E-04 1.19E-04 1.59E-04
<LLD 4.43E-04 Iron-55 Ci 6.73E-03
<LLD
<LLD
<LLD 6.'.'. E-03 Cobalt-58 Ci 3.18E-04 1.07E-04 5.93E-05
<LLD 4.84E-04 Cobalt-60 Ci 2.29E-03 8.68E-04 6.98E-04 2.74E-05 3.88E-03 Zinc-65 Ci 3.02E-04 1.60E-04
<LLD
<LLD 3.62E-04 Strontium-92 Ci
<LLD 3.38E-05 1.77E-04
<LLD
- 2. 1OE-04 Zirconium-95 cI
<LLD
<LLD 6.33E-05
<LLD 6.33E-05 Rhuthenium-105 Ci
<LLD
<LLD 5.88E-05
<LLD 5.88E-05 Silver-I 10m Ci
<LLD 2.15E-04 7.15E-04
<LLD 9.30E-04 Antimony-124 Ci
<LLD
<LLD 6.91E-04
<LLD 6.91E-04 Antimony-125 Ci 3.91E-04
<LLD 8.66E-04
<LLD 1.26E-03 Iodine-131 Ci 1.40E-05
<LLD
<LLD
<LLD 1.40E-05 Xenon-133 Ci 4.44E-05 6.63E-05 9.80E-05
<LLD 2.09E-04 Cesium-134 Ci 8.52E-05 6.86E-05
<LLD
<LLD 1.54E-04 Cesium-137 Ci 1.20E-04 9.55E-05 7.25E-05
<LLD 2.88E-04 Cesium-138 Ci 6.09E-05
<LLD
<LLD
-LLD 6.09E-05 Lanthanum-140 Ci 8.89E-05
<LLD
<LLD ILLD 8.89E-05 Total for Period Ci 8.50E+00 1.29E+01 1.29E+01 1.65E+00 3.60E+01
<LLD - Less than the lower limit of detection I-Radiological Effluent Releases Page 10 L
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ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Gaseous Effluents Gaseous effluents are made up of fission and activation gases, iodine and particulate releases. The fission and activation gas releases are primarily a result of containment purge operations, small steam leaks, and off-gassing during plant start up and shut down operations. The iodine and particulate releases are primarily a result of small steam leaks. Gaseous effluents from PNPP exit the plant via one of four effluent vents. Each of these four effluent vents contains radiation detectors that continuously monitor the air to ensure that the levels of radioactivity released are well below regulatory limits. Samples are also collected and analyzed on a routine basis to ensure regulatory compliance and dose minimization principals are maintained. The majority of gaseous effluents released from PNPP are considered continuous and at ground level.
A summation of all gaseous radioactive effluent releases is given in Table 4. If a radionuclide was not present at a level "greater than or equal to the LLD" (>_LLD), then the value is expressed as "less than the LLD" (<LLD). In each case, the measured LLDs either met or were below the levels required by the PNPP ODCM.
Table 4: Summation of All Gaseous Effluents QUARTER QUARTER QUARTER QUARTER EST. TOTAL 1
2 3
4 ERROR, %
A. Fission and Activation Products
- 1. Total Released, Ci 5.12E+01 2.13E+00 1.40E+00 1.83E+00 1.00E+01
- 2.
Average Release Rate, pCi/sec 6.59E+00 2.71E-01 1.76E-01 2.30E-01
- 3.
Percent of Applicable Limit, %
N/A N/A N/A N/A B.
- 1.
Total lodine-131 Released, Ci 1.69E-03 1.78E-04 3.91E-04 2.21E-04 1.00E+01
- 2.
Average Release Rate, gCi/sec 2.1 8E-04 2.26E-05 4.92E-05 2.77E-05
- 3.
Percent of Applicable Limit, %
N/A N/A N/A N/A C. Particulates with Half-Lives > 8 days I.
Total Released, Ci 1.05E-03 4.42E-04 4.21E-05 2.99E-04 1.00E+01
- 2.
Average Release Rate, gCi/sec 1.36E-04 5.62E-05 5.30E-06 3.76E-05
- 3.
Percent of Applicable Limit, %
N/A N/A N/A N/A D. Alpha Activity, Ci
<LLD
<LLD
<LLD
<LLD E.
- 1.
Total Released, Ci 7.90E-03 4.21E-02
<LLD 2.54E-02 1.00E+01
- 2.
Average Release Rate, J.LCi/sec i.02E-03 5.36E-03
<LLD 3.19E-03
- 3.
Percent of ODCM Limit, %
N/A N/A N/A N/A
<LLD - Less than the lower limit of detection N/A - Not Applicable, the ODCM does not have a limit forfission and activation products.
The radionuclide composition of all gaseous radioactive effluents for a continuous-mode, ground level release is given in Table 5. If a radionuclide was not present at a level "greater than or equal to the LLD" (>_LLD), then the value is expressed as "less than the LLD" (<LLD). In each case, LLDs were met or were below the levels required by the ODCM.
Radiological Effluent Releases Page 11
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Table 5: Radioactive Gaseous Effluent Nuclide Composition QUARTER QUARTER QUARTER QUARTER ANNUAL UNIT 1
2
- 3.
4 TOTAL A.
FISSION AND ACTIVATION GASES Tritium Ci 7.90E-03 4.21E-02
<LLD 2.54E-02 7.54E-02 Argon-14 Ci 4.61E-02 1.58E-03 4.07E-03
<LLD 5.18E-03 Krypton-85 Ci 8.15E-02
<LLD
<LLD
<LLD 8.15E-02 Krypton-85m Ci 8.0E-01 1.28E-02 9.49E-03
<LLD 1.30E-01 Krypton-87 Ci 4.44E-01 5.71E-02 3.18E-02
<LLD 5.33E-01 Krypton-88 Ci 2.72E-01 5.31E-02 2.93E-02
<LLD 3.54E-01 Xenon-131 m Ci 2.48E-0I
<LLD
<LLD
<LLD 2.48E-01 Xenon-133 Ci 3.93E+01 4.78E-01 3.33E-01 6.76E-01 4.08E+01 Xenon-133m Ci 6.04E-01
<LLD 1.53E-03 2.75E-02 6.33E-01 Xenon-135 Ci 3.OOE+00 1.09E+00 6.50E-01 7.52E-01 5.49E+00 Xenon-135m T
Ci 6.66E-01 I 8.69E-02 1.33E-01 1.57E-01 1.04E+00 Xenon-137 Ci 3.30E+00 1.08E-01 6.97E-02
<LLD 3.48E+00 Xenon-138 Ci 3.16E+00 2.48E-01 1.37E-01 2.15E-01 3.76E+00 Total for Period Ci 5.12E+01 2.17E+00 1.40E+00 1.85E+00 5.66E+01 B.
IODINE Iodine-131 Ci 1.69E-03 1.78E-04 3.91E-04 2.21E-04 2.48E-03 Iodine-132 Ci 4.54E-05
<LLD 2.37E-06
<LLD 2.82E-04 Iodine-133 Ci 1.08E-03 2.88E-04 5.60E-04 2.05E-04 2.13E-03 Iodine-134 Ci
<LLD
<LLD
<LLD
<LLD
<LLD Iodine-135 Ci 2.90E-04 4.34E-05 7.70E-05 6.31E-06 4.17E-04 Total for Period Ci 3.11E-03 5.09E-04 1.03E-03 4.32E-04 5.08E+03 B.
PARTICULATE Manganese-54 Ci 4.77E-07 1.24E-05 1.39E-06
<LLD 1.43E-05 Cobalt-58 Ci
<LLD
- 1. 1OE-06 2.48E-06
<LLD 3.58E-06 Cobalt-60 Ci 6.96E-09 2.01E-05 4.04E-06
<LLD 2.42E-05 Rubidium-88 Ci
<LLD
<LLD
<LLD
<LLD
<LLD Rubidium-89 Ci 6.02E-05
<LLD
<LLD
<LLD 6.02E-05 Strontium-89 Ci 2.79E-08 3.97E-07
<LLD
<LLD 4.25E-07 Strontium-90 Ci 2.86E-09 4.08E-08
<LLD
<LLD 4.37E-08 Strontium-91 Ci
<LLD
<LLD
<LLD
<LLD
<LLD Yttrium-91m Ci
<LLD
<LLD
<LLD
<LLD
<LLD Strontium-92 Ci
<LLD
<LLD
<LLD
<LLD
<LLD Molybdenum-99 Ci
<LLD
<LLD
<LLD
<LLD
<LLD Technetium-99m Ci
<LLD
<LLD
<LLD
<LLD
<LLD Cesium-137 "i
6.21E-05 3.17E-06
<LLD
<LLD 6.53E-05 Cesium-138 I I 6.59E-04 3.61E-04
<LLD 2.53E-04 1.27E-03 Barium-139 Ci 2.72E-04 4.41E-05 3.42E-05 4.62E-05 3.97E-04 Barium-140 Ci
<LLD
<LLD
<LLD
<LLD
<LLD Lanthanum-140 Ci
<LLD
<LLD
<LLD
<LLD
<LLD Lanthanum-142 Ci
<LLD
<LLD
<LLD
<LLD
<LLD Total for Period [
Ci t 1.05E-03 4.42E-04 4.21EF,05 2.99E-04 1.83E-03
<LLD - Less than the lower limit of detection Radiological Effluent Releases Page 12 L
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ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Solid Waste Two (2) shipments of PNPP solid radioactive waste were transported, by truck, directly to the Barnwell, South Carolina, disposal facility for burial. Solid radioactive waste from PNPP was processed and combined with waste from several other utilities by intermediate vendors (Duratek in Oak Ridge, TN; ATG in Oak Ridge TN and Richland, WA; and Studsvik in Erwin, TN). This waste was ultimately sent to the Barnwell, South Carolina, or Clive, Utah, disposal facilities for burial. No irradiated fuel or components were transported from PNPP in 2001. The solid radioactive waste summary in Table 6 include all PNPP shipments.
Table 6: Solid Waste Shipped Offsite for Burial or Disposal A. Type of Solid Waste Shipped
- VOLUME, ACTIVITY, EST. TOTAL m3 Ci ERROR, %
Spent resin, filter sludge, evaporator bottoms, etc.
25.0
-77.7
+/- 25 Dry compressible waste, contaminated equipment, etc.
44.5 18.2
+1-25 Irradiated components, control rods, etc.
0 0
+1-25 Other (describe) 0 0
+/-25 B. Estimate of Major") Nuclide Composition ABUNDANCE EST. TOTAL (by type of waste)
RADIONUCLIDE ERROR, %
Spent Resin, Filter Sludge, Evaporator Bottoms, etc.
Mn-54 12.2
+25 Fe-55 22.7 Co-58 2.4 Co-60 48.7 Ni-63 1.1 Zn-65 7.1 Ag-110m 1.6 Cs-137 1.6 Ce-144 1.1 Dry Compressible Waste, Contaminated Equipment, etc.
Mn-54 1.3
+/- 25 Fe-55 36.3 Co-60 47.8 Ni-63 1.4 Zn-65 4.8 Sb-125 1.3 Ce-144 5.3 Irradiated Components, Control Rods, etc.
None N/A N/A Other (describe)
None N/A N/A C. Disposition Number of Mode of Shipments Transportation Destination Solid Waste 2(2)
Truck Barnwell, SC Irradiated Fuel Shipments 0
N/A N/A N/A - Not Applicable
( 1 ) -- "Major" is defined as any individual radionuclide identified as >1% of the waste type abundance.
(2) -- Additional shipments were made to Studsvik, in Erwin, TN; Durateck, AERC andATG in Oak Ridge, TN; and ATG in Richlana4 WA. This waste was combined with waste from other utilities disposed of at Barnwell, SC or Envirocare of Utah.
Radiological Effluent Releases Page 13
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT METEOROLOGICAL DATA The Meteorological Monitoring System at PNPP consists of a 60-meter tower equipped with two independent systems for measuring wind speed, wind direction, and temperature at both 10-meter and 60-meter heights. The tower also has instrumentation to measure dew point and barometric pressure. Data is logged from the tower through separate data loggers, and transmitted to a common plant computer. This system compiles the data and calculates a variety of atmospheric parameters, communicates with the Meteorological Information Dose Assessment System (MIDAS), and sends data over communication links to the plant Control Room.
DOSE ASSESSMENT The maximum concentration for any radioactive release is controlled by the limits set forth in Title 10 of the Code of Federal Regulations, Part 20 (10CFR20). Sampling, analyzing, processing, and monitoring the effluent stream ensures compliance with these concentration limits. Dose limit compliance is verified through periodic dose assessment calculations. Some dose calculations are conservatively performed for a hypothetical individual who is assumed to reside on the site boundary at the highest potential dose location all year. This person, called the "maximum individual", would incur the maximum potential dose from direct exposure (air plus ground plus water), inhalation, and ingestion of water.
vegetation, and fish. Because no one actually meets these criteria, the actual dose receivw a real member of the public is significantly less than what is calculated forI this hypothetical inr
,dual.
Dose calculations for this maximum individual at the site boundary are performed for two cases.
First, they are performed using data for a 360' radius around the plant site (land and water based meteorological sectors), even though some of these sectors are over Lake Erie, which has no permanent residents. The second calculation is performed considering only those sectors around the plant in which people reside (land-based meteorological sectors).
The calculated hypothetical, maximum individual dose values at the site boundary are provided in Table 7. This table considers all meteorological sectors around PNPP and provides either the whole
[
body or worst-case, organ dose values. If any radionuclide was not present at a level greater than the LLD, it was not used in the dose calculations.
Table 7: Maximum Individual Site Boundary Dose, Considering All Sectors ESTIMATED
% OF TYPE OF DOSE ORGAN DOSE, mrem LIMIT LIMIT Liquid Effluent Whole body 2.3 1E-03 3.OE+00 7.7E-02 GI-Tract 2.99E-03 1.OE+01 3.OE-02 Noble Gas - gamma air N/A 2.59E-02 L.OE+01 2.6E-0I
- beta air N/A 4.62E-02 2.OE+01 2.3E-01 Noble Gas Whole body 6.16E-03 5.OE+00 1.2E-01 Skin 1.65E-02 1.5E+01 L.IE-01 Particulate & Iodine Thyroid 2.02E-02 1.5E+01 1.3E-01 N/A -- Not Applicable I
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ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT The calculated hypothetical, maximum population dose values at the site boundary are provided in Table 8. This table considers all meteorological sectors around PNPP and provides either the whole body or worst-case, organ dose values.
Table 8: Population Dose, Considering All Sectors ESTIMATED ORGAN DOSE person-rem Liquid Effluent Whole body 4.2E-01 Thyroid 1.7E-01 Gaseous Effluent Whole body 6.7E-04 Thyroid 4.2E-03 Table 9 provides the calculated hypothetical maximum site boundary dose values considering only the land-based sectors. If any radionuclide was not present at a level greater than the LLD, it was not used in the dose calculations.
Table 9: Maximum Individual Site Boundary Dose, Considering Sectors on Land ESTIMATED
% OF TYPE OF DOSE ORGAN DOSE, mrem LIMIT LIMIT Liquid Effluent Whole body 2.3 1E-03 3.OE+00 7.7E-02 GI-Tract 2.99E-03 1.OE+01 3.OE-02 Noble Gas
- gamma air N/A 2.76E-03 L.OE+01 2.8E-02
- beta air N/A 4.13E-03 2.OE+O1 2.1E-02 Noble Gas Whole body 5.16E-04 5.OE+00 L.OE-02 Skin 1.30E-03 1.5E+01 8.7E-03 Particulate & Iodine Thyroid 2.09E-03 1.5E+OI 1.4E-02 N/A - Not Applicable Other dose calculations are performed for a hypothetical individual who is assumed to be inside the site boundary for some specified amount of time. This person would receive the maximum dose during the time spent inside site boundary. Because no one actually meets the criteria established for these conservative calculations, the actual dose received by a real member of the public is significantly less than what is calculated for this hypothetical individual. This dose is assessed relative to the offsite dose, and considers dilution, dispersion, and occupancy factors.
The highest hypothetical dose from liquid effluents to a member of the public inside the site boundary is to a person who is fishing on Lake Erie from the shore on PNPP property. The calculations assume that this person will spend 60 hours6.944444e-4 days <br />0.0167 hours <br />9.920635e-5 weeks <br />2.283e-5 months <br /> per year fishing, with a liquid dilution factor of 10. The ratio of the exposure pathway to the doses calculated for offsite locations yields the dose values shown in Table 10.
Table 10: Maximum Site Dose from Liquid Effluents WHOLE BODY ORGAN DOSE, DOSE, m rem mrem First Quarter 1.2E-04 1.3E-04 Second Quarter 4.4E-04 5.2E-05 Third Quarter 3.6E-05 4.2E-05 Fourth Quarter 3.3E-06 3.9E-06 Annual 2.OE-04 2.3E-04 (1 ) - No liquid radioactive effluent releases during this period Radiological Effluent Releases Page 15
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Although several cases were evaluated to determine the highest hypothetical dose from gaseous j
effluents to members of the public inside site boundary, the activity inside the site boundary with the highest dose potential is also shoreline fishing. The cases evaluated included traversing a public road within the site boundary, shoreline fishing (assuming fishing 60 hours6.944444e-4 days <br />0.0167 hours <br />9.920635e-5 weeks <br />2.283e-5 months <br /> per year), non-plant related training, car-pooling, and job interviews. The maximum on-site gaseous doses generated are shown in Table 11.
Table 11: Maximum Site Dose from Gaseous Effluents WHOLE BODY DOSE, ORGAN DOSE, mrem mrem First Quarter 7.3E-04 2.9E-03 Second Quarter 3.OE-04 6.1 E-04 Third Quarter 1.3E-04 8.7E-04 Fourth Quarter 9.3E-05 5.1E-04 j
Annual
- 9. 1E-04 3.9E-03 An average whole body dose to individual members of the public is then determined by combining the dose from gaseous and liquid radiological effluents. The dose from gaseous radiological effluents is based upon the population that lives within 50 miles of PNPP (2,420,000 people). The dose from liquid radiological effluents is determined for the population that receives drinking water from intakes within 50 miles of PNPP (1,820,000 people). The results of this calculation are provided in Table 12.
Table 12: Average Individual Whole Body Dose Liquid Gaseous Effluents (mrem)
Effluents (mrem)
First Quarter 4.OE-10 2.4E-09 Second Quarter 3.3E-10 5.8E-10 Third Quarter 1.9E-10 4.IE-10 Fourth Quarter 3.8E-I1 3.4E-10/
Annual 9.5E-10 2.5E-09 (1) -- No liquid radioactive effluent releases during this period ABNORMAL RELEASES There were two abnormal radioactive release events, during 2001.
Turbine Bldg. HVAC (M35) System Condensate Drains Effluent Tritium Release During routine monitoring of the Turbine Building HVAC (M35) system condensate drains on August 20, 2001, tritium was detected in the effluent. This system was not expected to contain radioactivity, nor was the discharge from this system a radioactive liquid effluent discharge point.
[
The condensate drains collected condensed moisture entrained in the intake air to the M35 system.
By plant design, the condensed moisture from the outside air was discharged to the plant's storm drains as radiologically-clean effluent. The routing of the M35 system condensate drains to the plant's storm drains was implemented to remove a "radioactively clean" source of water from the radioactive liquid treatment system.
In accordance with the PNPP ODCM, this incident was considered an abnormal release. Although I
believed to be only a few days, the exact duration for the release could not be determined. The release was estimated to have started after August 13, 2001, which was the last time the M35 system was sampled and analyzed to have no detectable radioactivity. The immediate corrective action was to route the M35 drains to the radioactive liquid treatment system for processing.
Radiological Effluent Releases Page 16
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT The measured tritium activity of 9.73E-07 J.Ci/mL was 9.7E-02 % of the 10CFR20, Appendix B, Table 2, Column 2, limiting effluent concentration limit. The amount of tritium released over seven (7) days was calculated to be 3.1E-04 Ci. Since these dose values are well below any regulatory limits, this abnormal release (refer to Table 13) had minimal dose consequence to the general public.
Table 13: Turbine Bldg. HVAC Condensate Drain System Abnormal Release ESTIMATED DOSE, ANNUAL
% OF ORGAN mrem LIMIT LIMIT Liquid Effluent Whole body 6.30E-05 3.OE+00 2.1E-03 Liver 6.30E-05 1.OE+01 6.3E-04 The most probable cause for this event was the recycling of the radioactive gaseous treatment system effluent vent discharges back into the plant as part of the air intake. Four factors combined to contribute to the apparent causes associated with this event: 1) the gaseous treatment system effluent vents are considered ground-level release points; 2) the atmospheric high humidity and stability (very little wind); 3) tritium build-up in the plant; and 4) the near "zero discharge" policy for radioactive liquid discharges. It is postulated that the low levels of tritium in the effluent vents being short-cycled back into the M35 system intakes, combined with the contributing factors, resulted in the tritium being concentrated in the M35 drains.
The routing of the M35 drains to the storm drains system was to remove a "radioactively clean" source of water from the radioactive liquid treatment system. By reducing the input of "radioactively clean" water into the radioactive liquid treatment system, the need for discharges is significantly reduced, thus reducing the dose impact on the general public. At the time, engineering recognized the potential for radioactive material to enter the storm drains via this path. Monitoring was implemented, and corrective actions put in place should radioactivity be detected.
Unit 1 Containment Vacuum Breaker Inadvertent Opening On December 03, 2001, at 06:58, the Unit 1 containment vacuum breaker 1M17-F0010 was inadvertently opened, which resulted in a potential airborne radioactive effluent release to the environment. The duration of the release was estimated to be 15 seconds, but for calculational purposes, a release duration of 60 seconds was used. This incident was considered an abnormal release in accordance with the PNPP ODCM. As required by the PNPP ODCM, a grab sample was obtained of the Unit I Containment Building atmosphere and analyzed for principal gamma emitters.
Based on the analytical results and an estimated volume released of 4263 cu ft, compliance with the limits for Derived Air Concentration (0.0148 ýXCi/cc) and 10CFR50 (1.19E-04 pCi/cc) was verified.
The dose contributions from this event (refer to Table 14) had minimal dose consequence to the general public. Refer to Appendix D, 2001 Abnormal Gaseous Release Dose Summary and Meteorological Data for compliance data, dose summaries and meteorological data.
Table 14: Vacuum Breaker Abnormal Event Dose Contribution ESTIMATED ANNUAL
% OF ORGAN DOSE, mrem LIMIT LIMIT Noble Gas
-air gamma NA 1.58E-07 1.OE+01 1.6E-06
-air beta NA 2.92E-07 2.OE+01 1.5E-06 Noble Gas Whole body 9.84E-08 5.OE+00 2.OE-06 Skin 2.65E-07 1.5E+01 1.8E-06 Particulate & Iodine Thyroid 3.70E-07 1.5E+01 2.5E-03 During the performance of surveillance SVI-M17-T2002, Step 5.1.4.5, a plant operator in the field inadvertently operated the control switch for containment vacuum breaker I M 17-FOO 10 instead of Radiological Effluent Releases Page 17
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT
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the switch for containment vacuum breaker 1M 17-F0040. Opening valve IM 17-FOO10 resulted in an unmonitored release path to the environment. The apparent cause of this event was the result of aI human performance error related to attention to detail. The plant operator was not focused on the required switch manipulations prior to actually performing the evolution.
NON-COMPLIANCES There were two (2) non-compliance to the ODCM Controls requirements in 2001:
Radwaste Discharge Header High Flow Monitor Inoperable Greater Than 30 Days
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The liquid radwaste discharge to ESW header high flow monitor was inoperable for greater than 30 days as a result of a hardware failure. The flow monitor failed on 02/16/2001 due to a bad micrometer switch connector. This connector was not expected to fail, therefore, it was not considered a "critical" spare part or maintained in stock. The replacement connector arrived on-site on 03/17/01, with the monitor being returned to service on 03/22/01. The monitor was inoperable
[
for 34 days. In accordance with Control 3.3.7.9, Action b, the flow monitor was declared inoperable and the compensatory requirements of Table 3.3.7.9-1, Action 113, were implemented.
ESW Total Flow Monitor Inoperable Greater Than 30 Days The Emergency Service Water flow monitor 1P45-N0271 was out-of-service for greater than 30 days as a result of excessive turbulence in the monitor's stillwell, when two ESW pumps are operating.
On 5/02/01, the flow monitor was declared inoperable, when a satisfactory channel check could not be obtained. At that time, the monitor was declared inoperable and Control 3.3.7.9, Action b, was implemented. On 06/19/01, the total flow monitor was declared operable, which meant the flow monitor was inoperable for 48 days.
/
OFFSITE DOSE CALCULATION MANUAL CHANGES During this reporting period, there was two (2) changes to the Offsite Dose Calculation Manual:
ODCM Table 4.11.2.1.2-1, Table Notation c. was revised to permit the use of grab samples to demonstrate that the effluent point activity did not increase by greater than three times, when the noble gas monitor is inoperable.
Dose factors were added for Au-199.
PROCESS CONTROL PROGRAM CHANGES
/
During 2001, there were two (2) changes to the Process Control Program:
References for the vendors used to document compliance to the PCP was updated.
Additionally, references to Tech Specifications 1.34 was replaced by PCP Section 1.34.
References to the PNPP Quality Assurance Plan was revised to reference the FENOC Quality Assurance Program Manual.[
Radiological Effluent Releases Page 18
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT RADIOLOGICAL ENVIRONMENTAL MONITORING INTRODUCTION The Radiological Environmental Monitoring Program (REMP) was established at PNPP for several reasons. First, it verifies the adequacy of plant design and operation to control radioactive materials and limit 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 B, Technical Specifications and the ODCM. The Nuclear Regulatory Commission (NRC) established the REMP requirements.
A wide variety of samples are 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 NRC 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 Chemistry Unit staff, the Lake County General Health District, and the State of Ohio Department of Health.
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 added. Vegetation, precipitation and soil were added in 1985. Although the NRC did not require these last three media, they were incorporated into the program to establish baseline data. In 1993, feed/silage sampling was dropped from the program, based on ten years worth of data. For the same reason, strontium analyses were deleted from the program in 1994, gross beta and tritium were deleted from precipitation analyses in 1995, and precipitation sampling was deleted entirely in 1996.
In 1999, grass and soil sampling were dropped from the program. Although not required, the grass, soil and precipitation sampling sites remain available, if future sampling is desired.
SAMPLING LOCATIONS REMP samples are collected at numerous locations, both on site 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. Control locations are those which are considered to be unaffected by plant operation. Typically, they are a greater distance from the plant, in the least prevalent wind 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 15, Figure 2, Figure 3 and Figure 4 identify the PNPP REMP sampling locations.
Many REMP samples are collected in addition to those required by the PNPP ODCM. The ODCM requirements for each sample type are discussed in more detail below. Sample types and locations required by the ODCM are shown in Bold in Table 15.
Radiological Environmental Monitoring Page 19
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Table 15: REMP Sampling Locations (1)
Location #
Description Miles Direction Media( 2 1
Chapel Road 3.4 ENE TLD, AIP 2
Kanda Garden 1.9 ENE Food Products 3
Meteorological Tower 1.0 SE TLD, AIP 4
1 Site Boundary 0.7 S
TLD, AIP 5
Quincy Substation 0.6 SW TLD, Air 6
Concord Service Center 11.0 SSW TLD, AlP 7
Site Boundary 0.6 NE TLD, AIP 8
Site Boundary 0.8 E
TLD 9
Site Boundary 0.7 ESE TLD 10 Site Boundary 0.8 SSE TLD 12 Parmly Rd.
0.6 SSW TLD 12 Site Boundary 0.6 WSW TLD 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 Eubank Garden.
0.8 S
Food Products 20 Rainbow Farms 1.9 E
Food Products 21 Hardy Rd.
5.1 WSW TLD 23 High St. Substation 7.9 WSW TLD 24 St. Clair Ave.
15.1 SW TLD 25 Offshore - PNPP discharge 0.6 NNW Sediment, Fish 26 Offshore - Redbird 4.2 ENE Sediment 27 Offshore - Fairport Harbor 7.9 WSW Sediment 28 CEI Ashtabula Plant Intake 22.0 ENE Water 29 River Rd.
4.8 SSW TLD 31 Wood and River Rd.
4.8 SE TLD 32 Offshore - Mentor 15.8 WSW Sediment, Fish 33 River Rd.
4.5 S
TLD 34 PNPP Intake 0.7 NW Water 35 Site Boundary 0.6 E
TLD, AIP 36 Lake County Water Plant 3.9 WSW TLD, Water 37 Gerlica Farm 1.5 ENE Food Products 51 Rettger Milk Farm 9.6 S
Milk 53 Neff Perkins 0.5 WSW TLD 54 Hale Rd. School 4.6 SW TLD 55 Center Rd.
2.5 S
TLD 56 Madison High School 4.0 ESE TLD 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 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 (1) chronologically missing location numbers denote deleted or retired sampling locations.
(2)
AlP = Air, Iodine and Particulate Veg = Vegetation TLD = Thermoluminescent Dosimeter Radiological Environmental Monitoring Page 20 I
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[1 I1
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Figure 2: KEMP Sampling Locations Within Two Miles of Plant Site NNW NW N
NNE NE ENE E
SSE 1
0 1
2 MILES I
-wm Radiological Environmental Monitoring Page 21 WNW W
WSW SW
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Figure 3: REMP Sampling Locations Between Two and Eight Miles of Plant Site U
I
SSe 0
1 2
3 4
5 L
-E se I
10 MILES C" 3 Radiological Environmental Monitoring Page 22 5
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT C,,
Lt U C-I C
tmn C
'I-)
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I Figure 4: REMP Sampling Locations Greater Than Eight Miles from the Plant Site Co o Radiological Environmental Monitoring Page 23
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ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Sample Analysis When environmental samples are analyzed for radioactivity, several types of measurements are performed to provide information about the types of radiation and radionuclides present. The major analyses that are performed are discussed below.
Gross beta activity measures the total amount of beta-emitting radioactivity present in a sample, and acts as a tool to identify samples that may require further analysis. Beta radiation may be released 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 activity only indicates whether the sample contains normal, or abnormal amounts of beta-emitting radioactivity; it does not specifically identify the radionuclides present.
Gamma spectral analysis provides more specific information than does the analysis for gross beta I
activity. Gamma spectral analysis identifies each radionuclide, and the amount of radioactivity, present in the sample emitting gamma radiation. Each radionuclide has a very specific "fingerprint" that allows for accurate identification and quantification.j Iodine activity analysis measures the amount of radioactive iodine present in a sample. Some media (for example, air sample charcoal cartridges) are analyzed directly by gamma spectral analysis. With other media (for example, milk), the radioiodines are extracted by chemical separation before being analyzed by gamma spectral analysis.
Tritium activity analysis measures the amount of the radionuclide tritium (H-3) present in a sample.
Tritium is an isotope of hydrogen that emits low-energy beta particles. Tritium occurs naturally and I
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 ionizing radiation interacts with the sensitive phosphor material in the TLD. Energy is trapped in the TLD material and can be stored for months or years. This capability provides an excellent method to measure the dose received over long periods of time. The amount of energy that was stored in the TLD as a result ofL interaction with radiation is released by a controlled heating process and measured in a calibrated reading system. As the TLD is 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 reading process also zeroes the TLD and prepares it for reuse. Table 16 provides a list of the analyses performed on environmental samples collected for the PNPP REMP in 2001.
Sample results are often reported as less than the lower limit of detection (< LLD), which is defined as 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 < LLD, it means that noI radioactivity was detected at a value above, or equal to the appropriate ODCM table value. The NRC has established LLD values for REMP sample analyses. The vendor laboratory for REMP sample analyses was able to comply with those values in 2001.
R Radiological Environmental Monitoring Page 24 l
ANNuAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Table 16: REMP Sample Analyses TYPE SAMPLE FREQUENCY ANALYSIS Atmospheric Monitoring Airborne Weekly Quarterly Gross Beta Activity Particulates Gamma Spectral Analysis Airborne Weekly Iodine-131 Radioiodine Terrestrial Monitoring Milk Bi-Monthly Gamma Spectral Analysis Iodine-131 Food Products Monthly Gamma Spectral Analysis Vegetation As Required Gamma Spectral Analysis Soil As Required Gamma Spectral Analysis Aquatic Monitoring Water Monthly Gross Beta Activity, Gamma Spectral Analysis Quarterly Tritium Activity Fish Biannually Gamma Spectral Analysis Sediment Biannually Gamma Spectral Analysis Direct Radiation Monitoring TLD Quarterly Gamma Dose Annually Gamma Dose 2001 SAMPLING PROGRAM The contribution of radionuclides to the environment resulting from PNPP operation is assessed by comparing results from the 2001 program with pre-operational 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, 2001 REMP Data Summary Reports for a detailed listing of these results. The NRC requires special reporting whenever sample analysis results exceed set limits. No values exceeded these reporting levels in 2001.
Program Changes There were no changes to the REMP Program during 2001.
Missed Samples On occasion, samples cannot be collected. This can be due to a variety of events, including equipment malfunction, animal husbandry practices, or lost shipments. Events may also occur which prevent a sample from being collected in the normal way, or prevent a complete sample from being collected. The drying period for goats is an annual occurrence, since unlike cows, goats cannot produce milk year-round. Missing TLDs may be the result of vandalism. When vandalism has been identified as a recurring problem, the TLD is relocated. If the loss of a TLD is determined to be a single or unusual event, it is not normally relocated. Table 17 provides information on samples missed during 2001.
Radiological Environmental Monitoring Page 25
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT
[
Table 17: Missed REMP Samples in 2001 1
MEDIA LOCATION DATE REASON Food Products All April, 2001 Vegetables not ready for harvest Food Products All May, 2001 Vegetables not ready for harvest Food Products 2
June, 2001 Vegetables not ready for harvest Food Products 16 June, 2001 Vegetables not rady, for harvest Food Products 20 June, 2001 Vegetables not r-.i:;y for harvest Lake Water 59 01/25/2001 Sample unavailar-!e due to frozen shoreline Lake Water 60 01/25/2001 Sample unavailable due to frozen shoreline Lake Water 59 02/22/2001 Sample unavailable due to frozen shoreline Lake Water 60 02/22/2001 Sample unavailable due to frozen shoreline Milk 61 January, February, March, Drying period for goats November, December Milk 51 08/06/2001 Sample lost in transit to vendor lab TLD (Annual) 55 01/03/2002 Missing at time of collection; deep snow hampered search Atmospheric Monitoring Air Air sampling is conducted to detect any increase in the concentration of airborne radionuclides. The PNPP ODCM requires five locations (four indicator and one control). Air sampling pumps are used to draw continuous samples at a rate of approximately two cubic foot per minute. The air is drawn through glass fiber filters (to collect particulate material) and a charcoal cartridge (to adsorb iodine).
The samples are collected on a weekly basis, 52 weeks a year, from each of seven air sampling stations. Six (6) of these locations are within four miles of the plant site; the seventh is used as a control location and is eleven miles from PNPP.
On occasion, air sample locations can experience power losses associated with storms and/or malfunctioning equipment. On September 08, 2001, location # 35 experienced such a power loss, which required the complete replacement of the underground transformer that powered the sample station. Although the sample station was without power for 4 days, the sample collected was sufficient to provide the required analytical results.
Air samples are
-zed weekly for gross beta activity and radioiodine activity. The air samples are also analyzed b-,
na spectral analysis quarterly. A total of 364 for air particulate and 364 air radio-iodine samp*.., were collected and analyzed in 2001.
Gross beta activity was detected in all air samples and ranged up to 0.06 pCi/mi3. The annual average gross beta activity at both indicator and control locations was 0.02 pCi/m 3. Historically, the concentration of gross beta in air has been essentially identical at indicator and control locations.
Figure 5 reflects the average gross beta activity for 2001 and the previous years.
Except for naturally occurring beryllium-7, no radionuclides were identified in the gamma spectral analysis above the LLD values. Iodine-131 was not detected in any sample above the LLD of 0.05 pCi/m3.
Radiological Environmental Monitoring Page 26
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Figure 5: Annual Average Gross Beta Activity, in Air 0.05 0.04 kj0.03 3 0.02 0.01 0
Year 0 Indicator
- Control 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 historical data from soil and vegetation samples provides information on the atmospheric radionuclide deposition. The PNPP ODCM requires neither vegetation nor soil samples.
Milk 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 because animals usually feed outside on pasture and not on stored feed. The PNPP REMP includes three (3) milk locations (two within five miles of the plant, and one control). Since the milk sampling locations did not meet the requirements of the ODCM (no milk-producing animals located within the required areas), food product sampling (discussed below) was performed. Milk was collected from the available locations, even though they did not meet the ODCM requirements. If new locations that meet the ODCM requirements are identified in the future, they will be added to the program.
Milk samples are analyzed by gamma spectral analysis for radioiodines and other radionuclides. A total of 51 milk samples were collected in 2001. Iodine was not detected above the LLD of 0.75 pCiIL in 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 Food products can provide a direct pathway to humans by ingestion. They can absorb radionuclides from atmospheric deposition on soil or from irrigation water drawn from a lake or pond receiving airborne or liquid effluents. Also, radionuclides in the soil may be absorbed by the roots of the plants and become incorporated into the edible 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. Food products are collected monthly during the growing season from five farms in the vicinity of PNPP. The control location for food products is 16.2 miles from PNPP.
A total of seventy-seven (77) food product samples were collected and analyzed by gamma spectral analysis in 2001. Five (5) food products were collected which included: beet greens, turnip greens, chinese cabbage, swiss chard and kale. Beryllium-7 and potassium-40, naturally-occurring Radiological Environmental Monitoring Page 27
I ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT radionuclides, were found in several samples, as expected. No other radionuclides were detected above the required LLDs.
Aquatic Monitoring Radionuelides may be present in Lake Erie from many sources other than the PNPP. These sources include atmospheric deposition, run-off/soil erosion, and releases of radioactivity 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, while internal exposure can occur from either direct ingestion of radionuclides or the transfer of radionuclides through the aquatic food chain. Direct ingestion can occur from drinking the water, while the transfer via the aquatic food chain occurs from the eventual consumption of aquatic organisms, such as fish. To monitor these pathways, PNPP samples water, shoreline sediments, and fish.
Water I
Water is sampled from five locations along Lake Erie in the vicinity of the PNPP as required by the PNPP ODCM. 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 I
containers are emptied monthly and the samples shipped to the laboratory for analysis. Samples from two locations are collected weekly and combined. Each month the combined sample is shipped for analysis.
Fifty six (56) water samples were collected and analyzed for gross beta activity and gamma spectral analysis in 2001. From these monthly samples, a quarterly composite sample was obtained and analyzed for tritium activity.
5 Gross beta activity was detected in nine (9) of the fifty-six (56) samples collected. None (0) of the twelve (12) control samples, however, were above the LLD values listed in the ODCM. The detectable (i.e., above the lab LLD value) gross beta activity ranged from 3.06 pCi/L to 4.15 pCiL.
I Referring to Figure 6, the annual average gross beta activity was 3.67 pCi/L at the indicator locations and 3.32 pCi/Lat the control location, using the mean of values >LLD. The significant difference between the pre-1988 data and post-1988 data has been attributed to a change in vendor laboratories I
in 1987/1988. A comprehensive explanation for the observed difference is provided in the 1988 Annual Environmental Operating Report.
3 Figure 6: Annual Average Gross Beta Activity, in Water 12 1
10 0
Dlndicator Year aUContro' etc.
Radiological Environmental Monitoring Page 28
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT There were no radionuclides detected by gamma spectral analysis above the LLD. Tritium was not detected above the LLD value in any of the twenty (20) samples analyzed. These results are well within the range of those measured in previous years, which have ranged from below the LLD to 2,200 pCi/L.
Sampling lake bottom sediments can provide an indication of the accumulation of particulate radionuclides which may lead to internal exposure to humans through the ingestion of fish, the re suspension into drinking water, or as an external radiation source to fishermen and swimmers from shoreline exposure. Although the PNPP ODCM requires only one location, sediment is sampled twice each year from seven (7) locations. Two (2) of the sampling locations are also fish sampling locations. Sediment samples from offshore are collected using a hand dredge. Near shore samples are collected using a scoop. Fourteen (14) sediment samples were collected in 2001 and analyzed by gamma spectrometry.
The predominant radionuclide detected by gamma spectral analysis was naturally-occurring potassium-40. Potassium-40 has been detected in all samples, since the program began in 1981.
Cesium-137 activity was detected in five (5) of the fourteen (14) samples collected and ranged from 210.75 pCi/kg to 1388.10 pCi/kg. The annual average cesium-137 activity was 486.90 pCi/kg at the indicator locations and 799.43 pCi/kg at the control location.
Year-to-year variations in the lake bottom sediment sample activities is expected and beyond the control of PNPP. For example, cesium-137 activity variations (refer to Figure 7) in the control locations from year-to-year may be contributed to:
- 1. The movement of sediment on the lake bottom due to wave action and currents, and
- 2.
Sampling in nearly the same location approximately 41/2 miles off-shore, even with GPS, is extremely difficult.
Figure 7: Annual Average Cesium-137 Concentration in Sediment 1600 1400 a
1200 1000 soo 800 600 400 200 0
0Indicator Year EControl For these reasons, it is unlikely the same bed of sediment is sampled at each collection. The average Cs-137 radioactivity of 611.91 pCi/kg for all locations is within the maximum value of 864 pCi/kg established in 1981.
In 1999, a sediment sample from sample location #64 (northwest drain impoundment) was analyzed to contain 62.00 pCi/kg of cobalt-60. This activity was just above the detection limit. In 2000, ten (10) additional sample locations were established within the impoundment to identify the boundary of the cobalt-60 activity and to support supplemental monitoring activities. For 2001, sampling activities were performed on May 3 0", June 6t, October 8" and October 15". Referring to Radiological Environmental Monitoring Page 29
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT I
Table 18, the cobalt activity for sampling location #64 for the months of May and October, was
<8.9 pCi/kg dry and <6.7 pCi/kg dry, respectively.1 Table 18: Northwest Drain Impoundment Cobalt-60 Activity, pCi/kg (dry)
Location 05/30/01 06/06/01 10/08/01 10/15/01
[
64
< 8.9
< 6.7 64-1
<199
< 24.0 64-2
< 16.3 56+/-30 64-3 138.7 19.2 148 +/- 40 64-4 78.1 29.1 111 +/- 23 64-5
< 10.0 64-6
< 43.5
< 39.3 64-7 142.6+/-32.2 173+25 64-8 112.0 +/- 24.3 119 +/- 29 64-9 128.4131.7 267 +/- 35 64-10 206.0+30.9
__191+/-29 j
- Insufficient sample for analysis For the additional ten (10) sampling locations, in the month of June, the cobalt-60 activity ranged from <16.3 pCi/kg to 206.0 pCi/kg, while for October, the cobalt-60 activity range from
<10.0 pCi/kg to 267.0 pCi/kg. The cobalt-60 activity at sampling location #64 continues to be centered within the organic material at the top of the spillway, with little or no activity found farther upstream.
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 ODCM. 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 sampling.
Twenty-eight (28) fish samples were collected and analyzed by gamma spectral analysis in 2001.
Fourteen (14) species of fish were represented, including walleye, drum, carp, white and redhorse sucker, steelhead, stone and channel catfish, white perch, gizzard shad, smallmouth bass, rock bass, white bass and coho salmon. As expected, naturally occurring potassium-40 was found in all samples. No other radionuclides were detected above the LLD.
Direct Radiation Monitoring Thermoluminscent Dosimeter (TLD)
Environmental radiation is measured directly at twenty-eight locations around the PNPP site, two of which are control locations. The locations are positioned in two rings around the plant as well as at the site boundary. The inner ring is within a one-mile radius of the plantsite; the outer ring is four to five miles from the plant. The control locations are over ten miles from the plant in the two least prevalent wind directions. Each location is equipped with three TLDs, two of which are changed quarterly and one is changed annually.
A total of 251 TLDs were collected and analyzed in 2001. This includes all 224 collected on a quarterly basis and twenty seven (27) of (28) collected annually. During the 4 th quarter collection of TLDs on 1/3/02, all TLDs (quarterly and annual) were collected with the exception of the annual TLD for location #55. A search of the immediate area was performed but possible recovery was hampered by deep snow. It was determined that the location had not been vandalized, but that strong Radiological Environmental Monitoring Page 30 f
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT winds had dislodged the TLD from its mounting point. Annual TLDs are not required per the ODCM and are used for supplemental data only.
In 2001, the annual average dose for all indicator locations was 56.26 mrem, and 54.92 mrem for all control locations. Referring to Figure 8, the average quarterly dose for all indicator locations was 15.95 mtem, and 15.97 mrem for all control locations. Prior to 1988, the TLD results were higher due to a change in the vendor laboratory services. A comprehensive explanation of this difference was provided in the 1988 Annual Environmental Operating Report.
A typographical error was discovered in the 2000 report between Figure 8 and its respective text (refer to Appendix E, 2000 AEERR Corrections). Figure 8 reflected that the 2000 average quarterly TLD control dose was 15.2 mrem vs. the text reference of 9.1 mrem. The correct value was 15.2 mrem, as reflected in the graph.
Figure 8: Average Quarterly TLD Dose 25 20 t.6 15 1
ca5 (3indicator Year
- Control Conclusion Sediment samples continue to confirm cobalt-60 in the northwest drain impoundment. The activity level wasjust above the detection limits. Samples taken upstream did not find any additional activity or the source. Additional monitoring is being performed to monitor this location. An environmental evaluation determined that there would be less impact upon the environment by leaving this material in place. Atmospheric monitoring results were consistent with past results. The prevalent radionuclide 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 sediment samples 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.
Finally, direct radiation measurements are consistent with past data.
Radiological Environmental Monitoring Page 31
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT j
Inter-Laboratory Cross-Check Comparison Program Introduction The purpose of the Inter-laboratory Cross-Check Comparison Program (ICCCP) is to provide an independent check on the vendor laboratory's analytical procedures. Samples with a knownI concentration of specific radionuclides are provided to the vendor laboratory. The vendor laboratory measures and reports the concentration of specified radionuclides. The known values are then compared to the vendor results. Results consistently outside established acceptance criteria indicate I
a need to check instruments or procedures. Regulatory Guide 4.15 specifically required that contractor laboratories that performed environmental measurement participate in the EPA's Environmental Radioactivity Laboratory Inter-Comparison Studies Program, or an equivalent I
program.
The EPA's program is not longer funded and no longer offered. The reason that the EPA program was referenced in the regulatory guide is that the EPA standards were traceable to National BureauL of Standards (now known as National Institute Standard Technology). In response to this problem, Teledyne (our vendor lab) incorporated a program offered by Environmental Resource Associates (ERA Company), which covered the same analyses in the same matrix at the same frequency as the EPA program. The ERA Company has received NIST accreditation for its program, as an equivalent program. In addition to comparison cross checks performed with the ERA Company, 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),
Participating in the Department of Energy's Mixed Analyte Performance Program (MAPEP),
and
+ Participating in the Environmental Measurements Laboratory Quality Assessment Program (EML).
In the 2000 Annual Report, Table A-I (refer to Appendix E, 2000 AEERR Corrections), the "spiked" water sample STW-868 referenced the vendor laboratory results for Ra-228 as 5.6+/-1.0 pCi/L vs. the control limit of 1.3-3.2 pCi/L. Although re-analysis results were identified, no explanation was given for the reason the control limit was not met. Per the vendor lab (Environmental Inc.), the chemistry reanalysis results and the gamma spectroscopy results confirmed that their detectors were functioning properly. The vendor's investigation determined that the probable cause was a possible error in dilution. Sufficient spiked sample was not available to have the dilution steps re-performed.
4 Conclusion Appendix A, 2001 Inter-Laboratory Cross-Check Comparison Program Results, includes results from both the above referenced programs and the ERA Company cross-check program. One (1)I water sample analyzed for Sr-89 was determined to be outside the ERA program control limits.
Delay in processing possibly caused the resulting analysis. Reanalysis determined that the Sr-89 sample was within program control limits. Referring to the In-house "spike" sample results, one (1)
/
water sample analyzed for Ra-228 was lost during the analysis, causing the results to be outside the control limits on the low side. Insufficient sample remained to perform a re-analysis. One other "spiked" sample, Cs-137 in milk, was suspect due to its results being outside the control limits on the high side. A new Cs-137 spike was prepared and analyzed the following month. This value was within the accepted criteria. Two (2) In-house "blank" milk samples analyzed for Sr-90 were found to be outside the program control limits of<1.0 pCi/L liquid. Low levels of Sr-90 remain in the environment and concentrations of (1-5 pCi/I) found in milk is not unusual. The sample's results of Radiological Environmental Monitoring Page 32 l
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT 1.18+/- 0.35 pCi/i and 1.09+/- 0.36 pCi/l respectively, fall within these parameters. For the MAPEP Program, one (1) soil sample analyzed for Am-241 was included as a "false positive" with no activity expected. The resulting analysis was <0.8 Bq/l. In the ERL program, a soil sample analyzed for Bi-212 was found outside the control limits on the high side. The Vendor Laboratory determined that naturally occurring radium and thorium daughters contained in the shield background contributed to the slightly elevated results. To adjust for these occurrences, the vendor lab performs quarterly background readings and calibrates its equipment accordingly. All other analysis results performed under these programs were within the control limits established.
LAND USE CENSUS Introduction Each year a land use census, which is required by Section 3/4.12.2 of the PNPP ODCM, is conducted to identify the locations of the nearest milk animal, garden (of greater than 500 square feet), and residence in each of the meteorological sectors that is over land. 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 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. The 2001 Land Use Census, which was conducted August 8 th and 9th, provided the garden, residence and milk animal locations tabulated in Table 19 and depicted in Figure 9. Note that the W, WNW, NNW, NW, N, and NNE sectors extend over Lake Erie, and therefore, are not included in the survey.
Discussions and Results In general, the predominant land use within the census area continues to be rural/agricultural. The 2001 Land Use Survey used the 1999 survey map produced by the Commercial Survey Co. of Cleveland. GPS units were used for a more accurate and detailed identification of media locations.
Table 19 identifies the nearest residences, by sector, to the PNPP. The table is updated annually to reflect any changes identified during the annual Land Use Census. For 2001, there was only one change required. This change identified the construction of a new home, which resulted in a new "nearest residence" in the ESE sector.
Table 19: Nearest Residence, By Sector LOCATION MILES FROM XIQ VALUE, MAP LOCATOR SECTOR ADDRESS PNPP sec/rn 3 NUMBER NE 4384 Lockwood 0.7 2.66E-06 1
ENE 4460 Lockwood 0.8 1.59E-06 2
E 2626 Antioch 1.1 6.77E-07 3
ESE 2750 Antioch 1.0 5.08E-07 4
SE 4537 North Ridge 1.3 3.44E-07 5
SSE 4243 Parmly 1.2 4.83E-06 6
S 3119 Parmly 0.9 2.25E-06 7
SSW 3121 Center 0.9 1.11E-06 8
SW 3440 Clark 1.2 4.98E-07 9
WSW 3462 Parmly 1.1 8.67E-07 10 Radiological Environmental Monitoring Page 33
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Radiological Environmental Monitoring Page 34 I
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ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT During the 2001 Land Use Census, two (2) changes were identified regarding the nearest milk animal. Although no new milk animals were found, the goat previously identified in the S sector was found to be no longer present. In October, 2001, however, a new goat was identified to exist in the ESE sector and would be ready for milking in the Spring, 2002. These changes are reflected in Table 20.
Table 20: Nearest Milk Animal, By Sector I
LOCATION MILES FROM MAP LOCATOR SECTOR ADDRESS PNPP NUMBER ESE 3485 Dayton 4.0 19 S
3588 River 4.8 18 There were six (6) changes in the nearest gardens recorded during this year's census. These changes are identified in Table 21, which lists nearest gardens occupying at least 500 square feet.
Table 21: Nearest Garden, By Sector LOCATION ADDRESS SECTOR MILES FROM PNPP D/Q VALUE, MAP LOCATOR m"2 NUMBER NE 4384 Lockwood 0.6 1 1.76E-08 11 ENE 4762 Lockwood 1.6 2.08E-09 12 E
2610 Antioch 0.8 1.32E-08 13 ESE 2864 Antioch 1.1 3.96E-09 20 SE 4771 North Ridge 1.5 7 1.97E-09 14 SSE 3323 Call 1.5 2.04E-09 15 S
4176 NorthRidge 1.2 00.OE-08 21 SSW 3121 Center 0.9 i5.58E-09 8
SW 3440 Clark 1.2 2.24E-09 9
WSW
[ 2975 Perry Park 1.3 2.01E-09 17 Radiological Environmental Monitoring Page 35
ANNuAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT CLAM/MUSSEL MONITORING INTRODUCTION Sampling for benthic macro-invertebrates (clams and mussels) has been conducted in Lake Erie in the vicinity of PNPP, since 1971. The clam/mussel program currently focuses on two species:
Corbiculafluminea (Asiatic clam) and Dreissenapolymorpha (zebra mussel).
CORBICULA PROGRAM Monitoring specifically for Corbicula was initiated in response to a NRC bulletin and concerns of the Atomic Safety and Licensing Board. The 2001 monitoring was done as part of the Environmental Protection Plan (Operating License, Appendix B). The program consists of visually inspecting the raw water systems, whenever they are opened for maintenance. The purpose of this program is to detect Corbicula, should it appear at PNPP.
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 Corbicula 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 In 2001, samples were collected from the Service Water (SW), Emergency Service Water (ESW) and Circulating Water (CW) systems at PNPP. All samples were collected by Ponar hand dredge, hand scoop, or scraper. They were examined for asiatic clam shells and fragments. In addition to sample collections, plant components that use raw water are inspected whenever opened for maintenance or repair. Sample collection/inspection dates are listed in Table 22.
Table 22: 2001 Corbicula Monitoring DATE SAMPLE LOCATION i DATE SAMPLE LOCATION 02/04/01 SW Traveling Screens I 03/10/01 Condenser 1A 02/24/01 L ESW "A" Pump Discharge Strainer 03/10/01 Condenser IB 02/26/01 CW Cooling Tower 03/10/01 Condenser IC 02/26/01 ESW Valve 1P45-F0040A 1 03/10/01 Condenser ID 02/22/01 SW Main Lube Oil Cooler B i 03/10/01 Condenser 2A 03/05/01 tCW Strainer DOOO 1 03/10/01 Condenser 2B 03/08/01 Condenser 2A 03/10/01 Condenser 2C 03/09/01 Condenser 2B 03/10/01 Condenser 2D 03/09/01 Condenser 3A 03/10/01 Condenser 5A 03/09/01 Condenser 3B 03/10/01 Condenser 5B 03/09/01 Condenser 3C 03/10/01 Condenser 5C 03/09/01 Condenser 3D 03/10/01 Condenser 5D 03/09/01 Condenser 4A 03/10/01 Condenser 6A 03/09/01 Condenser 4B 03/10/01 Condenser 6B 03/09/01 Condenser 4C 03/10/01 Condenser 6C 03/09/01 Condenser 4D 1 03/10/01 03/09/01 ESW Valve 1P45-F0520 Results 04/30/01 Condenser 6D ESW Traveling Screen "B" As in the past, the 2001 monitoring program did not identify Corbicula in any sample collected.
Clam/Mussel Monitoring Page 36 I
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ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Conclusions The sample collected in June, 1987, was the only indication of Corbicula in the vicinity of PNPP.
Although the presence of Corbicula was detected at the Eastlake Power Plant, it has not been demonstrated that their presence has created any operational problems there, or at PNPP.
DREISSENA PROGRAM Dreissena, or 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 Dreissena monitoring program began in 1989, with monitoring and testing. The current control program was designed and implemented in 1990.
Monitoring In addition to visually inspecting the plant's raw water systems when they are opened for maintenance or repair, monitoring methods include the use of commercial divers, side-stream monitors, and plankton nets. Commercial divers monitor mussel infestation during the inspection of forebays, basins, and the intake and discharge structures. Divers have also been used to take underwater videotapes of the water basins and intake tunnel. Sidestream monitors are flow-through containers that receive water diverted from plant systems, and are normally used in three in-plant locations during the mussel season. The sidestream monitors are fitted with slides and inspected for veliger settlement. A plankton net was used on a limited basis in 2001 to help trend veligers during the spawning season.
Treatment Chemicals used for mussel control in 2001 included chlorine and a commercial molluscicide. The chlorine is intermittently injected into the plant service water, emergency service water, and circulating water systems by metering sodium hypochlorite into each system's influent. Sodium sulfite is added at the plant discharge structure for dechlorination prior to entry into Lake Erie.
The use of a commercial molluscicide requires approval by the Ohio Environmental Protection Agency (OEPA). The chemical selected for use at the PNPP in 2001 was alkyl-dimethyl-benzyl ammonium chloride. One treatment was applied in October, 2001. The active ingredients were detoxified by adsorption onto bentonite clay, prior to discharge into Lake Erie.
Results The effectiveness of the intermittent chlorination treatment has been determined in several ways.
First, visual inspections of raw water-system components are conducted when systems are open during maintenance or repair. In addition, settlement monitors were inspected for new settlement.
No live settlement has been found in any plant component to date.
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. The observed mortality rate in the flow-through container was >99%. To date, PNPP has had no problems related to zebra mussels.
CONCLUSIONS Perry Nuclear Power Plant has taken 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 treatment will be continued to minimize the possibility that PNPP will experience future problems due to zebra mussels.
Clam/Mussel Monitoring Page 37
I ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT HERBICIDE APPLICATIONS
[
Herbicides are used sparingly on the PNPP site. A request must be made to, and approved by the PNPP Chemistry Unit prior to spraying to ensure that only approved chemicals are used, and only in approved areas.
In 200 1, three (3) general herbicide requests were initiated for spraying applications. Each application was in compliance with the Ohio Environmental Protection Agency's rules and1 regulations. There were no adverse environmental impacts observed during weekly site environmental inspections as a result of these applications. The only herbicide approved for use in the Owner-Controlled Area was Round-Up. For each application, the type of weed to be treated h
dictated the herbicide concentration to be used. Table 23 provides detailed documentation for each application in 2001. The volume represents the quantity of herbicide applied, after dilution.
Table 23: 2001 Herbicide Applications Application Area Conc.
Volume
- _Date Location sg ft gal 1
06/08/01 Gravel areas within the perimeter fence 36,000 105
-3.8 07/07/01 Gravel areas within the perimeter fence 79,200 800 3.8 07/16/01 Gravel areas within the perimeter fence 4,000 105 3.8 06/08/01 Gravel areas inside protected area 160,000 205 3.8.I 06/10/01 Gravel areas inside protected area 397,000 200 3.8 07/02/01 Gravel areas inside protected area 14,000 24 3.8 07/09/01 Gravel areas inside protected area 48,000 75 3.8 07/16/01 Gravel areas inside protected area 122,000 250 3.8 I
07/23/01 Gravel areas inside protected area 128,000 210 3.8 07/30/01 Gravel areas inside protected area 162,000 200 3.8 08/06/01 Gravel areas inside protected area 150,000 28 3.8 08/13/01 Gravel areas inside protected area 150,000 50 3.8 08/21/01 Gravel areas inside protected area 120,000 25 3.8 08/27/01 Gravel areas inside protected area 129,000 29 3.8 06/04/01 Gravel areas/Landscaped beds inside owner controlled area 8,920 2
2.8 06/07/01 Gravel areas/Landscaped beds inside owner controlled area 118,000 48 3.8 06/08/01 Gravel areas/Landscaped beds inside owner controlled area 33,000 102 2.8 07/02/01 Gravel areas/Landscaped beds inside owner controlled area 17,000 12 3.8 07/07/01 Gravel areas/Landscaped beds inside owner controlled area 147,000 60 3.8 07/09/01 Gravel areas/Landscaped beds inside owner controlled area 15,000 10 3.8 1
07/16/01 Gravel areas/Landscaped beds inside owner controlled area 19,000 26 2.8 07/17/01 Gravel areas/Landscaped beds inside owner controlled area 24,500 100 3.8 07/24/01 Gravel areas/Landscaped beds inside owner controlled area 194,000 200 3.8 07/31/01 Gravel areas/Landscaped beds inside owner controlled area 62,000 20 2.8 I
08/06/01 Gravel areas/Landscaped beds inside owner controlled area 6,700 9
2.8 08/14/01 Gravel areas/Landscaped beds inside owner controlled area 198,000 50 3.8 08/21/01 Gravel areas/Landscaped beds inside owner controlled area 167,000 50 3.8 08/27/01 Gravel areas/Landscaped beds inside owner controlled area 249,000 80 3.8 08/28/01 Gravel areas/Landscaped beds inside owner controlled area 147,000 58 3.8 09/05/01 Gravel areas/Landscaped beds inside owner controlled area 157,000 28 3.8 09/17/01 Gravel areas/Landscaped beds inside owner controlled area 156,000 26 3.8
/
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Herbicide Usage Page 38
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT SPECIAL REPORTS NON-COMPLIANCES NPDES Permit The National Pollutant Discharge Elimination System (NPDES) permit is issued by the Ohio Environmental Protection Agency (OEPA). It establishes monitoring requirements and limits for discharges from the PNPP. It also specifies the locations from which the plant is allowed to discharge.
On February 19, 2001, the OEPA was notified of a leak from the Circulating Water (CW) system.
This leak was in an underground pipe, which released approximately 15,000 gallons to the environment. This water contained Ferroquest LP7202 at concentrations greater than the discharge limits. The CW system was shut down for repairs and the Ferroquest LP7202 was neutralized to meet Permit limits.
On October 02, 2001, the OEPA was notified that the permitted discharge limit for Clam-Trol was exceeded, during a zebra mussel chemical treatment evolution. The chemical injection rate was reduced and detoxification was increased to return the Clam-Trol to within the Permit limit. The zebra mussel chemical treatment test procedure was revised to improve the detoxification method and to require more detoxification chemical during future treatments.
Environmental Protection Plan The Environmental Protection Plan (EPP), which is a part of the PNPP Operating License, requires a non-radiological environmental monitoring and reporting program be established at the PNPP.
There were no instances of an EPP non-compliance identified in 2001.
UNREVIEWED ENVIRONMENTAL QUESTIONS All proposed changes to the PNPP design or operation, as well as tests or experiments, must be evaluated for potential environmental impacts in accordance with the EPP and administrative quality assurance procedures. In 2001, these reviews ensured that no changes to the facility or programs were performed, which could have resulted in an adverse environmental impact. Therefore, there were no potentially significant unreviewed environmental questions identified.
NON-ROUTINE REPORTS There were two (2) non-routine reports submitted in 2001.
On March 13, 2001, the OEPA was contacted to request permission to bypass Circulating Water in accordance with NPDES permit requirements.
On June 14, 2001, the OEPA was notified that a bypass had occurred during routine maintenance of the Emergency Service Water System. This caused untreated Lake Water to flow to the ground.
Authorization was given by the OEPA to continue the bypass for maintenance.
Special Reports Page 39
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT
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APPENDIX A, 2001 INTER-LABORATORY CROSS-CHECK COMPARISON PROGRAM RESULTS I.
Al Appendix A Page 40
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Environmental, Inc., Midwest Laboratory, formerly Teledyne Brown Engineering Environmental Services, Midwest Laboratory has participated in inter-laboratory cross-check comparison programs since the formulation of it's quality control program in December, 1971. These programs are operated by agencies which supply environmental type samples (e.g., milk or water) containing concentrations of radionuclides known to the issuing agency but not to participant laboratories. The purpose of such a program is to provide an independent check on a laboratory's analytical procedures and to alert it of any possible problems.
Participant laboratories measure the concentration of specified radionuclides and report them to the issuing agency. Several months later, the agency reports the known values to the participant laboratories and specifies control limits. Results consistently higher, or lower than the known values or outside the control limits indicate a need to check the instruments or procedures used.
The results in Table A-I were obtained through participation in the environmental sample crosscheck program for milk, water and air filters during the past twelve months. Data for previous years is available upon request. The U.S. Environmental Protection Agency, Office of Research and Development, National Exposure Research Laboratory, Characterization Research Division-Las Vegas, Nevada, conducted this program.
The results in Table A-2 were obtained for Thermoluminescent Dosimeters (TLDs), via various International Intercomparisons of Environmental Dosimeters under the sponsorships listed in Table A-2. Results of cross-check testing with Teledyne Brown Engineering are also listed.
Table A-3 lists results of the analyses on in-house "spiked" samples for the past twelve months. All samples are prepared using NIST traceable sources. Data for previous years is available upon request.
Table A-4 lists results of the analyses on in-house "blank" samples for the past twelve months. Data for previous years is available upon request.
Table A-5 lists results of the in-house "duplicate" program for the past twelve months. Acceptance is based on the difference of the results being less than the sum of the errors. Data for previous years is available upon request.
The results in Table A-6 were obtained through the participation in the Mixed Analyte Performance Evaluation Program.
The results in Table A-7 were obtained through the participation in the Environmental Measurement Laboratory Quality Assessment Program.
Attachment A lists acceptance criteria for "spiked" samples.
Al Appendix A Page 41
12-31-01 ATTACHMENT A ACCEPTANCE CRITERIA FOR "SPIKED" SAMPLES LABORATORY PRECISION: ONE STANDARD DEVIATION VALUES FOR VARIOUS ANALYSESO One Standard Deviation Analysis Level for single determinations Gamma Emitters Strontium-89b Strontium -90b Potassium-40 Gross alpha Gross beta Tritium Radium-226,-228 Plutonium Iodine-131, Iodine-129b Uranium-238, Nickel-63b Technetium-99b Iron-55 b 5 to 100 pCi/liter or kg
> 100 pCi/liter or kg 5 to 50 pCi/liter or kg
> 50 pCi/liter or kg 2 to 30 pCi/liter or kg
> 30 pCi/liter or kg
> 0.1 g/liter or kg 20 pCi/liter
> 20 pCi/liter 100 pCi/liter
> 100 pCi/liter 4,000 pCi/liter
> 4,000 pCi/liter 0.1 pCi/liter 0.1 pCi/liter, gram, or sample 55 pCi/liter
> 55 pCi/liter 35 pCi/liter
> 35 pCi/liter 50 to 100 pCi/liter
> 100 pCi/liter Othersb 5.0 pCi/liter 5% of known value 5.0 pCi/liter 10% of known value 5.0 pCi/liter 10% of known value 5% of known value 5.0 pCi/liter 25% of known value 5.0 pCi/liter 5% of known value 1s = (pCi/liter) =
169.85 x (known)""9*
10% of known value 15% of known value 10% of known value 6.0 pCi/liter 10% of known value 6.0 pCi/liter 15% of known value 10 pCi/liter 10% of known value 20% of known value A2
" From EPA publication, "Environmental Radioactivity Laboratory Intercomparison Studies Program, Fiscal Year, 1981-1982, EPA-600/4-81-004.
b Laboratory limit.
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Table A-1.
Interlaboratory Comparison Crosscheck program, Environmental Resource Associates (ERA)a.
Concentration in pCi/Lb Lab Sample Date Control Code Type Collected Analysis Laboratory resultc ERA Resultd Limits Gr. Alpha Gr. Beta 1-131 Ra-226 Ra-228 Uranium H-3 Gr. Alpha Ra-226 Ra-228 Uranium Co-60 Cs-134 Cs-i 37 Gr. Beta Sr-89 Sr-90 Ba-i 33 Co-60 Cs-134 Cs-1 37 Zn-65 Ra-226 Ra-228 Uranium Sr-89 31.9+/-2.1 25.3 +/- 2.7 27.2 +/- 0.8 4.0+/- 0.1 13.8+/-0.4 17.0_+/-0.3 17,400.0+/- 69.7 57.4 +/- 3.5 13.5+/- 0.4 10.1 +/-0.6 14.2_+/-0.2 27.9+/- 1.4 16.0+/-0.4 195.4+/- 1.5 340.0 +/- 51.0 62.8 +/- 5.7 3.4,2 +/- 1.6 37.8+/- 1.2 49.9 +/- 0.7 16.0+/-1.4 208.0 +/- 1.7 37.8+/- 0.7 14.6-+/-0.4 6.2 +/- 0.2 49.0+/- 1.0 19.8+/- 1.5 Delay in processing may have attributed to deviation.
Result of reanalysis; Sr-89, 35.3 +/- 4.4 pCi/L. Sr-90, 25.0 +/- 2.8 pCi/L.
STW-921 STW-922 STW-922 STW-924 STW-931 STW-931 STW-931 STW-932 STW-933 STW-933 Sr-90 Gr. Alpha Gr. Beta H-3 Ra-226 Ra-228 Uranium 1-131 Gr. Alpha Ra-226 26.3+/- 1.1 23.3+/- 1.9 48.5 +/- 4.6 2,680.0 +/- 41.9 10.9 +/- 0.2 9.7+/-1.1 11.2+/- 0.1 7.7 +/- 0.3 82.2 +/- 4.0 9.5+/- 1.2 STW-897 STW-897 STW-900 STW-902 STW-902 STW-902 STW-903 STW-917 STW-917 STW-917 STWN-917 STW-918 STW-918 STW-918 STW-918 STW-918 STW-918 STW-919 STW-919 STW-919 STW-919 STW-919 STW-920 STW-920 STW-920 STW-921 WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER Al-1 Jan, 2001 Jan, 2001 Feb, 2001 Feb, 2001 Feb, 2001 Feb, 2001 Mar, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jul, 2001 45.7+/- 11.4 16.7 +/- 5.0 28.3 +/- 3.0 4.7 +/- 0.7 14.4 +/- 3.6 20.4 +/- 3.0 17,800.0 +/- 1,780.0 56.0 +/-14.0 17.7 +/-2.7 8.1 +/-2.0 15.6 +/- 3.0 26.4 +/- 5.0 16.9 +/- 5.0 186.0 +93 343.0 +/-1.7 64.1 +/- 5.0 33.8 +/- 5.0 36.0 +/- 5.0 46.8 +/- 5.0 15.9 +/- 5.0 197.0 +/- 9.9 36.2 +/- 5.0 15.4+/- 2.3 4.5 +/- 1.1 55.7 +/- 5.6 31.2 +/- 5.0 25.9 +/- 5.0 17.8 +/- 5.0 53.0 +/-10.0 2,730.0 +/- 356.0 10.8+/- 1.6 9.0 +/- 2.2 13.1 +/-3.0 7.7 +/- 2.0 97.5+/- 24.4 10.8 +/-1.6 25.9 - 65.5 8.0 - 25.4 23.1 - 33.5 3.4 - 5.9 8.2-20.6 15.2 -25.6 14,700. - 20,900.0 31.8-80.2 13.1 -22.3 4.6-11.6 10.4-20.8 17.7-35.1 8.2 - 25.6 170.0 - 202.0 252.0 - 428.0 55.5 - 72.8 25.1 -42.5 27.3 - 44.7 38.1 - 55.5 7.2 - 24.6 180.0 - 214.0 27.5 - 44.9 11.4-19.4 2.6 - 6.5 46.1 - 65.3 22.5 - 39.9 17.2 - 34.6 9.1 - 26.5 35.7 - 70.3 2,110.0 - 3,350.0 8.0- 13.6 5.1 - 12.8 7.9-18.3 4.2-11.2 55.3-140.0 8.0- 13.6 WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER Jul, 2001 Jul, 2001 Jul, 2001 Aug, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Oct, 2001 Oct, 2001 Oct, 2001
Table A-1.
Interlaboratory Comparison Crosscheck program, Environmental Resource Associates (ERA)a.
Concentration in pCi/Lb Lab Sample Date Control Code Type Collected Analysis Laboratory resultc ERA Resultd Limits STW-933 WATER Oct, 2001 Ra-228 17.0+/- 0.8 15.6 +/- 3.9 8.9-22.4 STW-933 WATER Oct, 2001 Uranium 32.2+/- 1.4 37.2+/- 3.7 30.7 - 43.6 STW-934 WATER Oct, 2001 Co-60 82.4+/- 0.9 78.4+/- 5.0 69.7-87.1 STW-934 WATER Oct, 2001 Cs-1 34 52.2+/- 1.3 54.1 +/- 5.0 45.4-62.8 STW-934 WATER Oct, 2001 Cs-1 37 39.4_+/- 0.6 37.9 +/- 5.0 26.3 - 43.7 STW-934 WATER Oct, 2001 Gr. Beta 166.0+/-7.1 192.0+/-28.8 142.0- 242.0 STW-934 WATER Oct, 2001 Sr-89 12.8 +/-0.8 16.7 +/- 5.0 8.0 -25.4 STW-934 WATER Oct, 2001 Sr-90 6.8 +/- 0.7 7.7 +/- 5.0
-1.0 - 16.4 STW-935 W-ATER Oct, 2001 Gr. Alpha 63.5+/-2.5 64.0 +/- 16.0 36.5 - 91.5 STW-935 WATER Oct, 2001 Gr. Beta 26.0+/-1.2 21.5 +/- 5.0 12.8 - 30.2 STW-938 WATER Nov, 2001 Ba-133 66.7+/-1.2 69.3+/-6.9 57.5-81.1 STW-938 WATER Nov, 2001 Co-60 59.3+/- 0.6 59.7 +/-5.0 51.0-68.4 STW-938 WATER Nov, 2001 Cs-134 86.7+/- 1.5 93.9+/-5.0 85.2-103.0 STW-938 WATER Nov, 2001 Cs-137 45.0+/- 1.0 42.0+/-5.0 33.3-50.7 STW-938 WATER Nov, 2001 Zn-65 80.7 +/- 0.6 77.3 +/- 7.7 63.9 - 90.7 Results obtained by Environmental, Inc., Midwest Laboratory as a participant in the environmental samples crosscheck program operated by Environmental Resources Associates (ERA).
'All results are in pCi/L, except for elemental potassium (K) data in milk, which are in mg/L; air filter samples, which are in pCi/Filter.
c Unless otherwise indicated, the laboratory result is given as the mean +/- standard deviation for three determinations.
"d Results are presented as the known values, expected laboratory precision (1 sigma, 1 determination) and control limits as provided by ERA.
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Table A-2. Crosscheck program results; Thermoluminescent Dosimeters. (TLDs).
mR Lab Known Lab result Code TLD Type Date Measurement Value
+/- 2 Sigma Control Limits Teledyne Brown En-qineerinoq 2000-1 LiF-100 Chips 2000-1 LiF-100 Chips 2000-1 LiF-100 Chips Mar, 2000 Mar, 2000 Mar, 2000 Reader 1, #1 Reader 1, #2 Reader 1,#3 17.8 35.5 62.2 14.4 +/-0.2 32.4 +/- 0.1 61.8 +/- 0.9 12.46 - 23.14 24.85 - 46.15 43.54 - 80.86 Teledyne Brown Enqineeringq 2000-2 CaSO,: Dy Cards Mar, 2000 2000-2 CaSO,: Dy Cards Mar, 2000 2000-2 CaSO,: Dy-Cards Mar, 2000 Chips and cards irradiated by Teledyne 12th International Intercomparison 022-1 CaSO,: Dy Cards 022-1 CaSO,: Dy Cards 022-1 CaSO4: Dy Cards 022-1 CaSO,: Dy Cards 022-1 CaSO4 : Dy Cards Environmental, Inc.
2001-1 CaSO,: Dy Cards 2001-1 CaSO,: Dy Cards 2001-1 CaSO4: Dy Cards 2001-1 CaSO4: Dy Cards 2001-1 CaSO,: Dy Cards 2001-1 CaSO,: Dy Cards 2001-1 CaSO4: Dy Cards 2001-1 CaSO,: Dy Cards Jun, 2000 Jun, 2000 Jun, 2000 Jun, 2000 Jun, 2000 Dec, 2001 Dec, 2001 Dec, 2001 Dec, 2001 Dec, 2001 Dec, 2001 Dec, 2001 Dec, 2001 Reader 1, #1 Reader 1, #2 Reader 1,#3 Brown Engineering, Field Field 1 Field 2 Field 3 Lab, 1 Reader 1, #1 Reader 1, #1 Reader 1, #2 Reader 1, #2 Reader 1, #3 Reader 1,#3 Reader 1, #4 Reader 1,#4 17.8 21.3+/-0.3 35.5 40.1 1.9 62.2 69.9 3.5 Westwood, New Jersey, in March 161.0 548.0 391.0 623.0 391.0 4.0 4.0 7.1 7.1 15.9 15.9 63.6 63.6 184.9 +/-1.9 502.2 +/-1.7 412.0 +/- 2.9 643.2 +/- 2.9 442.8 +/- 2.5 3.7+/-0.1 3.4+/-0.1 7.9 +/- 0.2 7.6 +/- 0.3 18.6+/--0.4 19.6+/-0.1 78.2 +/- 1.2 79.9 +/- 2.5 12.46 - 23.14 24.85-46.15 43.54 - 80.86 of 2000.
112.70- 209.30 383.60- 712.40 273.70 - 508.30 436.10 - 809.90 273.70 - 508.30 2.79-5.17 2.79-5.17 4.95-9.19 4.95-9.19 11.13-20.67 11.13-20.67 44.53 - 82.69 44.53 - 82.69 A2-1
Table A-3.
In-house "spike" samples.
Concentration in pCi/La Lab Sample Date Laboratory results Known Controlc Code Type Collected Analysis 2s, n=lb Activity Limits SPAP-477 SPW-479 SPW-481 SPW-481 SPW-482 SPW-482 SPW-483 SPW-483 Sample was SPW-485 SPW-485 SPW-485 SPW-485 SPAP-754 SPW-1 037 SPW-1 037 SPW-1224 SPW-1224 SPW-1225 SPW-1225 SPW-1272 SPW-1272 SPVE-1 274 SPCH-1276 SPMI-1270 SPMI-1270 The Cs-1 37 SPMI-1270 SPU-2901 SPW-2161 SPU-3128 SPW-3129 Air Filter Water Water Water Water Water Water Water lost during Water Water Water Water Air Filter Water Water Water Water Water Water Water Water Vegetation Charcoal Milk Milk spike is sus Milk Urine Water Urine Water Jan, 2001 Cs-1 37 Jan, 2001 H-3 Jan, 2001 Gr. Aiph Jan, 2001 Gr. Beta Jan, 2001 Gr. Alph Jan, 2001 Gr. Beta Jan, 2001 Ra-226 Jan, 2001 Ra-228 analysis. Insufficient samp Jan, 2001 Co-60 Jan, 2001 Cs-134 Jan, 2001 Cs-137 Jan, 2001 Sr-90 Jan, 2001 Gr. Beta Feb, 2001 U-233/4 Feb, 2001 U-238 Feb, 2001 Ra-226 Feb, 2001 Ra-228 Feb,2001 Gr. Alph Feb, 2001 Gr. Beta Feb,2001 1-131.
Feb, 2001 1-131(g)
Feb, 2001 1-131(g)
Feb, 2001 1-131(g)
Mar, 2001 Cs-134 Mar, 2001 Cs-137 pect; A new cesium spike Mar, 2001 1-131(g)
Mar, 2001 H-3 Mar, 2001 Ra-228 Apr, 2001 H-3 Apr, 2001 Gr. Alpha 1.76 +/- 0.02 1.68 1.01 -2.35 54702.00 +/- 644.00 54549.00 43639.20 - 65458.80 a
58.08+/- 2.79 69.14 34.57 - 103.71 213.83+/- 3.07 220.26 198.23 - 242.29 a
51.77+/-2.18 69.14 34.57-103.71 202.48 +/-2.98 220.26 198.23 - 242.29 20.11 +/- 0.34 20.86 14.60 - 27.12 10.55+/-2.02 19.43 13.60 - 25.26 le available to perform reanalysis.
33.53_+/-3.40 31.13 21.13 - 41.13 32.80 +/- 2.54 30.81 20.81 - 40.81 42.10 +/- 5.60 36.00 26.00 - 46.00 154.34+/-_3.49 137.66 110.13-165.19 8.53 +/- 0.02 7.88
-2.12 - 17.88 3.74+/-0.10 4.17 2.50-5.84 3.81 +/-0.10 4.17
-7.83 - 16.17 21.25+/- 0.50 20.68 14.48 - 26.88 21.76 +/-2.65 19.27 13.49 - 25.05 a
71.87+/-3.07 69.14 34.57 - 103.71 36.30 +/-1.47 28.75 18.75 - 38.75 56.82 +/-0.71 63.05 50.44 - 75.66 65.69+/- 10.21 63.05 53.05 - 73.05 0.78 +/-0.05 0.76 0.45 - 1.06 1.57+/-0.05 1.58 0.95-2.21 31.89 +/-4.71 29.77 19.77 - 39.77 46.61 +/- 8.81 35.90 25.90 - 45.90 has been prepared. Reference to SPMI-3232.
81.92+/-10.80 81.95 71.95 - 91.95 51512.00+/- 1369.00 50189.00 40151.20- 60226.80 29.92 +/-5.13 31.75 22.23 - 41.28 2065.00+/-408.00 2008.00 1317.37 - 2698.63 37.94 +/- 2.42 34.57 17.29 - 51.86 A3-1
£ I
I
Table A-3. In-house "spike" samples.
Concentration in pCi/La Lab Sample Date Laboratory results Known Control' Code Type Collected Analysis 2s, n=lb Activity Limits SPW-3129 SPAP-3508 SPMI-3232 SPMI-3232 SPMI-3232 SPMI-3232 SPMI-3232 SPSO-3356 SPSO-3356 SPAP-3359 SPW-3376 SPW-3376 SPW-3376 SPW-3377 SPW-3129/1 SPW-3129/1 SPW-3129/2 SPW-3129/2 SPVE-3303 SPSO-5701 SPSO-5701 SPW-5779 SPW-5779 SPW-5779 SPF-5781 SPF-5781 SPW-5937 SPW-59441 SPW-59441 SPAP-5703 SPW-3129/3 Water Air Filter Milk Milk Milk Milk Milk Soil Soil Air Filter Water Water Water Water Water Water Water Water Vegetation Soil Soil Water Water Water Fish Fish Water Water Water Air Filter Water Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 May, 2001 May, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Gr. Beta Gr. Beta Cs-1 34 Cs-1 37 1-131 1-131(g)
Sr-90 Co-60 Cs-1 37 Cs-137 Co-60 Cs-134 Sr-90 1-131 Gr. Alpha Gr. Beta Gr. Alpha Gr. Beta 1-131(g)
Co-60 Cs-1 37 Co-60 Cs-1 37 Sr-90 Co-60 Cs-137 H-3 Ra-226 Ra-228 Cs-137 Jul, 2001 Gr. Alpha 117.83 +/- 2.37 0.80 +/- 0.01 32.69 +/- 6.50 44.20 +/- 9.08 48.05 +/- 0.90 55.64+/-11.39 143.77+/- 3.04 18.49 +/- 0.21 18.71 +/-0.24 1.80 +/- 0.01 48.17+/-4.85 37.14 +/- 3.90 159.84 +/- 3.42 68.60 +/- 2.63 37.94 +/- 2.42 117.83 +/-2.37 34.42 +/- 2.14 119.99 +/-2.45 0.81 +/- 0.03 17.42+/- 0.19 16.03 +/- 0.22 250.05+/- 18.63 178.68 +/- 19.89 72.12+/- 2.24 1.87 +/- 0.08 1.43 +/- 0.07 51177.00 +/- 631.00 36.62 +/-1.74 41.46 +/- 6.44 1.81 +/- 0.02 35.31 +/- 3.04 109.46 0.78 33.96 35.79 56.68 56.68 136.82 19.57 16.61 1.67 45.19 33.96 136.82 85.02 34.57 109.46 34.57 109.46 0.86 19.05 16.52 233.26 175.91 68.12 1.79 1.39 50189.00 34.46 36.06 1.67 34.75 98.51 -120.41
-9.22 - 10.78 23.96 - 43.96 25.79 - 45.79 45.34 - 68.02 46.68 - 66.68 109.46 - 164.18 9.57 - 29.57 6.61 -26.61 1.00-2.34 35.19 - 55.19 23.96 - 43.96 109.46 - 164.18 68.02 - 102.02 17.29 - 51.86 98.51 - 120.41 17.29 - 51.86 98.51 - 120.41 0.51 -1.20 9.05 - 29.05 6.52 - 26.52 209.93 - 256.59 158.32 - 193.50 54.50 - 81.74 1.07 - 2.51 0.83 - 1.95 40151.20 - 60226.80 24.12 - 44.80 25.24 - 46.88 1.00 - 2.34 17.38 - 52.13 A3-2
Table A-3. In-house "spike" samples.
Concentration in pCi/La Lab Sample Date Laboratory results Known Controlc Code Type Collected Analysis 2s, n=1b Activity Limits SPW-3129/3 Water Jul, 2001 Gr. Beta 113.28 +/-3.65 109.46 98.51 - 120.41 SPMI-6145 Milk Jul, 2001 Cs-137 188.45+/- 19.10 175.91 158.32-193.50 SPW-6604 Water Jul, 2001 Gr. Alpha 35.36 +/- 1.94 34.57 17.29 - 51.86 SPW-6604 Water Jul, 2001 Gr. Beta 112.56 +/-2.46 108.82 97.94-119.70 SPW-9008 Water Oct, 2001 H-3 48285.00+/-606.10 50189.00 40151.20- 60226.80 SPAP-9010 Air Filter Oct, 2001 Cs-1 37 1.91 +/- 0.01 1.67 1.00-2.34 SPW-1 0723 Water Dec, 2001 U-233/4 40.12 +/- 1.09 41.73 25.04 - 58.42 SPW-1 0723 Water Dec, 2001 U-238 40.16+/-1.09 41.73 29.21 - 54.25 SPAP-11550 Air Filter Dec, 2001 Gr. Beta 1.58+/-0.02 1.56
-8.44 - 11.56 SPW-11757 Water Dec, 2001 Co-60 43.82+/-3.14 41.36 31.36 - 51.36 SPW-11757 Water Dec, 2001 Cs-134 24.11 +/-2.42 22.59 12.59 - 32.59 SPW-11757 Water Dec, 2001 Cs-1 37 52.11 +/-4.40 50.89 40.89 - 60.89 SPMI-11759 Milk Dec, 2001 Cs-134 28.03 +/-2.64 27.10 17.10- 37.10 SPMI-11759 Milk Dec, 2001 Cs-1 37 54.59+/- 5.08 50.89 40.89 - 60.89 SPF-11761 Fish Dec, 2001 Cs-134 0.94+/- 0.02 0.90 0.54-1.26 SPF-11761 Fish Dec, 2001 Cs-137 1.43+/- 0.04 1.43 0.86 -2.00 a All results are in pCi/L, except for elemental potassium (K) in milk, which are in mg/L.; air filter samples, which are in pCi/Filter; and food products, which are in pCi/kg.
b Results are based on single determinations.
c Control limits are based on Attachment A, Page A2 of this report.
NOTE: For fish, Jello is used for the spike matrix. For vegetation, coleslaw is used for the spike matrix.
A3-3 I
I
Table A-4.
In-house "blank" samples.
Lab Code SPAP-478 SPAP-478 SPAP-478 SPW-480 SPW-484 SPW-484 SPW-484 SPW-484 SPW-486 SPW-486 SPW-486 SPW-486 SPAP-755 SPW-1038 SPW-1 038 SPW-1 223 SPW-1223 SPW-1223 SPW-1223 SPMI-1268 SPMI-1268 SPMI-1268 SPW-1271 SPW-1271 SPW-1 271 SPVE-1 273 SPVE-1273 SPCH-1275 SPW-2164 SPU-3126 Sample Type AIR FILTER AIR FILTER AIR FILTER WATER WATER WATER WATER WATER WATER WATER WATER WATER AIR FILTER WATER WATER WATER WATER WATER WATER MILK MILK MILK WATER WATER WATER VEGETATIQN VEGETATION CHARCOAL CANISTER WATER URINE Sample Date Jan 2001 Jan 2001 Jan 2001 Jan 2001 Jan 2001 Jan 2001 Jan 2001 Jan 2001 Jan 2001 Jan 2001 Jan 2001 Jan 2001 Jan 2001 Feb 2001 Feb 2001 Feb 2001 Feb 2001 Feb 2001 Feb 2001 Feb 2001 Feb 2001 Feb 2001 Feb 2001 Feb 2001 Feb 2001 Feb 2001 Feb 2001 Feb 2001 Mar 2001 Apr 2001 Analysis Co-60 Cs-134 Cs-1 37 H-3 Gr. Alpha Gr. Beta Ra-226 Ra-228 Co-60 Cs-134 Cs-137 Sr-90 Gr. Beta U-238 U-238 Gr. Alpha Gr. Beta Ra-226 Ra-228 Cs-1 34 Cs-137 1-131(g)
Co-60 Cs-1 34 Cs-1 37 Cs-1 34 Cs-1 37 1-131(g)
-66.00 +335.00
<1.0
<200.0 2.0 ml. sample volume.
A4-1 Concentration pCi/La.
Laboratory results Acceptance (4.66 Sigma)
Criteria LLD Activityb (4.66 Sigma)
< 1.12
<100.0
< 1.66
<100.0
< 2.46
<100.0
< 162.00
-1.86 +/- 80.40
<200.0
< 0.68
<1.0
< 1.35
<3.2
< 0.02 0.03 +/- 0.01
<1.0
< 0.97 0.43 +/- 0.50
<2.0
< 2.68
<10.0
< 3.46
<10.0
< 5.43
<10.0
< 0.65 0.06 +/- 0.31
<1.0
< 1.60 0.16 +/- 0.90
<3.2
< 0.03
<1.0
< 0.00
<1.0
< 0.46
<1.0
< 1.50
<3.2
< 0.02 0.03 +/-0.01
<1.0
< 0.95 0.45 +/- 0.49
<2.0
< 5.86
<10.0
< 3.02
<10.0
< 7.46
<20.0
< 1.06
<10.0
< 2.61
<10.0
< 2.37
<10.0
< 10.04
<100.0
< 6.00
<100.0
< 0.01
<9.6
< 0.02
< 642.00
Table A-4.
In-house "blank" samples.
Concentration pCi/L2.
Laboratory results Acceptance Lab Sample Sample (4.66 Sigma)
Criteria Code Type Date Analysis LLD Activity' (4.66 Sigma)
SPDW-3130 SPDW-3130 SPMI-3233 SPMI-3233 SPMI-3233 SPMI-3233 SPMI-3233 Low levels of unusual.
SPSO-3357 SPSO-3357 SPAP-3358 SPW-3375 SPW-3375 SPW-3375 SPW-3375 SPDW-3130 SPDW-3130 SPDW-3130 SPDW-3130 SPVE-3304 SPVE-3304 SPVE-3304 SPSO-5702 SPSO-5702 SPSO-5702 SPAP-5704 SPAP-5704 SPAP-5704 SPW-5780 SPW-5780 SPW-5780 WATER Apr2001 WATER Apr2001 MILK Apr2001 MILK Apr2001 MILK Apr2001 MILK Apr 2001 MILK Apr2001 Sr-90 are still detected in the SOIL SOIL AIR FILTER WATER WATER WATER WATER WATER WATER WATER WATER VEGETATION VEGETATION VEGETATION SOIL SOIL SOIL AIR FILTER AIR FILTER AIR FILTER WATER WATER WATER Apr2001 Apr 2001 Apr 2001 Apr2001 Apr 2001 Apr 2001 Apr 2001 May 2001 May 2001 Jun 2001 Jun 2001 Jun 2001 Jun 2001 Jun 2001 Jul 2001 Jul 2001 Jul 2001 Jul 2001 Jul 2001 Jul 2001 Jul 2001 Jul 2001 Jul 2001 Gr. Alpha
< 0.54 Gr. Beta
< 1.46 Cs-1 37
< 2.66 1-131
< 0.26 1-131(g)
< 3.91 Sr-89
< 0.79 Sr-90 environment. A concentration Cs-1 34 Cs-1 37 Cs-1 37 Co-60 Cs-1 34 1-131(g)
Sr-90 Gr. Alpha Gr. Beta Gr. Alpha Gr. Beta Co-60 Cs-1 34 Cs-1 37 Co-60 Cs-1 34 Cs-1 37 Co-60 Cs-1 34 Cs-1 37 Co-60 Cs-134 Cs-1 37
< 14.77
< 11.72
< 0.55
< 2.90
< 3.71
< 0.39
< 0.56
< 0.45
< 1.26
< 0.44
< 1.46
< 7.06
< 11.56
< 8.30
< 12.80
< 13.96
< 8.10
< 0.79
< 0.84
< 0.60
< 1.86
< 2.46
< 3.77 0.04 +/- 0.38 0.67 +/- 1.04
-0.06 +/- 0.14
-0.32 +/- 0.79 1.18 +/-0.35 of (1-5 pCi/L) in milk 0.02 0.05 0.15 0.34 0.09 0.66
+ 0.22
+ 0.27
+ 0.34
+ 0.95
+ 0.32
+ 1.04 A4-2
<1.0
<3.2
<10.0
<0.5
<20.0
<5.0
<1.0 is not
<100.0
<100.0
<100.0
<10.0
<10.0
<20.0
<1.0
<1.0
<3.2
<1.0
<3.2
<100.0
<100.0
<100.0
<100.0
<100.0
<100.0
<100.0
<100.0
<100.0
<10.0
<10.0
<10.0 I
L I
Table A-4.
In-house "blank" samples.
Concentration pCi/L'.
Laboratory results Acceptance Lab Sample Sample (4.66 Sigma)
Criteria Code Type Date Analysis LLD Activity' (4.66 Sigma)
SPF-5782 FISH Jul 2001 Co-60
< 5.64
<100.0 SPF-5782 FISH Jul 2001 Cs-134
< 7.51
<100.0 SPW-5938 WATER Jul 2001 H-3
< 163.22
-16.21 +/-85.07
<200.0 SPW-59451 WATER Jul 2001 Ra-226
< 0.01 0.04 +/- 0.01
<1.0 SPW-59451 WATER Jul 2001 Ra-228
< 0.77 0.70 +/- 0.44
<2.0 SPDW-3130 WATER Jul 2001 Gr. Alpha
< 0.54 0.36 +/- 0.40
<1.0 SPDW-3130 WATER Jul 2001 Gr. Beta
< 2.27
-0.78 - 1.35
<3.2 SPMI-6146 MILK Jul2001 Sr-90
< 0.50 1.09 +/-0.36
<1.0 Low levels of Sr-90 are still detected in the environment. A concentration of (1-5 pCi/L) in milk is not unusual.
SPW-6605 WATER Jul 2001 Gr. Beta
< 1.34 0.55 +/-1.01
<3.2 SPW-9009 WATER Oct 2001 H-3
< 160.00
-56.70 +/- 76.50
<200.0 SPAP-9011 AIR FILTER Oct 2001 Co-60
< 0.76
<100.0 SPAP-9011 AIR FILTER Oct 2001 Cs-1 37
< 0.58
<100.0 SPW-5780 WATER Oct 2001 Sr-90
< 0.54 0.36 +/- 0.30
<1.0 SPW-10724 WATER Dec 2001 U-238
< 0.13 0.04 +/- 0.10
<1.0 SPAP-11549 AIR FILTER Dec 2001 Gr. Beta
< 0.00 0.01 +/- 0.00
<3.2 SPW-11756 WATER Dec 2001 Cs-137
< 2.62
<10.0 SPMI-11758 MILK Dec 2001 Cs-137
< 4.00
<10.0 SPMI-11758 MILK Dec 2001 1-131(g)
< 16.57
<20.0 SPF-11760 FISH Dec 2001 Cs-137
< 7.96
<100.0 a Liquid sample results are reported in pCi/Liter, air filter sample results are in pCi/filter, charcoal sample results are in pCi/charcoal, and solid sample results are in pCi/kilogram.
b The activity reported is the net activity result.
A4-3
Table A-5.
In-house "duplicate" samples.
Concentration in pCi/La Lab Sample First Second Averaged Codes L"OLV AP-10675, 10676 AP-10803, 10804 AP-10833, 10834 WW-51, 52 MI-72, 73 MI-96, 97 U-858, 859 MI-389, 390 DW-879, 880 SWU-813,814 MI-708, 709 MI-740, 741 MI-740, 741 MI-789, 790 DW-901, 902 SWU-1 544, 1545 DW-1426, 1427 DW-1426, 1427 WW-1476, 1477 MI-1523, 1524 MI-1523, 1524 MI-1572, 1573 MI-1572, 1573 SW-1648, 1649 MI-1800, 1801 SW-1779, 1780 SW-1779, 1780 MI-1447, 1448 MI-1447, 1448 WW-2115, 2116 SW-1698, 1699 DW-2272, 2273 WW-2356, 2357 AP-2812, 2813 AP-2812, 2813 LW-2217, 2218 Jan, 2001 Jan, 2001 Jan, 2001 Jan, 2001 Jan, 2001 Jan, 2001 Jan, 2001 Jan, 2001 Jan, 2001 Jan, 2001 Feb, 2001 Feb, 2001 Feb, 2001 Feb, 2001 Feb, 2001 Feb, 2001 Feb, 2001 Feb, 2001 Feb, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Analysis Be-7 Be-7 Be-7 H-3 K-40 K-40 Gr. Beta K-40 Gr. Beta Gr. Beta K-40 1-131 K-40 K-40 Gr. Beta Gr. Beta Gr. Beta H-3 H-3 1-131 K-40 K-40 Sr-90 K-40 K-40 Gr. Alpha Gr. Beta 1-131 K-40 H-3 Gr. Beta Gr. Beta Gr. Beta Be-7 Be-7 Gr. Beta 0.06 +/- 0.02 0.04 +/- 0.01 0.04 +/- 0.01 362.60 +/- 94.70 1,566.90+/- 196.80 1,418.30 +/-117.80 2.17 +/-2.47 1,489.20+/-141.10 2.63 +/- 0.52 2.48 +/- 0.58 1,179.40+/-103.00 0.01 +/- 0.26 1,434.00 +/- 156.50 1,584.30+/-158.80 4.67 +/-1.08 3.13 +/- 0.63 2.05 +/- 0.92 42.60 +/- 94.23 53.06 +/- 65.79
-0.01 +/- 0.20 1,396.00 +/-184.80 1,499.20 +/- 113.30 1.65 +/- 0.44 297.80 +/- 67.20 1,425.80+183.30 2.22 +/- 0.73 6.28 +/- 0.74
-0.65 +/- 0.27 1,496.20 +/-155.40 540.04 +/- 111.84 6.07 +/-1.75 2.10+/- 0.86 1.22 +/- 0.50 0.07 +/- 0.02 0.07 +/- 0.02 1.85+/- 0.51 L
0.06 +/- 0.02 0.04 +/- 0.01 0.04 +/- 0.01 417.20 +/- 96.80 1,372.40 +152.50 1,545.70 +/-162.50 4.23 +/- 2.74 1,463.30 +/- 168.20 2.37 +/-0.50 2.46 +/- 0.63 1,280.40 +/- 90.26
-0.12+/- 0.26 1,435.00+/-126.10 1,390.70+/- 136.50 5.54+/- 1.13 2.33 +/- 0.52 2.34 +/- 0.93 131.31 +/--95.34 53.06 +/- 93.03
-0.10_+/-0.37 1,576.00 +184.90 1,326.00 +/- 118.80 1.51 +/- 0.52 344.80 +/- 82.30 1,372.20 +/- 119.70 2.14+/--0.69 6.62 +/- 0.70 0.13+/-0.55 1,413.40 +/-169.60 500.85 +/-110.46 5.57 +/- 1.85 1.63 +/-0.83 1.32 +/- 0.47 0.05 +/- 0.01 0.05 +/- 0.01 2.23 +/- 0.55 0.06 +/- 0.01 0.04 +/- 0.01 0.04 +/- 0.01 389.90 +/- 67.71 1,469.65+/-124.49 1,482.00 +/-100.35 3.20+/-1.84 1,476.25 +/- 109.77 2.50+/- 0.36 2.47 +/- 0.43 1,229.90+68.48
-0.05-+/-0.18 1,434.50+100.49 1,487.50 +104.70 5.11 +/-0.78 2.73 +/- 0.41 2.20 +/- 0.65 86.96 +/- 67.02 53.06 +/- 56.97
-0.06 +/- 0.21 1,486.00+130.71 1,412.60 +/- 82.08 1.58 +/- 0.34 321.30 +/- 53.13 1,399.00 +/-109.46 2.18 +/- 0.50 6.45 +/- 0.51
-0.26 +/- 0.31 1,454.80+/-115.01 520.44 +/- 78.59 5.82 +/-11.27 1.87 +/- 0.60 1.27 +/- 0.35 0.06 +/- 0.01 0.06 +/- 0.01 2.04 +/- 0.37 A5-1 L
1 mesuI R~esult Result
Table A-5.
In-house "duplicate" samples.
Concentration in pCi/La Lab Sample First Second Averaged Codes LJDte AP-2833, 2834 AP-3038, 3039 AP-3038, 3039 DW-2398, 2399 LW-2467, 2468 MI-2446, 2447 AP-3017, 3018 SW-2423, 2424 BS-3103, 3104 SWU-3239, 3240 SS-3322, 3323 W-3990, 3991 BS-4347, 4348 BS-4347, 4348 MI-3364, 3365 SO-3385, 3386 SO-3385, 3386 SO-3385, 3386 CL-4068, 4069 MI-3475, 3476 WW-3545, 3546 MI-3681, 3682 SW-3702, 3703 SW-3702, 3703 BS-4021, 4022 BS-4021, 4022 BS-4021, 4022 BS-4021, 4022 BS-4021, 4022 BS-4021, 4022 BS-4021, 4022 F-3813, 3814 G-4158, 4159 SO-4179, 4180 SO-4179, 4180 SO-4179, 4180 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 Apr, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 Analysis Be-7 Be-7 Be-7 Gr. Beta Gr. Beta K-40 Be-7 K-40 Gr. Beta Gr. Beta K-40 Sr-89 K-40 K-40 K-40 Gr. Alpha Gr. Beta K-40 K-40 Gr. Beta Gr. Beta K-40 Gr. Alpha Gr. Beta Cs-137 H-3 K-40 Pu-238 Pu-239/40 Ra-226 Sr-90 K-40 Be-7 Ac-228 Bi-214 Cs-1 37 0.04 +/- 0.01 0.07 +/- 0.02 0.06 +/- 0.02 1.58 +/- 0.89 2.52 +/- 0.53 1,285.40 +/-177.10 0.05 +/- 0.01 255.60 +/- 59.80 7.99 +/- 1.80 3.30 +/- 0.60 15.99+/- 1.08 91.35 +/-18.94 3,982.40 +/- 489.60 3.26 +/- 0.45 1,325.90 +/- 160.20 6.51 +/- 3.09 24.63 +/- 3.15 19.17 +/-1.08 1.09 +/- 0.27 1,297.10 +/- 114.60 1.57 +/- 0.55 1,417.20+/- 125.70 4.51 +/- 1.66 8.74+/- 1.36 224.30 +/- 30.20 842.00 +/- 47.00 21,117.00 +/- 953.00 80.30 +/- 36.50 49.40 +/- 31.80 7,436.00 +/- 577.90 10.60 +/- 2.71 2.10 +/-0.17 0.37 +/- 0.13 0.45+/- 0.13 0.31 +/- 0.06 0.46 +/- 0.05 0.06 +/- 0.02 0.07 +/- 0.02 0.07 +/- 0.01 1.81 +/- 0.88 2.42 +/- 0.53 1,376.00 +/-175.90 0.05 +/- 0.01 268.40 +/- 65.40 8.17+/- 1.73 4.30 +/- 0.74 15.59+/-1.01 85.29 +/- 23.99 3,255.80 +450.10 3.98 +/- 0.49 1,453.20+/-163.00 9.01 +/- 3.44 28.17+/- 3.12 17.94 +/- 0.76 1.13 +/-0.23 1,433.60 +/-156.60 1.36 +/-0.53 1,496.20+/-124.50 3.22 +/-1.55 7.11 +/-1.38 205.90 +/- 43.00 860.00 +/- 48.00 21,629.00+/-1,357.00 59.50 +/- 22.00 41.10+/-19.60 9,126.00 +/- 751.90 16.80 +/- 3.22 2.30 +/- 0.26 0.41 +/-0.14 0.52 +/- 0.14 0.41 +/- 0.06 0.47 +/- 0.04 0.05_+/- 0.01 0.07_+/- 0.01 0.07 +/- 0.01 1.69 +/- 0.63 2.47 +/- 0.37 1,330.70+/- 124.81 0.05 +/- 0.00 262.00 +/- 44.31 8.08 +/- 1.25 3.80 +/- 0.48 15.79 +/- 0.74 88.32 +/-15.28 3,619.10 +332.53 3.62 +/- 0.33 1,389.55 +/- 114.27 7.76 +/- 2.31 26.40 +/- 2.22 18.56+/-0.66 1.11 +/-0.18 1,365.35 +/- 97.03 1.47 +/- 0.38 1,456.70 +/- 88.46 3.87 +/- 1.13 7.93 +/- 0.97 215.10 +/-26.27 851.00 +/- 33.59 21,373.00+/- 829.10 69.90 +/- 21.31 45.25 +/-18.68 8,281.00 +/- 474.16 13.70+/-2.10 2.20 +/-0.16 0.39 +/-0.10 0.49 +/-0.10 0.36 +/- 0.04 0.47 +/- 0.03 A5-2 r"zesol Result result
Table A-5.
In-house "duplicate" samples.
I Lab Codes SO-4179, 4180 SO-4179, 4180 SO-4179, 4180 SO-4179, 4180 SO-4179, 4180 BS-4233, 4234 BS-4233, 4234 SWU-4376, 4377 DW-4449, 4450 DW-4397, 4398 MI-4114, 4115 F-4284, 4285 DW-4326, 4327 MI-4470, 4471 SW-4493, 4494 BS-4725, 4726 BS-4725, 4726 BS-4725, 4726 MI-4775, 4776 WW-5110, 5111 G-5085, 5086 G-5085, 5086 MI-5259, 5260 MI-5259, 5260 SWU-5422, 5423 VE-5401, 5402 VE-5401, 5402 AP-5830, 5831 SW-5557, 5558
>-5851, 5852 SW-5636, 5637 LW-5681, 5682 G-5535, 5536 G-5535, 5536 G-5535, 5536 AP-5788, 5789 Concentration in pCi/L3 Sample First Second Averaged n-.~
f1 cJaLV May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 May, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jun, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Analysis Gr. Beta K-40 Pb-212 Ra-226 TI-208 Cs-1 37 K-40 Gr. Beta Gr. Beta Gr. Beta K-40 K-40 Gr. Beta K-40 Gr. Beta Co-60 Cs-137 K-40 K-40 H-3 Be-7 K-40 K-40 Sr-90 Gr. Beta Gr. Beta K-40 Be-7 Gr. Beta Be-7 Gr. Beta Gr. Beta Be-7 Gr. Beta K-40 Be-7 rsesUIL Result Result 26.65 +/- 2.63 16.35 +/- 0.86 0.35 +/- 0.04 0.56 +/- 0.98 0.14+/- 0.03 0.03 +/- 0.01 8.18+/- 0.48 2.58 +/- 0.55 2.83 +/- 0.55 9.13+/- 1.26 1,325.90 +/- 118.80 2.23 +/- 0.32 2.60 +/- 0.97 1,514.50+116.60 4.05+/-1.23 112.00+/-24.30 3,083.10+/-100.10 8,143.70 +/- 640.40 1,362.20 +/- 71.80 1,173.50+/-129.10 0.89 +/-0.17 5.13+/-0.39 1,529.70 +122.70 1.69 +/- 0.42 2.59 +/- 0.54 8.12+/-0.24 6.55 +/- 0.52 0.08 +/- 0.01 5.43 +/- 1.70 0.07 +/- 0.02 4.75 +/- 1.38 2.42 +/- 0.37 0.99 +/- 0.29 7.62 +/- 0.12 7.26 +/- 1.03 0.08 +/- 0.02 24.68 +/- 2.52 16.05+/- 0.82 0.43 +/- 0.05 1.03_+/- 0.31 0.17+/- 0.03 0.03 +/- 0.02 7.80 +/- 0.58 2.94 +/- 0.58 3.74 +/- 0.65 10.20+/-1.34 1,394.70 +/- 133.10 2.12+/-0.35 1.47 +/- 0.83 1,456.80+130.90 4.64 +/- 1.32 84.50 +/- 8.70 3,094.80 +/- 35.30 8,083.80 +225.10 1,363.90 + 73.40 1,046.80 +/- 125.20 1.14+/-0.39 5.22 +/- 0.70 1,406.20 +123.80 1.71 +/- 0.44 1.91 +/- 0.52 8.88 +/- 0.26 6.26 +/- 0.65 0.08 +/- 0.01 5.96 +/- 1.56 0.07 +/- 0.02 4.18 +/-1.34 2.18+/- 0.34 0.97 +/- 0.54 7.72 +/-0.12 7.64 +/- 0.93 0.07 +/- 0.02 L
25.67 +/- 1.82 16.20 +/- 0.59 0.39 +/- 0.03 0.79 +/- 0.51 0.15+/- 0.02 0.03 +/- 0.01 7.99 +/- 0.38 2.76+/- 0.40 3.29 +/- 0.43 9.66 +/- 0.92 1,360.30 +/- 89.20 2.18+/- 0.24 2.04 +/- 0.64 1,485.65 +/- 87.65 4.35 +/- 0.90 98.25+/-12.91 3,088.95 +/- 53.07 8,113.75+/- 339.40 1,363.05 +/- 51.34 1,110.15+/-89.92 1.02 +/- 0.21 5.17+/- 0.40 1,467.95 +/- 87.15 1.70 +/- 0.30 2.25 +/- 0.37 8.50_+/-0.18 6.40 +/- 0.42 0.08 +/- 0.01 5.70+/-1.15 0.07 +/- 0.01 4.47 +/- 0.96 2.30 +/- 0.25 0.98 +/- 0.31 7.67 +/- 0.08 7.45 +/- 0.69 0.08 +/- 0.01 I
I I
I 1.
I A5-3
Table A-5.
In-house "duplicate" samples.
Lab Codes AP-5872, 5873 AP-5893, 5894 AP-5809, 5810 SW-5724, 5725 SW-5724, 5725 SW-5767, 5768 LW-5920, 5921 SO-6172, 6173 SO-6172, 6173 SO-6172, 6173 MI-6353, 6354 SW-6376, 6377 VE-6424, 6425 VE-6424, 6425 MI-6445, 6446 LW-6489, 6490 MI-6533, 6534 DW-6835, 6836 MI-6693, 6694 MI-6693, 6694 WW-6952, 6953 MI-6906, 6907 VE-6973, 6974 LW-7851, 7852 MI-7001, 7002 MI-7073, 7074 LW-7145, 7146 MI-7221, 7222 MI-7221, 7222 SWU-7527, 7528 VE-7485, 7486 DW-7506, 7507 MI-7622, 7623 MI-7664, 7665 MI-7876, 7877 G-7960, 7961 Concentration in pCi/La Sample First Second Averaged UaLL Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Jul, 2001 Aug, 2001 Aug, 2001 Aug, 2001 Aug, 2001 Aug, 2001 Aug, 2001 Aug, 2001 Aug, 2001 Aug, 2001 Aug, 2001 Aug, 2001 Aug, 2001 Aug, 2001 Aug, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Analysis Be-7 Be-7 Be-7 Gr. Alpha Gr. Beta 1-131 Gr. Beta Cs-1 37 K-40 Sr-90 K-40 1-131 Gr. Beta K-40 K-40 Gr. Beta K-40 Gr. Beta K-40 Sr-90 Gr. Beta K-40 K-40 Gr. Beta K-40 K-40 Gr. Beta K-40 Sr-90 Gr. Beta K-40 Gr. Beta K-40 K-40 K-40 Be-7 0.07 +/- 0.02 0.08 +/- 0.02 0.07 +/- 0.02 2.95 +/- 0.70 8.79 +/- 0.71 0.79 +/- 0.31 3.06 +/- 0.64 0.30 +/- 0.05 18.20+/-1.08 0.03 +/- 0.01 966.35 +/- 82.28 0.58+/-0.16 2.52 +/- 0.05 3.04 +/- 0.26 1,407.40 +/- 97.10 2.61 +/- 0.57 1,498.60 +/- 113.90 2.01 +/- 0.59 1,294.30 +/- 118.70 1.47 +/- 0.42 5.49 +/- 0.69 1,613.80 +/- 218.50 4.21 +/- 0.24 2.20 +/- 0.48 1,453.80+/- 148.10 1,217.30 + 80.83 2.77 +/- 0.53 1,192.90 +/- 95.40 2.10+/-0.48 17.51 +/- 3.06 2.12+/- 0.47 4.25+/-1.18 1,340.10+/-111.10 1,408.10 +/- 102.70 1,416.40 +/- 192.30 1.27 +/-_
0.21 0.08 +/- 0.02 0.08 +/- 0.01 0.06 +/- 0.01 2.89 +/- 0.60 8.21 +/- 0.65 0.61 +/- 0.26 3.15+/-0.58 0.32 + 0.04 17.55 +/- 0.82 0.05 +/- 0.02 986.31 +/-91.91 0.81 +/-0.17 2.49 +/- 0.05 3.12 +/-0.37 1,442.20+189.60 2.79 +/- 0.54 1,375.50+/- 129.60 2.36 +/- 0.63 1,417.30 +/-176.50 1.23 +/- 0.41 5.80 +/- 0.69 1,532.70 +135.80 4.29 +/- 0.64 2.12+/-0.42 1,285.30 +/-190.50 1,218.30+/-99.13 3.60 +/- 0.59 1,388.90 +132.70 1.72 +/- 0.47 20.36 +/- 3.31 2.47 +/- 0.34 4.13++/-1.12 1,290.80+/-116.50 1,396.90 +/- 114.30 1,318.00+/-155.50 1.25 +/- 0.25 0.07 +/- 0.01 0.08 +/- 0.01 0.06 +/- 0.01 2.92 +/- 0.46 8.50 +/- 0.48 0.70 +/- 0.20 3.11 +/- 0.43 0.31 +/- 0.03 17.88 +/-0.68 0.04 +/- 0.01 976.33 +/- 61.68 0.70+/- 0.12 2.51 +/- 0.03 3.08 +/- 0.23 1,424.80 +/- 106.51 2.70 +/- 0.39 1,437.05 +/- 86.27 2.19+/-0.43 1,355.80 +/-106.35 1.35 +/- 0.29 5.64 +/-0.49 1,573.25 +/- 128.63 4.25 +/- 0.34 2.16+/- 0.32 1,369.55+/-120.65 1,217.80 +/- 63.95 3.19 +/-0.39 1,290.90 +/- 81.72 1.91 +/- 0.34 18.93+/- 2.25 2.30 +/- 0.29 4.19 +/-0.81 1,315.45 +80.49 1,402.50 +/- 76.83 1,367.20 +/- 123.65 1.26+/-0.16 A5-4 ResUlL M'fc*sult rKsUlL
Table A-5.
In-house "duplicate" samples.
Concentration in pCi/La Lab Sample First Second Averaged fln +,.,
G-7960, 7961 F-8011, 8012 F-8011, 8012 F-8011, 8012 MI-8149, 8150 MI-8343,8344 VE-8319, 8320 VE-8319, 8320 AP-9069,9070 AP-9566,9567 VE-8700, 8701 VE-8700, 8701 VE-8700, 8701 AP-9048, 9049 DW-8636, 8637 DW-8615, 8616 AP-9090, 9091 AP-9166, 9167 AP-9187, 9188 VE-10562,10563 VE-10562,10563 WW-8636, 8637 DW-8894, 8895 MI-9232, 9233 VE-9518, 9519 WW-10257,10258 VE-10333,10334 VE-10333,10334 MI-10588,10589 DW-10688,10689 WW-10905,10906 SS-10953,10954 SS-10953,10954 SS-10953, 10954 SS-10953,10954 SS-10953,10954 Result Result Result Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Oct, 2001 Oct, 2001 Oct, 2001 Oct, 2001 Oct, 2001 Oct, 2001 Oct, 2001 Oct, 2001 Oct, 2001 Oct, 2001 Oct, 2001 Oct, 2001 Oct, 2001 Oct, 2001 Oct, 2001 Nov, 2001 Nov, 2001 Nov, 2001 Nov, 2001 Nov, 2001 Dec, 2001 Dec, 2001 Dec, 2001 Dec, 2001 Dec, 2001 Dec, 2001 Coaes VU Analysis K-40 Cs-1 37 Gr. Beta K-40 K-40 K-40 Gr. Beta K-40 Be-7 Be-7 Be-7 K-40 Sr-90 Be-7 Gr. Beta Gr. Beta Be-7 Be-7 Be-7 Be-7 K-40 Gr. Beta G.r. Beta K-40 K-40 H-3 Be-7 K-40 K-40 Gr. Beta H-3 Ac-228 Bi-214 Co-58 Co-60 Cs-1 37 5.21 +/- 0.57 0.06 +/- 0.02 3.68+/-0.12 3.47 +/- 0.49 1,551.70+/-118.00 1,550.30+/- 170.60 3.37+/- 0.10 2.14 +/- 0.46 0.07 +/- 0.02 0.08 +/- 0.02 0.24+/- 0.10 2.03 +/- 0.24 0.01 +/- 0.00 0.07 +/- 0.01 4.74+/- 1.06 4.65 +/- 0.58 0.07 +/- 0.01 0.08 +/- 0.02 0.07 +/- 0.01 309.90 +/-158.80 6,407.10+/- 620.70 5.08+/-1.20 4.28 +/- 0.89 1,440.70 +/- 46.60 1.91 +/- 0.22 755.90+/- 102.50 0.68 +/- 0.26 6.10+/- 0.72 1,428.40 +/- 114.70 3.49 +/- 0.91 233.90 +/- 90.60 1.10+/-0.25 0.69 +/- 0.08 0.21 +/- 0.05 0.93 +/- 0.06 0.13+/- 0.03 5.70 +/- 0.63 0.04 +/- 0.02 3.50 +/-0.11 3.38 +/- 0.47 1,489.90 +/- 123.60 1,368.10+/-126.70 3.42 +/- 0.11 2.24 +/- 0.37 0.07 +/- 0.01 0.09 +/- 0.03 0.19+/- 0.10 2.03 +/- 0.21 0.01 +/- 0.00 0.07 +/- 0.00 5.08 +/-1.21 4.28 +/- 0.54 0.07 +/- 0.01 0.08 +/- 0.02 0.05 +/- 0.01 348.30+/- 168.10 6,057.50 +/- 660.40 4.74+/-1.06 3.40 +/- 0.90 1,424.80 +/- 76.40 1.97 +/- 0.39 684.70 +/- 99.90 0.99 +/- 0.26 5.83 +/- 0.72 1,445.50+/-129.40 2.36 +/- 0.76 226.30 +/- 90.20 0.91 +/- 0.16 0.75 +/- 0.08 0.18+/-0.04 0.94 +/- 0.06 0.16+/- 0.03 5.45 +/- 0.43 0.05 +/- 0.01 3.59 +/- 0.08 3.43 +/- 0.34 1,520.80 +/- 85.44 1,459.20+/-106.25 3.39 +/- 0.07 2.19 +/- 0.29 0.07 +/- 0.01 0.09 +/- 0.02 0.22 +/- 0.07 2.03 +/- 0.16 0.01 +/- 0.00 0.07 +/- 0.01 4.91 +/--0.80 4.47 +/- 0.40 0.07 +/- 0.01 0.08 +/- 0.01 0.06 +/- 0.01 329.10+/-115.62 6,232.30 +/- 453.15 4.91 +/- 0.80 3.84 +/- 0.63 1,432.75 +/- 44.75 1.94 +/- 0.22 720.30 +/- 71.57 0.84_+/-0.18 5.97 +/- 0.51 1,436.95 +/- 86.46 2.93 +/- 0.60 230.10 +/- 63.92 1.00+/-0.15 0.72 +/- 0.06 0.19+/- 0.03 0.93 +/- 0.04 0.14 +/- 0.02 I
A5-5 I
I 1
I
Table A-5.
In-house "duplicate" samples.
Concentration in pCi/L' Lab Sample First Second Averaged Codes Date Analysis Result Result Result SS-10953, 10954 Dec, 2001 K-40 9.91 +/-0.83 8.36+/-0.80 9.13+/-0.57 SS-10953, 10954 Dec, 2001 Pb-212 0.94+/-0.05 0.91 +/- 0.06 0.92 +/-0.04 SS-10953, 10954 Dec, 2001 Pb-214 0.83+/-0.08 0.82+/- 0.07 0.83 +/-0.05 SS-10953, 10954 Dec, 2001 Ra-226 1.76+/-0.37 1.67+/-0.37 1.72+/-0.26 SS-10953, 10954 Dec, 2001 TI-208 0.34+/-0.05 0.31 +/-0.05 0.32+/-0.04 MI-11033, 11034 Dec, 2001 K-40 1,339.80+/-128.70 1,435.80+/-117.30 1,387.80+/-87.07 MI-11033, 11034 Dec, 2001 Sr-90 1.31 +/-0.41 1.38+/-0.37 1.35+/-0.28 AP-11888, 11889 Dec, 2001 Be-7 0.06+/-_0.02 0.06+/-0.02 0.06+/-0.01 Duplicate analyses are performed on every twentieth sample received in-house.
Results are not listed for those analyses with activities that measure below the LLD.
" Results are reported in units of pCi/L, except for elemental potassium (K) in milk (mg/L), air filters (pCi/Filter), food products and vegetation (pCi/g), soil and sediments (pCi/kg).
A5-6
Table A-6.
Department of Energy's Mixed Analyte Performance Evaluation Program (MAPEP)a.
Concentrationb Lab Sample Date MAPEP Result' Control Code Type Collected Analysis Laboratory result' Is, N=1 Limits STSO-923 SOIL Jan, 2001 Am-241 0.0 - 2.6 Included in the testing series as a "false positive". No activity expected. Result of analysis; < 0.8 Bq/L.
STSO-923 SOIL Jan, 2001 Co-57 100.2+/-3.5 103.0+/- 10.3 72.1 -133.9 STSO-923 SOIL Jan, 2001 Co-60 1,285.1 +/- 5.3 1,270.0+/- 127.0 889.0 - 1,651.0 STSO-923 SOIL Jan, 2001 Cs-134 81.1 +/-1.8 91.1+/- 9.1 63.8-118.4 STSO-923 SOIL Jan, 2001 Cs-137 1,210.6+/-6.6 1,240.0+/- 124.0 868.0- 1,612.0 STSO-923 SOIL Jan, 2001 K-40 732.6 +/-21.2 652.0+/- 65.2 456.4 - 847.6 STSO-923 SOIL Jan, 2001 Mn-54 212.6+/-6.7 203.0+/- 20.3 142.1 - 263.9 STSO-923 SOIL Jan, 2001 Pu-238 110.7+/--7.2 115.0+/- 11.5 80.5-149.5 STSO-923 SOIL Jan, 2001 Pu-239/40 79.6 +/- 5.9 83.4+/- 8.3 58.4-108.4 STSO-923 SOIL Jan, 2001 Sr-90 159.8+/- 9.5 209.0+/- 20.9 146.3 - 271.7 STSO-923 SOIL Jan, 2001 U-233/4 45.0+/- 3.9 60.0+/- 6.0 42.0-78.0 STSO-923 SOIL Jan, 2001 U-238 165.6+/- 7.4 191.0+/- 19.1 133.7 - 248.3 STSO-923 SOIL Jan,.2001 Zn-65 428.5+/-10.9 382.0+/- 38.2 267.4 - 496.6 a
Results obtained by Environmental, Inc., Midwest Laboratory as a participant in the Department of Energy's Mixed Analyte Performance Evaluation Program, Idaho Operations office, Idaho Falls, Idaho.
'All results are in Bq/kg or Bq/L as requested by the Department of Energy.
' MAPEP results are presented as the known values and expected laboratory precision (1 sigma, 1 and control limits as defined by the MAPEP.
determination)
A6-1 J
I L
.1
Table A-7.
Environmental Measurements Laboratory Quality Assessment Program (EML)a.
Concentration b Lab Sample Date Control Code Type Collected Analysis Laboratory result EML Resultc Limits' STSO-904 SOIL STSO-904 SOIL STSO-904 SOIL Naturally-occurring radium of the higher bias seen for Mar, 2001 Ac-228 45.60+/-4.0 42.70 Mar, 2001 Am-241 14.40+/- 0.5 14.80 Mar, 2001 Bi-212 53.20 +/- 3.1 42.00 and thorium daughters are present in the shield background, and isotopes of lead and bismuth.
0.80- 1.50 0.63 - 2.64 0.45-1.23 a probable cause STSO-904 STSO-904 STSO-904 STSO-904 STSO-904 STSO-904 STSO-904 STW-905 STW-905 STW-905 STW-905 STW-905 STW-905 STW-905 STW-905 STW-905 STW-906 STW-906 STAP-907 STAP-907 STAP-907 STAP-907 STAP-907 STAP-907 STAP-907 SOIL SOIL SOIL SOIL SOIL SOIL SOIL WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER AIR FILTER AIR FILTER AIR FILTER AIR FILTER AIR FILTER AIR FILTER AIR FILTER Mar, 2001 Bi-214 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Cs-137 K-40 Pb-212 Pb-214 Pu-239/40 Sr-90 Am-241 Co-60 Cs-137 H-3 Pu-238 Pu-239/40 Sr-90 U-233/4 U-238 Gr. Alpha Gr. Beta Am-241 Co-60 Cs-134 Cs-1 37 Mn-54 Pu-238 Pu-239/40 42.10+/-7.7 1,772.60 +/- 79.8 583.80 +/- 52.6 46.60 +/- 8.5 45.30 +/- 8.6 26.00 +/- 0.8 55.60 +/- 2.2 2.15+/- 0.1 97.00 +/- 0.8 70.10+/--4.0 76.50 +/- 5.5 1.69 +/- 0.1 1.69 +/- 0.1 3.85 +/- 0.1 0.90 +/- 0.1 0.88 +/- 0.1 1,724.60+/-141.7 1,246.40 +/- 31.1 0.47 +/- 0.0 20.11 +/--0.2 2.71 +/- 0.2 9.86 +/- 0.2 7.25 +/- 0.2 0.23 +/- 0.0 0.12 +/-0.0 32.60 0.78-1.50 1,740.00 468.00 41.50 34.30 25.60 69.00 1.67 98.20 73.00 79.30 1.58 1.64 4.40 1.04 1.04 1,900.00 1,297.00 0.49 19.44 2.83 8.76 6.52 0.22 0.14 0.80-1.29 0.80- 1.37 0.74-1.36 0.76-1.53 0.71 -1.33 0.61 - 3.91 0.76-1.48 0.80- 1.20 0.80- 1.20 0.74 - 2.29 0.74-1.22 0.75-1.26 0.64-1.50 0.80-1.40 0.80-1.29 0.58-1.26 0.56-1.50 0.69 - 2.40 0.79-1.30 0.74-1.21 0.78-1.35 0.80 - 1.36 0.66-1.35 0.69-1.29 A7-1
Table A-7.
Environmental Measurements Laboratory Quality Assessment Program (EML)a.
Concentration b Lab Sample Date Control Code Type Collected Analysis STAP-907 STAP-907 STAP-907 STAP-908 STAP-908 STVE-909 STVE-909 STVE-909 STVE-909 STVE-909 STVE-909 STVE-909 STW-925 STW-925 STW-925 STW-925 STW-925 STW-925 STW-925 STW-925 STW-925 STW-926 STW-926 STSO-927 STSO-927 STSO-927 STSO-927 STSO-927 STSO-927 AIR FILTER AIR FILTER AIR FILTER AIR FILTER AIR FILTER VEGETATION VEGETATION VEGETATION VEGETATION VEGETATION VEGETATION VEGETATION WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER SOIL SOIL SOIL SOIL SOIL SOIL Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Mar, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sep, 2001 Sr-90 U-233/4 U-238 Gr. Alpha Gr. Beta Am-241 Cm-244 Co-60 Cs-1 37 K-40 Pu-239/40 Sr-90 Am-241 Co-60 Cs-1 37 H-3 Ni-63 Pu-238.
Pu-239/40 Sr-90 Uranium Gr. Alpha Gr. Beta Ac-228 Am-241 Bi-212 Bi-214 Cs-137 K-40 EML Resultc Limitsd Laboratory result 7.41+/- 0.2 0.05 +/- 0.0 0.05 +/- 0.0 2.66 +/- 0.0 2.30 +/- 0.0 6.10+/-0.2 3.50 +/- 0.5 28.50+/-2.1 795.50+/- 76.4 592.60 +/- 42.5 8.50 +/- 0.6 1,239.60 +/- 130.0 0.70+/-0.1 206.70 +/- 4.7 46.60 +/- 0.8 254.10+/-3.6 50.90 +/- 3.0 1.10+/-0.1 1.60+/-_0.1 4.10+/- 0.3 2.20 +/- 0.2 1,220.00 +/- 32.0 8,461.00 +/- 206.0 68.10+/-1.4 5.20 +/- 1.3 65.10+/-1.6 47.30 +/- 4.7 659.20+/-10.8 737.70 +/-16.6 U
U 7.10 0.05 0.05 3.97 2.58 6.17 3.69 30.40 842.00 603.00 9.58 1,330.00 0.76 209.00 45.13 207.00 45.25 1.09 1.63 3.73 2.37 1,150.00 7,970.00 59.57 4.43 62.07 36.90 612.33 623.33 0.55 - 2.05 0.80- 1.92 0.80- 1.59 0.57-1.47 0.76-1.52 0.72 - 2.34 0.61 - 1.61 0.75-1.51 0.80- 1.37 0.78-1.43 0.67-1.49 0.52-1.23 0.76-1.48 0.80- 1.20 0.80- 1.24 0.74 - 2.29 0.70- 1.30 0.74-1.22 0.75-1.26 0.64-1.50 0.73-1.37 0.58-1.26 0.56-1.50 0.80- 1.50 0.63 - 2.64 0.45-1.23 0.78-1.50 0.80-1.29 0.80-1.37 I
I A7-2 I
I
Table A-7.
Environmental Measurements Laboratory Quality Assessment Program (EML)a.
Concentration Lab Sample Date Control Code Type Collected Analysis Laboratory result EML Result' Limitsd STSO-927 SOIL Sep, 2001 Pb-212 64.70+/-3.8 58.33 0.74-1.36 STSO-927 SOIL Sep, 2001 Pb-214 53.70 +/- 7.7 39.67 0.76-1.53 STSO-927 SOIL Sep, 2001 Pu-239/40 9.30 +/-2.9 8.95 0.71 - 1.33 STSO-927 SOIL Sep, 2001 Sr-90 27.40-+/- 6.3 30.60 0.61 -3.91 STSO-927 SOIL Sep, 2001 Uranium 155.60+/- 7.8 194.23 0.62-1.35 STVE-928 VEGETATION Sep, 2001 Am-241 7.00+/- 0.3 6.92 0.72 -2.34 STVE-928 VEGETATION Sep, 2001 Cm-244 4.30+/- 0.8 4.31 0.61 - 1.61 STVE-928 VEGETATION Sep, 2001 Co-60 40.20 +/- 0.9 35.30 0.75 - 1.51 STVE-928 VEGETATION Sep, 2001 Cs-137 1,184.00_+/-2.8 1,030.00 0.80 - 1.37 STVE-928 VEGETATION Sep, 2001 K-40 1,023.00 +/-44.1 898.67 0.78-1.43 STVE-928 VEGETATION Sep, 2001 Pu-239/40 8.90+/-1.4 11.02 0.67 - 1.49 STVE-928 VEGETATION Sep, 2001 Sr-90 1,364.00+/- 18.4 1,612.80 0.52-1.23 STAP-929 AIR FILTER Sep, 2001 Am-241 0.09 +/- 30.0 0.09 0.69 - 2.40 STAP-929 AIR FILTER Sep, 2001 Co-60 16.90 +/- 0.3 17.50 0.79 - 1.30 STAP-929 AIR FILTER Sep, 2001 Cs-1 34 11.80 +/-0.2 12.95 0.74-1.21 STAP-929 AIR FILTER Sep, 2001 Cs-137 18.30_+/-0.3 17.10 0.78-1.35 STAP-929 AIR FILTER Sep, 2001 Mn-54 85.40+/-1.3 81.15 0.80-1.36 STAP-929 AIR FILTER Sep, 2001 Pu-238 0.05+/-0.0 0.07 0.66 - 1.35 STAP-929 AIR FILTER Sep, 2001 Pu-239/40 0.22+/- 0.0 0.23 0.69-1.29 STAP-929 AIR FILTER Sep, 2001 Sr-90 3.11 +/- 0.1 3.48 0.55 - 2.05 STAP-929 AIR FILTER Sep, 2001 Uranium 0.24+/-0.1 0.22 0.80 - 2.54 STAP-930 AIR FILTER Sep, 2001 Gr. Alpha 6.30 +/-0.1 5.36 0.57-1.47 STAP-930 AIR FILTER Sep, 2001 Gr. Beta 13.80+/-0.1 12.77 0.76-1.52 a The Environmental Measurements Laboratory provides the following nuclear species : Air Filters,
- Soil, Vegetation and Water.
' Results are reported in Bq/L with the following exceptions: Air Filter results are reported in Bq/Filter, Soil results are reported in Bq/Kg, Vegetation results are reported in Bq/Kg.
c The EML result listed is the mean of replicate determinations for each nuclide+/-the standard error of the mean.
'Control limits are reported by EML as the ratio of Reported Value ! EML value.
A7-3
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT L
_L APPENDIX B, 2001 REMP DATA
SUMMARY
REPORTS h
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Appendix B Page 42
Air Gamma Spectral Summary Report 2001 Radiological Enivironmental Monitoring Program Data Summary Perry Nuclear Power Plant, Lake County Ohio Docket no..: 50-440/50-441 Type and N
P timber of Lower Analyses Limit erfornied I
(LLD)
Be-7 N/A 28 Co-58 N/A 28 N
Co-60 iN/A Sample Type and Units Air pCihn3 Air pCihn3 Air pCi/m3 Air pCi/m3 Air Cs-137 pCi/rn3 28 Mean of Results from All Locations and Number Detected/Number Collected and Range 0.06 28 /28 0.05 - 0.08 Mean of Results from All Indicator Locations and Number Detected/Number Collected; and Range 0.06 24 / 24 0.05 - 0.08 Location with Highest Annual Mean:
Mean of Results from Location # and Mean and All Control Locations and Distance and Number Detected/Number Collected Number Detected/Number Collected Direction and Range and Range 1
3.40 ENE 0.06 4 /20 0.05
- 0.08 0.06 4/4 0.05 - 0.07 LLD LLD LLD LLD 0.04
!0.05 28 Cs-134 28
Air Gross Beta Summary Report 2001 Radiological Environmental Monitoring Program Data Summary Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Mean of Results from Mean of Results from All Locations and All Indicator Locations and Number Detected/Number Collected: Number Detected/Number Collected.
and Range and Range 0.02 364 I 364 0.01 - 0.06 0.02 312 / 312 0.01
- 0.06 Location with Highest Annual Mean:
Mean of Results from Location # and Mean and All Control Locations and Distance and Number Detected/Number Collected Number Detected/Number Collected Direction and Range and Range 5
0.60 SW 0.02 52 / 52 0.01
- 0.06 0.02 52 / 52 0.01 - 0.05 Sample Type and Units Air pCi/n3 Type and Number of Analyses Performed Gross Beta 364 Lower Limit (LLD)
.0.01
Air Iodine Summary Report 2001 Radiological Environmental Monitoring Program D~ata Summary Perry Nuclear Powver Plant, Lake County Ohio Docket no..: 50-440/50-441 Type and Number of Lower Analyses Limit Performed (LLD) 1-131 0.05 364 Mean of Results from Mean of Results from All Locations and All Indicator Locations and Number Detected/Number Collected 1 Numnber Detected/Number Collected and Range and Range LLD Location with Highest Annual Mean:
Mean of Results from Location # and Mean and All Control Locations and Distance and Number Detected/Number Collected Number Detected/Number Collected Direction and Range and Range Sample Type and Units Air pCi/m3
Fish Gamma Spectral Summary Report 2001 Radiological Environmental Monitoring Program Data Summary Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Type and Number of Lower Analyses Limit Performed (LLD)
Sample Type and Units Fish pCi/kg wet Fish pCi/kg wet Fish pCi/kg wet Fish pCi/kg wet Fish pCi/kg wet Fish pCi/kg wet Fish pCi/kg wet Fish pCi/kg wet 97.00 97.00 97.00 112.00 195.00 Co-58 28 Co-60 28 Cs-134 28 Cs-137 28 Fe-59 28 K-40 28 Mn-54 28 Zn-65 28 Mean of Results from All Locations and Number Detected/Number Collectedi and Range Mean of Results from All Indicator Locations and Number Detected/Number Collected and Range Location with Highest Annual Mean:
Location # and Mean and Distance and Number Detected/Number Collected Direction and Range Mean of Results from All Control Locations and Number Detected/Number Collected and Range LLD LLD LLD LLD LLD 1,615.38 28 / 28 796.52 - 2,219.20 97.00 1,671.33 14 /14 972.88 - 2,219.20 25 0.60 NNW 1,671.33 14 / 112 972.88 - 2,219.20 1,559.44 14 / 14 796.52 - 2,178.20 LLD LLD 195.00 N/A
Food Products Gamma Spectral Summary Report 2001 Radiological Environmental Monitoring Program Data Summary Perry Nuclear Power Plant, Lake County Ohio Docket no..: 50-440/50-441 Type and IN P
Sample Type and Units Food Products pCi/kg wet Food Products pCi/kg wet Food Products pCi/kg wet Food Products pCi/kg wet Food Products pCi/kg wet Food Products pCi/kg wet Food Products pCi/kg wet
'lumber of Lower Analyses Limit Perforaned (LLD)
Be-7 N/A 75 Co-58 IN/A 75 Co-60 N/A 75 Cs-134 75 45.00 Cs-137
'60.00 75 1-131 45.00 75 K-40
'N/A 75 Mean of Results from All Locations and Number Dctected/Number Collected and Range 533.19 23 / 75 145.90-1,016.60 Mean of Results from All Indicator Locations and Number Detected/Number Collected and Range 518.48 18 / 57 145.90 - 1,016.60 Location with Ilighest Annual Mean:
Location # and Mean and Distance and Number Detected/Number Collected Direction and Range 37 1.50 ENE 715.41 2 / 119 584.86
- 845.95 Mean of Results from All Control Locations and Number Detected/Number Collected and Range 586.14 5 /18 288.07 - 834.16 LLD LLD LLD LLD LLD 4,986.25 75 / 75 2,475.60 - 11,972.00 4,719.38 57 / 57 2,475.60 - 7,163.80 70 16.20 SSW 5,831.36 18 / 126 3,106.20
- 11,972.00 5,831.36 18 / 18 3,106.20 - 11,972.00
Milk Gamma Spectral Summary Report 2001 Radiological Environmental Monitoring Program Data Summary Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Mean of Results from All Locations and Number Detected/Number Collected and Range Mean of Results from All Indicator Locations and Number Detected/Number Collected and Range Location with IHighest Annual Mean:
Location # and Mean and Distance and Number Detected/Number Collected Direction and Range Mean of Results from All Control Locations and Number Detected/Number Collected and Range K-40 N/A 50 La-140 50 Ba-140 50 Cs-134 50 Cs-137 50 1,409.80 50 / 50 704.00-1,865.60 11.00 i45.00 1,454.37 32 / 32 1,134.80-1,865.60 61 7.40 SE 1,702.49 13 / 65 1,401.40
- 1,865.60 1,330.56 18 / 18 704.00-1,545.70 LLD LLD LLD LLD Milk pCi/L Milk pCi/L Milk pCi/L Milk pCi/L Milk pCi/L Sample Type and Units Type and Number of Analyses Performed Lower Limit (LLD) 11.00 13.00
I
(
I I
/I Milk Iodine Summary Report 2001 Radiological Environmental Monitoring Program Data Summary Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 ype and umber of Low*
Analyses Lim erformed (LL 1-131 0.75 50 ver nit D)
Mean of Results from All Locations and Number Detected/Number Collected I and Range Mean of Results from All Indicator Locations and Number Detected/Number Collected and Range Location with H lighest Annual Mean:
Location It and Mean and Distance and Number Detected/Number Collected Direction and Range Mean of Results from All Control Locations and Number Detected/Number Collected and Range LLD Sample Type and Units Milk pCi/L 1
N P
Pc
Sediment Gamma Spectral Summary Report 2001 Radiological Environmental Monitoring Program Data Summary Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Mean of Results from Mean of Results from Lower All Locations and All Indicator Locations and Limit Number Detected/Number Collected Number Detected/Number Collected (LLD) and Range and Range Location with Highest Annual Mean:
Mean of Results from Location # and Mean and All Control Locations and Distance and Number Detected/Number Collected Number Detected/Number Collected Direction and Range and Range Sample Type and Units Sediment pCi/kg dry Sediment pCi/kg dry Sediment pCi/kg dry Sediment pCi/kg dry Sediment pCi/kg dry Type and Number of Analyses Performed Co-58 14 Co-60 14 Cs-134 14 Cs-137 14 K-40 14 50.00 140.00 112.00 135.00 N/A 32 15.80 WSW 32 15.80 WSW 799.43 2/
10 210.75 -
1,388.10 20,260.00 2/
10 11,639.00
- 28,881.00 799.43 2/2 210.75-1,388.10 20,260.00 2/2 11,639.00 - 28,881.00 K-
-
-
K-611.91 5 /14 210.75-1,388.10 13,477.90 14 / 14 6,494.20 -
28,881.00 LLD LLD LLD 486.90 3/
12 292.05 -
775.19 12,347.55 12 / 12 6,494.20 - 23,983.00
t I
(
I I
I
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I I
I I
TLD Gamma Dose Summary Report 2001 Radiological Environmental Monitoring Program Data Summary Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Type and Units TLD TLD TLD Mean of Results fromr Mean of Results from Lower All Locations and All Indicator Locations and Limit Number Detected/Number Collected! Number Detected/Number Collected.
and Range Type and Number of Analyses Performed Direct 112 and Range 15.97 104 I 104 11.26 - 21.51 15.93 104 / 104 10.64 - 21.67 56.26 25 / 25 47.85 - 75.22 Location with Highest Annual Mean:
Location # and Mean and Distance and Number Detected/Number Collected Direction 29 4.30 SSE 33 4.50 S
36 3.90 WSW and Range 20.28 4/4 19.43
- 21.51 21.01 4/4 19.99
- 21.67 75.22 1/
1 75.22 - 75.22 Mean of Results from All Control Locations and Number Detected/Number Collected and Range 16.34 8/8 14.76-17.95 15.59 8/8 13.51 -
17.83 54.92 2/2 51.49 - 58.34 16.00 112 / 112 11.26 - 21.51 15.90 112 / 112 10.64 - 21.67 56.16 27 / 27 47.85 - 75.22 (LLD) 1.00 Direct 1.00 112 Direct 1.00 27
Water Gamma Spectral Summary Report 2001 Radiological Environmental Monitoring Program Data Summary Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sarnple Type and Units Water pCi/L Water pCi/L Water pCi/L Water pCi/L Water pCi/L Water pCi/L Type and Number of Analyses Performed Ba-140 56 Co-58 56 Co-60 56 Cs-134 56 Cs-137 56 Fe-59 56 La-140 11.00 56 Mn-54 56 Nb-95 56 Zn-65 56 Zr-95 56 11.00 11.00 22.00 22.00 Mean of R~esults from All Locations and Number Detected/Number Collected' and Range Mean of Results from All Indicator Locations and Number Detected/Number Collected and Range Location with 1ulighest Annual Mean:
Location # and Mean and Distance and Number Detected/Number Collected Direction and Range Mean of Results from All Control Locations and Number Detected/Number Collected and Range Lower Limit (LLD) 45.00 11.00 11.00 13.00 13.00 LLD LLD LLD LLD LLD LLD LLD LLD LLD LLD LLD Water pCi/L Water pCi/L Water pCi/L Water pCi/L Water pCi/L
{
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I I
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I I
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Water Gross Beta Summary Report 2001 Radiological Environmental Monitoring Program Data Summary Perry Nuclear Powver Plant, Lake County Ohio Docket no. : 50-440/50-441 Type and Number of Lower Analyses Limit Performed (LLD)
Gross Beta 3.00 56 Mean of Results from All Locations and Number Detected/Number Collected and Range 3.55 9/56 3.06 - 4.15 Mean of Results from All Indicator Locations and Number Detected/Number Collected and Range 3.67 6
44 3.21
- 4.15 Location with Highest Annual Mean:
Location 4 and Mean and Distance and Number Detected/Number Collected Direction and Range 60 1.00 WSW 3.85 4 /10 3.62 - 4.15 Mean of Results from All Control Locations and Number Detected/Number Collected and Range 3.32 3 /12 3.06 - 3.48 Sample Type and Units Water pCi/L
Water Tritium Summary Report 2001 Radiological Environmental Monitoring Program Data Summary Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Mean of Results from All Locations and Number Detected/Number Collected and Range Mean of Results from All Indicator Locations and Number Detected/Number Collected and Range Location with Highest Annual Mean:
Location # and Mean and Distance and Number Detected/Number Collected Direction and Range Mean of Results from All Control Locations and Number Detected/Number Collected and Range LLD Sample Type and Units Water pCi/L Type and Number of Analyses Performed
[1-3 20 Lower Limit (LLD) 1,500.00
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT APPENDIX C, 2001 REMP DETAILED DATA REPORTS Appendix C Page 43
Location 3
.3 3
3 3/27/01 7/3/01 10/3/01 Air Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Quarterly Results in pCi/n3 +/- 2 Sigma Be-7 Co-58 Co-60 Sample Type Air Air Air Air 0.059 +/- 0.009 0.067 +/- 0.012 0.064 +/- 0.012 Collection Date 3/27/01 7/3/01 10/3/01 1/2/02 3/27/01 7/3/01 10/3/01 1/2/02
< 0.000
< 0.000
< 0.000
< 0.000
< 0.000
- 0.000 0.059 +/- 0.012 0.079 +/- 0.011 0.073 +/- 0.010 0.048 +/- 0.009 0.050 +/- 0.010 0.071 +/-0.009 0.062 +/- 0.011 0.045 +/- 0.009 4
4 4
< 0.001
< 0.000
< 0.000
< 0.000
- 0.000
< 0.000
< 0.000
< 0.000 Air Air Air Air Air Air Air Cs-134
< 0.000
< 0.001
< 0.001
< 0.000
< 0.000
< 0.001
< 0.001
< 0.000 Cs-137
< 0.000
< 0.000
< 0.000
< 0.000
< 0.000
< 0.000
< 0.000
< 0.000
- 0.000
- 0.001
- 0.001
- 0.000
- 0.000
- 0.000
< 0.000
< 0.000
< 0.000
< 0.001
< 0.000
< 0.000
< 0.000
< 0.001
Air Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Quarterly Results in pCi/m3 +/- 2 Sigma Location Samnle Tvne Collection Date Be-7 Co-58 Co-60 4
Air 5
5 5
6 6
6 6
1/2/02 3/27/01 7/3/01 10/3/01 1/2/02 Air Air Air Air Air Air Air Air 7
Air 7
Air 3/27/01 7/3/01 10/3/01 1/2/02 3/27/01 7/3/01 0.049 +/- 0.009 0.052 +/- 0.010 0.062 +/- 0.009 0.058 +/- 0.010 0.064 +/- 0.010 0.054 +/- 0.011 0.070 +/- 0.010 0.054 +/- 0.011 0.049 +/- 0.008 0.060 +/- 0.011 0.064 +/- 0.012
< 0.000
< 0.000
< 0.000
< 0.000
< *0.000
< 0.001
!< 0.000
< 0.000
< 0.000
< 0.001
< 0.000
< 0.001
< 0.000
< 0.000
< 0.000
<* 0.001
< 0.001
< 0.000
< 0.000
- 0.001
< 0.000
< 0.000
{
I I
I Cs-134
< 0.000
< 0.000
< 0.000
< 0.000
< 01000
< 0.000
< 0.000
< 0.001
< 0.000
< 0.000
< 0.000 Cs-137
< 0.000
< 0.000
< 0.000
< 0.000
< 0.000
< 0.000
< 0.000
< 0.000
- 0.000
< 0.000
< 0.000
Location 7
7 35 35 35 35 Air Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Quarterly Results in pCi/m3 +/- 2 Sigma Be-7 Co-58 Co-60 0.057+/-0.010
< 0.000
< 0.000 0.048 +/- 0.010
< 0.000
< 0.001 Sample Type Air Air Air Air Air Air Collection Date 10/3/01 1/2/02 3/27/01 7/3/01 10/3/0 I 1/2/02
- 0.000
< 0.000
"< 0.000
< 0.001
-
---
0.055 +/- 0.011 0.064 +/- 0.010 0.065 +/- 0.013 0.045 +/- 0.006
< 0.000
< 0.000
< 0.001
< 0.000 Cs-134
< 0.000
< 0.000
< 0.000
< 0.001
< 0.001
< 0.000 Cs-137
< 0.000
< 0.000
< 0.000
< 0.000
< 0.000
- 0.000
Air Gross Beta Detail Report 2001 Radiological Environmental Monitoring Program Data Summary Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Weekly Results in pCi/m3 +/- 2 Sigma Loc Collection Date 1/10/01 1/17/01 1/24/01 1/31/01 2/7/01
.2/14/01
.2/21/01 2/28/01 3/7/01 3/14/01 3/21/01 3/27/01 4/4/01 4/11/01 4/18/01 Sample Type Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air 1
7 0.031 +/- 0.003 0.028 +/- 0,003 0.032 +/- 0.003 0.028 +/-.0.003 0.038 +/- 0.003 0.034 +/- 0.003 0.029 +/- 0.003 0.025 +/- 0.002 0.036 +/- 0.003 0.030 +/- 0.003 0.026 +/- 0.003 0.021 +/- 0.002 0.038 +/- 0.003 0.033 +/- 0.003 0.028 +/- 0.003 0.024 +/- 0.003 0.026 +/- 0.003 0.023 +/- 0.003 0.020 +/- 0.002 0.015 +/- 0.002 0.019 +/- 0.003 0.020 +/- 0.003 0.016 +/- 0.003 0.017 +/- 0.003 0.017 +/- 0.002 0.017 +/- 0.002 0.017 +/- 0.003 0.018 +/- 0.002 0.018 +/- 0.003 0.016 +/- 0.002 4
3 35 0.031 +/- 0.003 0.031 +/- 0.003 0.031 +/- 0.003 0.032 +/- 0,003 0.040 +U- 0.003 0.035 +/- 0.003 0.026 +/- 0.003 0.028 +/- 0.003 0.030 +/- 0.003 0.032 +/- 0.003 0.022 +/- 0.002 0.024 +/- 0.003 0,031 +/- 0.003 0.032 +/- 0.003 0.025 +/- 0.003 0.025 +/- 0.003 0.022 +/- 0.003 0.024 +/- 0.003 0.015 +/- 0.002 0.018 +/- 0.002 0.017 +/- 0.002 0.019 +/- 0.003 0.015 +/- 0.003 0.016 +/- 0.003 0.017 +/- 0.002 0.018 +/- 0.002 0.017 +/- 0.002 0.016 +/- 0.002 0.017 +/- 0.002 0.017 +/- 0.002 cation 5
6 0.030 +/- 0.003 0.029 +/- 0.003 0.036 +/- 0.003 0.028 +/- 0.003 0.031 +/-0.003 0.025 +/- 0.003 0.031 +/- 0.003 0,024 +/- 0.003 0.025 +/- 0.003 0.018 +/- 0.002 0.019 +/- 0.003 0.018 +/- 0.003 0.017 +/- 0.002 0.015 +/- 0.002 0.019 +/- 0.002 0.031 +/- 0.003 0.031 +/- 0.003 0.035 +/- 0.003 0.028 +/- 0.003 0.034 +/- 0.003 0.022 +/- 0.003 0.032 +/- 0.003 0.024 +/-0.003 0.023 +/- 0.003 0.016 +/- 0.002 0.019 +/- 0.003 0.017 +/-/- 0.003 0.017 +/- 0.002 0.017 +/- 0.003 0.016 +/- 0.002 0.028 +/- 0.003 0.031 +/- 0.003 0.033 +/- 0.003 0.027 +/- 0.003 0.031 +/- 0.003 0.022 +/- 0.003 0.029 +/- 0.003 0.026 +/- 0.003 0.025 +/- 0.003 0.016 +/- 0.002 0.018 +/- 0.003 0.017 +/- 0.003 0.017 +/- 0.002 0.018 +/- 0.003 0.018 +/- 0.002
Air Gross Beta Detail Report 2001 Radiological Environmental Monitoring Program Data Summary Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Weekly Results in pCi/m3 +/- 2 Sigma Location Collection Date 4/25/01 5/2/01 5/9/01 5/16/01 5/23/01 5/30/01 6/6/01 6/13/01 6/20/01 6/27/01 7/3/01 7/11/01 7/18/01 7/25/01 8/1/01 Sample Type Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air 1
7 0.022 +/- 0.003 0.020 +/- 0.002 0.027 +/- 0.003 0.025 +/- 0.003 0.022 +/- 0.003 0.021 +/- 0.003 0.020 +/- 0.003 0.019 +/- 0.003 0.016 +/- 0.003 0.013 +/- 0.003 0.012 +/- 0.002 0.010 +/- 0.002 0.010 +/-0.002 0.008 +/- 0.002 0.020 +/- 0.002 0.018 +/-0.002 0.023 +/- 0.003 0.021 +/- 0.002 0.017 +/- 0.002 0.015 +/- 0.002 0.025 +/- 0.003 0.021 +/- 0.003 0.019 +/- 0.002 0.018 +/- 0.002 0.017 +/- 0.003 0.015 +/- 0.003 0.028 +1- 0.003 0.031 +/- 0.003 0.016 +/- 0.003 0.014 +/- 0.003 3
35 0.023 +/- 0.003 0.024 +/- 0.003 0.025 +/- 0.003 0.025 +/- 0.003 0.023 +/- 0.003 0.025 +/- 0.003 0.022 +/- 0.003 0.020 +/- 0.003 0.016 +/- 0.003 0.014 +/- 0.003 06011 +/-0.002 0.012 +/- 0.002 0.009 +/- 0.002 0.010 +/- 0.002 0.019 +/- 0.002 0.021 +/- 0.002 0.024 +/- 0.003 0.023 +/- 0.003 0.016 +/- 0.002 0.015 +/- 0.002 0.022 +/- 0.003 0.022 +/- 0.003 0.019 +/- 0.002 0.018 +/- 0.002 0.018 +/- 0.003 0,018 +/- 0.003 0.033 +/- 0.003 0.031 +/- 0.003 0.015 +/- 0.003 0.015 +/- 0.003 4
5 0.022 +/- 0.002 0.021 +/- 0.003 0.024 +/- 0.003 0.020 +/- 0.003 0.017 +/- 0.003 0.011 +/-0.002 0.008 +/- 0.002 0.020 +/- 0.002 0.023 +/- 0.003 0.016 +/- 0.002 0,021 +/- 0.003 0.019 +/- 0.002 0,015 +/- 0.003 0.030 +/- 0.003 0.016 +/- 0.003 6
0.023 +/- 0.003 0.026 +/- 0.003 0.024 +/- 0.003 0.021 +/- 0.003 0.015 +/- 0.003 0.011 +/- 0.002 0.008 +/- 0.002 0.020 4-/- 0.002 0.021 +/- 0.002 0.016 +/- 0.002 0.020 +/- 0.003 0.019 +/- 0.002 0.018 +/- 0.003 0.033 +/- 0.003 0.015 +/- 0.003 0.020 +/- 0.003 0.024 +/- 0.003 0.019 +/- 0.003 0.022 +/- 0.003 0.015 +/- 0.003 0.012 +/- 0.002 0.009 +/- 0.002 0.020 +/- 0.002 0.025 +/- 0.003 0.016 +/- 0.002 0.022 +/- 0.003 0.018 +/- 0.002 0.017 +/- 0.003 0.033 +/- 0.003 0.015 +/- 0.003
-
Air Gross Beta Detail Report 2001 Radiological Environmental Monitoring Program Data Summary Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Weekly Results in pCi/m3 +/- 2 Sigma Location Collection Date 8/8/01 8/15/01 8/21/01 8/29/01 9/5/01 9/12/01 9/19/01 9/26/01 10/3/01 10/10/01 10/17/01 10/24/01 10/31/01 11/7/01 11/14/01 Sample Type Air Air Air Air Air Air Air Air 3
35 1
7 0.036 +/- 0.003 0.031 +/- 0.003 0.023 +/- 0.003 0.022 +/-/- 0.003 0.024 +/- 0.003 0.023 +/- 0.003 0,024 +/- 0,003 0.022 +/- 0.003 0.020 +/- 0.003 0.019 +/- 0.003 0.033 +/- 0.003 0.026 +/- 0.003 0.026 +/- 0.003 0,024 +/- 0,003 0,024 +/- 0.003 0.024 +/- 0.003 0.022 +/- 0.002 0.021 +/-0.002 0.026 +/- 0.003 0.026 +/- 0.003 0.017 +/- 0.002 0.016 +/- 0.002 0.027 +/- 0.003 0.029 +/- 0.003 0.015 +/- 0.002 0.018 +/- 0.003 0.022 +/- 0.003 0.022 +/- 0.003 0.021 +/- 0.003 0.024 +/- 0.003 Air Air Air Air Air Air Air 0.032 +/- 0.003 0.032 +/- 0.003 0.020 +/- 0.003 0.020. +Q- 0.003 0.025 +/- 0.003 0.026 +/- 0.003 0.026 +/- 0,003 0.024 +/- 0.003 0.020 +/- 0.003 0.020 +/- 0.003 0.030 +/- 0.003 0.020 +/- 0.007 0.025 +/- 0.003 0.027 +/- 0.004 0.025 +/- 0.003 0.024 +/- 0.003 0.021 +/- 0.002 0.022 +/- 0.002 0.026 +/- 0.002 0.027 +/- 0.003 0.016 +/- 0.002 0.018 +/- 0.002 0.027 +/- 0,003 0.026 +/- 0.003 0.016 +/- 0.002 0.017 +/- 0.003 0.023 +/- 0.003 0.021 +/-0.003 0.022 +/- 0.003 0.023 +/-/- 0.003 4
5 0.031 +/-0.003 0.023 +/- 0.003 0.026 +/- 0.003 0.027 +/- 0.003 0.019 +/- 0.003 0.029 +/- 0.003 0.026 +/- 0.003 0.025 +/- 0.003 0.022 +/- 0.003 0.025 +/- 0.003 0.016 +/- 0.002 0.027 +/- 0.003 0.017 +/- 0.003 0.023 +/- 0.003 0.024 +/- 0.003 6
0,033 +/- 0.003 0,033 +/- 0.003 0.025 +/- 0.003 0.023 +/- 0.003 0.023 +/- 0.003 0.023 +/- 0.003 0.026 +1- 0.003 0.030 +/- 0.003 0.019 +/- 0,003 0.028 +/- 0.003 0.024 +/- 0.003 0.024 +/- 0.003 0.020 +/- 0.002 0.044 +/- 0.006 0.017 A-/- 0.002 0.026 +/- 0.003 0.015 +/- 0.002 0.024 +/- 0.003 0.022 +/- 0.003 0.021 +/- 0.003 0.029 +/- 0.003 0.028 +/- 0.003 0.024 +/- 0.003 0.021 +/- 0.002 0,024 +/- 0.003 0.018 +/- 0.002 0.027 +/- 0.003 0.017 +/- 0.003 0.022 +/- 0.003 0.023 +/- 0.003
Air Gross Beta Detail Report 2001 Radiological Environmental Monitoring Program Data Summary Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Weekly Results in pCi/m3 +/- 2 Sigma Location Collection Date 11/21/01 11/28/01 12/5/01 12/12/01 12/19/01 12/26/01 1/2/02 Sample Type Air Air Air Air Air Air Air 1
7 3
35 0.048 +/- 0.004 0.048 +/- 0.003 0,046 +/- 0.004 0.048 4-/- 0.004 0.028 +/- 0.003 0.028 +/- 0.003 0.030 +/- 0.003 0.030 +/- 0.003 0.027 +1- 0.003 0.027 +/- 0.003 0.028 +/- 0.003 0.031 +/- 0.003 0.030 +/- 0.003 0.033 +/- 0.003 0.032 +/- 0.003 0.032 +/- 0.003 0.018 +/- 0.002 0.021 +/-/- 0.002 0.019 +/- 0.002 0.021 +/- 0.003 0.027 +/- 0.003 0.027 +/- 0.003 0.023 +/- 0.003 0.026 +/- 0.003
- 0.025 +/- 0.003 0.024 +/- 0.003 0.026 +/- 0.003 0.024 +/- 0.003 4
5 0.053 +/- 0.004 0.024 +/- 0.003 0.027 +/- 0.003 0.033 +/- 0.003 0.019 +/- 0.002 0;025 +/- 0.003 0.023 +/- 0.003 6
0.056 +/- 0.004 0.030 +/- 0.003 0.033 +/- 0.003 0.032 +/- 0.003 0.024 +/- 0.003 0.027 +/- 0.003 0.028 +/- 0.003 0.048 +/- 0.003 0.027 +/- 0.003 0.029 +/- 0.003 0.031 +/- 0.003 0.021 +/- 0.002 0:024 +/- 0.003 0.022 +/- 0.003
Air Iodine Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no.
50-440/50-441 Sample Frequency is: Weekly Results in pCi/m3 +/- 2 Sigma Location Sample Type Collection Dat 1-131 Air 1/10/01
< 0.007 Air 1/17/01
< 0.003 1
Air 1/24/01
< 0.004 Air 1/31/01
< 0.005 Air 2/7/01
< 0.005 Air 2/14/01
< 0.004 1
Air 2/21/01
< 0.005 1
Air 2/28/01
< 0.007 1
Air 3/7/01
< 0.007 1
Air 3/14/01
< 0.007 1
Air 3/21/01
< 0.005 1
Air 3/27/01
< 0.004 1
Air 4/4/01
< 0.004 I
Air 4/11/01
< 0.004 Air 4/18/01
< 0.007 1
Air 4/25/01
< 0.004 1
Air 5/2/0"1
< 0.004 I
Air 5/9/01
< 0.005 1
Air 5/16/01
< 0.006 1
Air 5/23/01
< 0.004 1
Air 5/30/01
< 0.004 1
Air 6/6/01
< 0.003 1
Air 6/13/01
< 0.005 1
Air 6/20/01
< 0.004 1
Air 6/27/01
< 0.005 Air 7/3/01
< 0.008 1
Air 7/11/01
< 0.003 1
Air 7/18/01
< 0.003 1
Air 7/25/01
< 0.004 Air 8/1/01
< 0.006 1
Air 8/8/01
< 0.007 Air 8/15/01
< 0.003 1
Air 8/21/01
< 0.005 1
Air 8/29/01
< 0.004 1
Air 9/5/01
< 0.003 1
Air 9/12/01
< 0.003 1
Air 9/19/01
< 0.003 1
Air 9/26/01
< 0.002 I
Air 10/3/01
< 0.005 I
Air 10/10/01
< 0.003 I
Air 10/17/01
< 0.004 1
Air 10/24/01
< 0.006
Air Iodine Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Weekly Results in pCi/m3 +/- 2 Sigma Collection Dat 10/31/01 11/7/01 11/14/01 11/21/01 11/28/01 12/5/01 12/12/01 12/19/01 12/26/01 1/2/02 Location 3
3 3
3 3
3
.3 3
3 3
3 3
3 3
3 3
3 3
3 3
3 3
3 3
3 3
3 3
3 3
3 3
Sample Type Air Air Air Air Air Air Air Air Air Air 1-131
- 0.005
- 0.003
- 0.004
- 0.010
- 0.003
- 0.006
- 0.005
- 0.006
- 0.007
- 0.005
- 0.006
- 0.003
- 0.003
- 0.005
- 0.004
- 0.003
- 0.004
- 0.006
- 0.007
- 0.006
- 0.005
- 0.004
- 0.004
- 0.004
- 0.006
- 0,003
- 0.004
- 0.005
- 0.006
- 0.004
- 0.004
- 0.003
- 0.005
- 0.004
- 0.005
- 0.008
- 0.003
- 0.003
- 0.004
- 0.006
- 0.007
- 0.003 1/10/01 1/17/01 1/24/01 1/31/01 2/7/01 2/14/01 2/21/01 2/28/01 3/7/01 3/14/01 3/21/01 3/27/01 4/4/01 4/11/01 4/18/01 4/25/01 5/2/01 5/9/01 5/16/01 5/23/01 5/30/01 6/6/01 6/13/01 6/20/01 6/27/01 7/3/01 7/11/01 7/18/01 7/25/01 8/1/01 8/8/01 8/15/01 Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air
- Air, Air Air Air Air Air Air Air Air
_J.
SAir' ioune Deaii Repotr.suOl Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Weekly Results in pCi/m3 +/- 2 Sigma Location Sample Type Collection Dat 1-131 3
Air 8/21/01
< 0.005 3
Air 8/29/01
< 0.004 3
Air 9/5/01
< 0.003 3
Air 9/12/01
< 0.003 3
Air 9/19/01
< 0.003 3
Air 9/26/01
< 0.002 3
Air 10/3/01
< 0.005 3
Air 10/10/01
< 0.003 3
Air 10/17/01
< 0.005 3
Air 10/24/01
< 0.006 3
Air 10/31/01
< 0.005 3
Air 11/7/01
< 0.004 3
Air 11/14/01
< 0.004 3
Air 11/21/01
< 0.010 3
Air.
11/28/01
< 0.003 3
Air 12/5/01
< 0.006 3
Air 12/12/01
< 0.005 3
Air 12/19/01
< 0.006 3
Air 12/26/01
< 0.006 3
Air 1/2/02
< 0.004 4
Air 1/10/01
< 0.006 4
Air 1/17/01
< 0.003 4
Air 1/24/01
< 0.003 4
Air 1/31/01
< 0.005 4
Air 2/7/01
< 0.004 4
Air 2/14/01
< 0.004 4
Air 2/21/01
< 0.004 4
Air 2/28/01
< 0.006 4
Air 3/7/01
< 0.007 4
Air 3/14/01
< 0.006 4
Air 3/21/01
< 0.005 4
Air 3/27/01
< 0.004 4
Air 4/4/01
< 0.004 4
Air 4/11/01
< 0.004 4
Air 4/18/01
< 0.006 4
Air 4/25/01
< 0.003 4
Air 5/2/01
< 0.004 4
Air 5/9/01
< 0.005 4
Air 5/16/01
< 0.006 4
Air 5/23/01
< 0.004 4
Air 5/30/01
< 0.004 4
Air 6/6/01
< 0.003
Air Iodine Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Weekly Results in pCi/m3 +/- 2 Sigma Location 4
4 4
4 4
4 4
4 4
4 4
4 4
4 4
4 4
4 4
4
.4 4
4 4
4 4
4 4
4 4
5 Air 5
Air 5
Air 5
Air 5
Air 5
Air 5
Air 5
Air 5
Air 5
Air 5
Air 5
Air Sample Type Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air 1/10/01 1/17/01 1/24/01 1/31/01 2/7/01 2/14/01 2/21/01 2/28/01 3/7/01 3/14/01 3/21/01 3/27/01 0.007 0.003 0.004 0.005 0.005 0.004 0.005 0.007 0.007 0.007 0.005 0.004 Collection Dat 6/13/01 6/20/01 6/27/01 7/3/01 7/11/01 7/18/01 7/25/01 8/I/01 8/8/01 8/15/01 8/21/01 8/29/01 9/5/01 9/12/01 9/19/01 9/26/01 10/3/01 10/10/01 10/17/01 10/24/01 10/31/01 11/7/01 11/14/01 11/21/01 11/28/01 12/5/01 12/12/01 12/19/01 12/26/01 1/2/02 1-131 0.005 0.004 0.005 0.008 0.003 0.003 0.004 0.006 0.007 0.003 0.005 0.004 0.003 0.003 0.004 0.002 0.005 0.004 0.005 0.007 0.005 0.004 0.005 0.011 0.003 0.007 0.005 0.006 0.006 0.004
I I
Location 5
5 5
5 5
5 5
5 5
5 5
5 5
5 5
5 5
5 5
5 5
5 5
5 5
5 5
5 5
5 5
5 5
5 5
5 5
5 5
5 1/10/01 1/17/01 Sample Type Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air
< 0.007
< 0.003 Air wusne Dutan Repr LIO1M Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Weekly Results in pCi/m3 +/- 2 Sigma I
I Collection Dat 4/4/01 4/11/01 4/18/01 4/25/01 5/2/01 5/9/01 5/16/01 5/23/01 5/30/01 6/6/01 6/13/01 6/20/01 6/27/01 7/3/01 7/11/01 7/18/01 7/25/01 8/1/01 8/8/01 8/15/01 8/21/01 8/29/01 9/5/01 9/12/01 9/1"9/0 I 9/26/01 10/3/01 10/10/01 10/17/01 10/24/01 10/31/01 11/7/01 11/14/01 11/21/01 11/28/01 12/5/01 12/12/01 12/19/01 12/26/01 1/2/02 1-131 0.004 0,004 0.006 0.003 0.004 0.004 0.006 0.004 0.004 0.003 0.005 0.004 0.005 0.008 0.003 0,003 0.004 0.006 0.007 0.003 0.005 0.004 0.003 0.003 0.004 0.002 0.005 0.009 0.005 0.006 0.005 0.004 0.005 0.011 0.003 0.007 0.005 0.007 0.007 0.005 6
6 Air Air
Air Iodine Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Weekly Results in pCi/m3 +/- 2 Sigma Location 6
6 6
6 6
6 6
6 6
6 6
6 6
6 6
6 6
6 6
6 6
6 6
6 6
6 6
6 6
6 6
6 6
6 6
6 6
6 6
6 6
6 6
1-131 Sample Type Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air r---
Collection Dat 1/24/01 1/31/01 2/7/01 2/14/01 2/21/01 2/28/01 3/7/01 3/14/01 3/21/01 3/27/01 4/4/01 4/11/01 4/18/01 4/25/01 5/2/01 5/9/01 5/16/01 5/23/01 5/30/01 6/6/01 6/13/01 6/20/01 6/27/01 7/3/01 7/11/01 7/18/01 7/25/01 8/l/01 8/8/01 8/15/01 8/21/01 8/29/01 9/5/01 9/12/01 9/19/01 9/26/01 10/3/01 10/10/01 10/17/01 10/24/01 10/31/01 11/7/01 11/14/01 0.004 0.005 0.005 0.004 0.005 0.007 0.007 0.007 0.005 0.004 0.004 0.004 0.006 0.004 0.004 0.005 0.006 0.004 0.004 0.003 0.005 0.005 0.005 0.008 0.003 0.003 0.004 0.006 0.007 0.003 0.005 0.004 0.003 0.003 0.003 0.002 0.005 0.004 0.005 0.006 0.005 0.004 0.005
I I
Location 6
6 6
6 6
6 6
7 7
7 7
7 7
7 7
7 7
7 7
7 7
7 7
7 7
7 7
7 7
7 7
7 7
7 7
7 7
7 7
7 7
7 Air Iodine Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Weekly Results in pCi/m3 +/- 2 Sigma Sample Type Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air 1-131 0.011 0.003 0.007 0.005 0.006 0.006 0.004 Collection Dat 11/21/01 11/28/01 12/5/01 12/12/01 12/19/01 12/26/01 1/2/02 1/10/01 1/17/01 1/24/01 1/31/01 2/7/01 2/14/01 2/21/01 2/28/01 3/7/01 3/14/01 3/21/01 3/27/01 4/4/01 4/11/01 4/18/01 4/25/01 5/2/01 5/9/01 5/16/01 5/23/01 5/30/01 6/6/01 6/13/01 6/20/01 6/27/01 7/3/01 7/11/01 7/18/01 7/25/01 8/1/01 8/8/01 8/15/01 8/21/01 8/29/01 9/5/01 0.007 0.003 0.003 0.005 0.005 0.004 0.004 0.007 0.007 0.007 0.005 0.004 0.004 0,004 0.006 0.003 0.004 0.005 0.006 0.004 0.004 0.003 0.005 0.004 0.005 0.008 0.003 0.003 0.004 0.006 0.007 0.003 0.005 0.004 0.003
Air Iodine Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Weekly Results in pCi/ln3 +/- 2 Sigma Location 7
7 7
7 7
7 7
7 7
7
'7 7
7 7
7 7
7 Sample Type Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air 1/10/01 1/17/01 1/24/01 1/31/01 2/7/01 2/14/01 2/21/01 2/28/01 3/7/01 3/14/01 3/21/01 3/27/01 4/4/01 4/11/01 4/18/01 4/25/01 5/2/01 5/9/01 5/16/01 5/23/01 5/30/01 6/6/01 6/13/01 6/20/01 6/27/01 Collection Dat 9/12/01 9/19/01 9/26/01 10/3/01 10/10/01 10/17/01 10/24/01 10/31/01 11/7/01 11/14/01 11/21/01 11/28/01 12/5/01 12/12/01 12/19/01 12/26/01 1/2/02
<K K
K K
K K
K K
K K
K K
K K
35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 1-131 0.003 0.003 0.002 0.005 0.004 0.005 0.007 0.005 0.004 0.005 0.011 0.003 0.007 0.005 0.006 0.007 0.005 0.002 0.003 0.002 0.001 0.002 0.001 0.003 0.004 0.003 0.002 0.003 0.003 0.003 0.006 0.003 0.004 0.002 0.003 0.003 0.003 0.002 0.002 0.002 0.004 0.004 H-
_6 1--
I I
Location 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 35 Sample Type Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air Air iodine Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Weekly Results in pCi/m3 +/- 2 Sigma Collection Dat 7/3/01 7/11/01 7/18/01 7/25/01 8/1/01 8/8/01 8/15/01 8/21/01 8/29/01 9/5/01 9/12/01 9/19/01 9/26/01 10/3/01 10/10/01 10/17/01 10/24/01 10/31/01 11/7/01 11/14/01 11/21/01 11/28/01 12/5/01 12/12/01 12/19/01 12/26/01 1/2/02 1-131 0.005 0.003 0.003 0.002 0.006 0.007 0.005 0.005 0.003 0.004 0.012 0.008 0.002 0.005 0.005 0.003 0.003 0.004 0.003 0.002 0.008 0.007 0.004 0.003 0.006 0.005 0.003
Location Sample Type 25 carp 25 channel catfish 25 freshwater drum 25 gizzard shad 25 redhorse sucker 25 sniallnouth bass 25 walleye 25 white bass 25 white perch 25 white sticker 25 coho salmon 25 redhorse sucker Fish Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Bi-Annually Results in pCi/kg wet +/- 2 Sigma Collection Date Co-58 Co-60 Cs-134 K-40 Mn-54 Zn-65 5/31/01
< 9.98
< 7.92
< 7.25 2,173.35 +/- 235.93
< 9.52
< 17.42 5/31/01
< 14.45
< 9.82 16.48 1,718.70+/- 376.20
< 15.82
< 40.47 5/31/01
< 10.94
< 14.12
< 15.43 1,424.00+/- 388.80
< 16.91
< 24.07 5/31/01
< 24.23
< 13.46 14.89 1,293.30+/-399.80
< 13.98
< 53.43 5/31/01
< 14.35 12.34
< 13.57 1,848.40+/-374.10 16.15
< 23.13 5/31/01 11.17
< 5.98
< 7.09 1,971.00+/-330.60
< 9.55 10.64 5/31/01 19.25
< 18.32 17.88 2,219.20+/-411.00
< 14.69
< 41.60 5/31/01
< 9.06
< 14.67 13.98 1,343.70 +/-293.40
< 10.79
< 21.54 5/31/01 12.68
< 12.58
< 19.36 1,387.80+/-330.40 19.20
< 30.87 5/31/01 10.29
< 13.59 15.18 972.88 +/- 320.40 15.94
< 9.56 10/9/01
< 29.33
< 27.31
< 26.98 1,389.20+/-441.30
< 15.71
< 29.41 10/9/01
< 18.88
< 9.02
< 9.52 2,102.70 +/-339.70
< 8.73
< 19.60 Cs-137
< 9.43 16.32 13.83
< 5.53 13.09 14.60
< 17.56 14.69 19.52 17.29
< 18.35
< 10.62 Fe-59 12.76
< 29.68
< 38.50
< 45.64
- 22.55
< 26.14
< 33.28
< 22.16
< 24.88
< 14.26 100.92
< 53.37
I'I I
I 11.50 1,504.80 +/- 239.50
< 8.78 1,494.60 +/- 282.50 17.41 1,476.50 +/- 308.50
< 7.04 1,782.80 +/- 373.90 11.59 1,568.50 +/- 336.90 14.15 1,221.60 +/- 378.50 18.08 1,903.10 +/- 373.00
< 16.67 1,452.80+/ 261.00
< 14.27 1,795.10 +/- 356.40
< 26.24 796.52 +/- 366.70 6.87 4.67 8.91 15.09 16.73 16.05 9.48 18.15 10.01 8.72 8.80 16.97 8.04 7.90 9.27 10.43 15.76 15.61 19.85 13.78 7.91 15.41 13.82 8.20 15.80 37.98 16.05 26.68 8.76 33.80 17.07 24.06 13.06 36.49 11.12 18.40 23.44 42.31 21.07 43.11 Fish Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Bi-Annually Results in pCi/kg wet +/- 2 Sigma Collection Date Co-58 Co-60 Cs-134 K-40 Mn-54 Zn-65 10/9/01
< 16.64
< 8.22
< 11.34 1,764.40 +/- 284.30
< 8.33
< 15.56 10/9/01
< 10.13
< 10.03
< 6.72 1,790.00 +/- 310.40
< 11.07
< 16.13
- 8.51 10.42 16.05 17.05
< 8.34
- 23.02
< 6.55
< 10.68 16.35 19.38 Cs-137
< 11.96
< 11.48 Location 25 25 Sample Type steelhead walleye Fe-59
< 36.19 16.07 freshwater drum redhorse sucker smallniouth bass walleye white bass white perch white sucker channel catfish coho salmon gizzard shad 5/31/01 5/31/01 5/31/01 5/31/01 5/31/01 5/31/01 5/31/01 10/9/01 10/9/01 10/9/01
< 23.75
< 30.15
< 20.80 13.53
< 32.17
< 41.21
< 28.05
< 33.72
< 71.88
< 30.64
Fish Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Bi-Annually Results in pCi/kg wet +/- 2 Sigma Location Sample Type 32 redhorse sticker 32 small mouith bass 32 steelhead 32 white sucker Collection Date 10/9/01 10/9/01 10/9/01 10/9/01 Co-58 K-40
< 15.79 1,669.20 +/- 344.20
< 20.12 1,097.90 +/- 383.40
< 13.22 2,178.20 +/- 362.80 14.59 1,890.50 +/-270.20
- ~-
~
/,
- 8.01
< 20.02 15.51 13.99
< 15.46
< 13.91
< 11.06
< 7.92 Cs-134 Zn-65 17.33
< 35.87 17.13
< 47.47 18.54
< 29.30 14.26
< 21.21 Cs-137 16.30
< 22.30 19.48
< 9.98 Fe-59
< 36.51
< 32.05
< 57.68
< 60.71
I
'I I
I Location Sample Type 2
swiss chard 2
turnip greens 2
kale 2
swiss chard 2
beet greens 2
kale 2
swiss chard 2
beet greens 2
kale 2
swiss chard 2
kale 2
swiss chard 1V I
I Il Food Products Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Monthly Results in pCi/kg wet +/- 2 Sigma Collection Date Be-7 Co-58 Co-60 1-131 K-40 7/16/01
< 126.27
< 7.14
< 9.82
< 13.32 5,979.30 +/- 452.90 7/16/01
< 128.63
< 12.09
< 8.05
< 9.28 3,741.50 +/- 462.90 8/13/01
< 112.08
< 8.61
< 10.67
< 18.29 3,945.10 +/- 363.00 8/13/01
< 191.25
< 21.19
< 16.99
< 25.79 3,646.50 +/- 552.10 9/10/01
< 166.74
< 13.72
< 11.94
< 19.84 5,024.30 +/- 604.20 9/10/01
< 115.40
< 8.79
< 9.90
< 14.96 4,210.80 +/-366.80 9/10/01
< 96.44
< 5.94
< 5.48
< 13.74 4,726.20 +/-319.50 10/4/01 412.36+/- 100.71
< 9.50
< 8.03
< 16.59 6,310.45 +/-312.15 10/4/01
< 141.52
< 9.22
< 10.42
< 16.14 4,607.10 +/-399.20 10/4/01
< 171.57
< 9.02
< 19.80
< 19.34 4,526.10 +/- 525.00 11/12/01
< 270.41
< 20.82
< 17.31
< 25.36 4,994.70 +/- 640.40 11/12/01
< 199.10
< 19.12
< 16.80
< 26.26 5,517.60 +/- 612.40 Cs-134 Cs-137 15.42
< 9.78 13.89
< 10.54
< 7.79
< 11.00
< 21.50
< 21.36 10.39 11.36
< 11.45
< 11.89
< 12.00
< 9.66
< 7.74
< 11.48
< 10.97
< 11.15
< 23.69 19.16 15.97
< 25.13
< 24.30
< 21.06
Location 16 16 16 16 16 16 16 16 16 16 16 16 1/2 -- -H---
V -
Sample Type chinese cabbage swiss chard turnip greens chinese cabbage swiss chard turnip greens chinese cabbage swiss chard turnip greens swiss chard turnip greens swiss chard Food Products Gamma Spectral Detail Report 2001 Radiological Environmental Monit,-iig Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Monthly Results in pCi/kg wet +/- 2 Sigma Collection Date Be-7 Co-58 Co-60 1-131 K-40 7/16/01
< 158.26
< 13.07
< 19.15
< 18.29 6,059.80 +/-631.30 7/16/01 140.80
< 10.91
< 12.29 13.15 2,805.90 +-347.80 7/16/01 142.44
< 10.85
< 13.49
< 20.35 6,510.80+/- 599.70 8/13/01 250.77+/- 145.60
< 22.08
< 23.45
< 15.57 4,566.20+/- 576.40 8/13/01 385.43+/-.183.40
< 24.79
< 13.02
< 14.82 6,912.80+/- 736.10 8/13/01 327.44 +/- 154.00
<.19.85
< 18.90
< 27.38 5,005.30 +/- 583.00 9/10/01 479.93+/-248.00
< 15.66
< 13.55
< 27.18 4,834.40 +/- 677.20 9/10/01
< 177.91
< 12.56
< 10.41
< 20.02 6,724.10 +/- 591.90 9/10/01 325.23 +/- 144.50
< 22.68 17.30
< 24.08 6,480.40 +/- 643.90 10/4/01
< 151.35
< 9.07 16.42 15.52 4,897.40 +/-497.90 10/4/01 904.68+/- 136.00
< 4.94
< 8.30 17.11 6,756.70 +/-424.20 11/12/01 389.90 +/- 219.90
< 19.05
< 28.82
< 30.93 7,163.80 +/- 705.60 Cs-134 16.67 16.87
< 22.85
< 12.27
< 24.77 15.14
< 20.35
< 22.40
< 15.58 14.56
< 8.13 19.39 Cs-137
< 21.51 16.61 14.41
< 9.90 19.44
< 24.69
< 23.00
< 21.66
< 18.74
< 13.88
< 11.01
< 17.52
-1 jr-
I I
Location Sample Type 16 turnip greens chinese cabbage swiss chard turnip greens chinese cabbage swiss chard turnip greens chinese cabbage swiss chard turnip greens chinese cabbage swiss chard Collection Date 11/12/01 7/16/01 7/16/01 7/16/01 8/13/01 8/13/01 8/13/01 9/10/01 9/10/01 9/10/01 10/4/0 I 10/4/01 Food Products Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Monthly Results in pCi/kg wet +/- 2 Sigma
~~~~~~~~~~~~~.
Be-7 Co-58 Co-60 1-131 K-40 772.41 +/-314.10
< 27.39
< 14.20
< 36.04 4,929.30 +/- 708.90 185.00
< 20.15
< 14.29
< 20.63 3,560.20 +/- 446.20 147.75
< 13.43
< 14.90 19.24 3,878.10 +/-376.70 175.87
< 9.57
< 10.28 19.91 4,747.80 +/- 547.80
< 96.45
< 5.47
< 5.81 10.61 3,261.10+/-262.10 188.89
< 14.50
< 8.98
< 26.18 3,866.10 +/-486.30 311.55+/-174.70
< 10.37
< 11.91
< 30.65 4,092.60 +/-481.70
< 139.10
< 8.16
< 9.32
< 16.97 2,475.60 +/-321.10
< 177.57
< 15.37
< 21.53
< 23.66 4,552.30 +/- 544.20 519.00+/-36.14
< 3.48
< 4.07
- 5.62 5,830.90+/- 119.30
< 152.79
< 13.34
< 10.62
< 31.80 4,146.30+/-493.60 145.90 +/- 84.76
< 7.28
< 10.30
< 9.12 3,207.10+/-272.80 Cs-134
< 25.52 Cs-137
< 22.57 22.10 11.73 24.37 8.84 18.74 16.82 15.22 13.02 3.92 19.87 9.34
< 22.58 18.79 18.32 LLD 18.64
< 23.63 18.12
< 19.34 LLD 19.19
< 8.86 I
I I
i I
Location Sample Type Collection Date 20 turnip greens 10/4/01 20 chinese cabbage 11/12/01 20 swiss chard 11/12/01 20 turnip greens 11/12/01 Food Products Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. " 50-440/50-441 Sample Frequency is: Monthly Results in pCi/kg wet +/- 2 Sigma Bc-7 Co-58 Co-60 1-131 K-40 1,016.60+/-277.10
< 17.10
< 18.11
< 22.81 6,102.00 +/- 734.90 431.83+/-200.40
< 19.16 13.71 19.37 4,806.00+/- 603.30 396.05 +/- 174.3o 14.63
< 22.62
< 26.48 4,572.60 +/- 549.00 832.73 +/- 184.04
< 20.57
< 13.63
< 21.02 5,963.75 +/- 507.31 37 chinese cabbage 37 swiss chard 37 turnip greens 37 chinese cabbage 37 swiss chard 37 turnip greens 37 swiss chard 37 turnip greens 6/25/01
< 137.77
< 17.59 6/25/01
< 134.54 14.52 6/25/01
< 93.87
< 12.03 7/16/01
< 181.41
< 26.75 7/16/01 152.17 19.69 7/16/01 183.36 11.18 8/13/01 144.77
< 19.52 8/13/01
< 138.99
< 11.90
< 11.36 5,178.30 +/- 416.40 15.92 6,966.30 +/- 444.30
< 5.70 5,268.30 +/- 340.70 15.55 4,084.00 +/- 513.40
< 13.42 4,553.10 +/- 489.40
< 9.67 4,809.50 +/- 537.20 10.74 3,411.30 +/- 503.30
< 8.81 3,935.20 +/- 459.50 Cs-134
- 24.74
- 20.65 19.72 18.53 Cs-137
< 21.10
< 23.83
< 24.50
< 22.04
- 12.62 K 13.45
- 9.54 15.89 18.19
- 12.61
- 17.57 16.35
- 9.16
- 10.50
- 8.54
- 22.68
- 15.42
- 15.06
- 16.69
- 13.39
- 10.61
- 11.33
- 8.14
- 25.23
- 20.38
- 17.80
- 15.76
- 15.89
Food Products Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Monthly Results in pCi/kg wet +/- 2 Sigma Location Sample Type Collection Date Be-7 Co-58 Co-60 1-131 K-40 37 chinese cabbage 9/10/01
< 132.88
< 14.88
< 7.92
< 18.33 3,240.10+/-401.30 37 swiss chard 9/10/01
< 149.37
< 11.98 13.71
< 23.69 4,758.60 +1-409.20 37 turnip greens 9/10/01
< 156.47
< 10.73 10.50
< 19.19 3,763.60+/-466.10 37 chinese cabbage 10/4/01
< 137.45
< 12.60 16.34
< 12.11 2,624.60+/-461.60 37 swiss chard 10/4/01
< 121.84
< 14.74 16.25
< 17.82 3,312.50 +/- 425.10 37 turnip greens 10/4/01 584.86 +/- 192.10
< 18.93 14.91
< 26.45 5,785.90 +/- 536.90 37 chinese cabbage 11/12/01
< 131.80
< 9.32
< 8.35
< 21.54 2,481.30 +/- 353.20 37 swiss chard 11/12/01
< 150.76
< 11.11
< 12.12
< 9.48 3,932.10 +/- 465.70 37 turnip greens 11/12/01 845.95 +/- 166.30
< 6.47
< 9.01
< 19.83 4,960.90 +/- 436.30 70 chinese cabbage 6/25/01
< 134.25
< 13.95
< 11.70
< 16.74 4,381.90 +/-460.80 70 swiss chard 6/25/01
< 127.97
< 13.27
< 11.41
< 17.27 4,758.60 +/-468.60 70 turnip greens 6/25/01
< 192,65
< 11,44
< 17.88
< 26.54 4,632.70 +/- 542.40 I
I I
I Cs-134
- 17.93
< 7.09 18.42 15.87
< 15.81
< 17.66
< 14.68 16.65 12.63 Cs-137
< 10.08 10.47
< 18.26
- 20.02
< 14.66
< 17.89
< 15.17 16.78 18.51 15.83 15.31 14.11 10.87 19.71 20.78
Location Sample Type 70 chinese cabbage 70 swiss chard 70 turnip greens 70 chinese cabbage 70 swiss chard 70 turnip greens 70 chinese cabbage 70 swiss chard 70 turnip greens 70 chinese cabbage 70 swiss chard 70 turnip greens Collection Date 7/16/01 7/16/01 7/16/01 8/13/01 8/13/01 8/13/01 9/10/01 9/10/01 9/10/01 10/4/0 I 10/4/01 10/4/01 Food Products Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Monthly Results in pCi/kg wet +/- 2 Sigma Be-7 Co-58 Co-60 1-131 K-40
< 75.74
< 3.92
< 4.99 11.17 3,656.70+/-284.00 115.46
< 13.04
< 7.11
< 19.27 7,167.00 +/-453.40 197.48
< 17.75
< 19.22 16.93 6,772.90 +-640.60 343.56 +/- 119.70
< 13.40
< 14.82 16.90 7,102.00+/-417.80 190.07 18.22
< 16.91 15.05 11,972.00 +/-903.20 819.30+/-233.50
< 19.20
< 15.65
< 24.18 8,667.40 +/- 631.60 141.66
< 9.43 11.20
- 14.19 4,233.60+/-409.70 154.22
< 18.62
< 15.28
< 25.16 5,419.90+/-571.60 176.79
< 21.03
< 18.37
< 27.08 5,122.80 +/- 563.10 140.41
< 11.13 19.78
< 21.20 3,106.20 +/-465.40
< 202.21
< 15.19
< 7.62
< 26.80 6,087.90 +/- 541.00 645.61 +/- 142.40
< 10.04
< 6.99
< 16.62 5,698.30+/-359.10 Cs-134 7.95 14.35 18.46 13.09 19.34 15.73 10.71 10.75 15.26 22.77 20.04 12.04 Cs-137
< 8.14
< 10.73
< 22.94
< 7.00 18.06
< 18.55
< 11.52 10.88
< 22.62
< 10.10 15.70 10.94
I I
I I
I I
Food Products Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Monthly Results in pCi/kg wet +/- 2 Sigma Location Sample Type 70 chinese cabbage 70 swiss chard 70 turnip greens Collection Date 11/12/01 "11/12/01 11/12/01 Be-7 1-131
< 128.11
< 10.45 288.07 +/- 174.60
< 13.16 834.16 +/- 258.00
< 26.38 Co-58 K-40
< 10.09 3,340.50 +/- 479.20
< 16.46 6,378.70 +/- 641.80
< 18.41 6,465.30 +/- 646.90 Co-60 12.88 16.42
< 23.45 Cs-134
< 12.38
< 21.18
< 24.20 Cs-137 17.77
< 18.68
< 20.34
Location 51 51 51 51 51 51 51 51 51 51 51 51 Milk Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Bi-Monthly Results in pCi/L +/- 2 Sigma Ba-140 Cs-134 Cs-137
< 19
< 7
< 6
<17
<3
<4
<15
<4
<5
< 34
< 4
< 4
<17
<4
<3
<19
<3
<3 Sample Type Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk Collection Date 1/8/01 2/5/01 3/5/01 4/10/01 4/23/01 5/7/01 5/21/01 6/4/01 6/18/01 7/9/01 7/23/01 8/20/01
< 4
< 6
< 4
< 3
< 3
< 3 K-40 La-140 t5
< 24
< 33
< 37
< 40 13
< 3
< 4
< 4
< 3
< 3
< 4 1,546 +/- 177 1,488 +/- 105 1,479 -/- 140 1,336 +/- 149 1,262 +/- 117 1,314+/- 104 1,360+/-89 1,269 +/- 149 1,407 +/- 130 1,327+/-69 1,409+/-80 1,239+/-98
< 2
< 3
< 5
< 6
< 2
< 2
< 2
< 4
< 5
< 8
< 8
< 4
Milk Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Bi-Monthly Results in pCi/L +/- 2 Sigma Location Sample Type Collection Date Ba-140 Cs-134 Cs-137 51 Milk 9/5/01
< 31
< 5
< 7 51 Milk 9/17/01
< 21
< 3
< 3 51 Milk 10/8/01
< 36
< 2
< 3 51 Milk 10/22/01
< 29
< 1
< 1 51 Milk 11/5/01
< 44
< 3
< 3 51 Milk 12/3/01 13
< 6
< 5 61 Milk 61 Milk 61 Milk 61 Milk 61 Milk 61 Milk 4/9/01 4/23/01 5/7/01 5/23/01 6/4/01 6/18/01
< 41
< 17
< 37
< 18
< 14
< 19
< 4
< 3
< 5
< 4
< 4
< 4
< 5
< 3
< 7
< 4
< 5
< 4 I
I 1,401 +/- 134 1,648 +/- 146 1,680 +/- 177 1,705 +/- 134 1,730 +/- 136 1,844 +/- 90 K-40 1,401 +/- 187 1,333 +/- 119 1,368 +/- 94 1,402 +/- 42 704 +/- 82 1,307 +/- 143
< 6
< 3
< 6
< 3
< 2
< 2 La-140
< 3
< 4
< 11
< 6
< 4
< 2
Location 61 61 61 61 61 61 61 71 71 71 71 71 Milk Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Bi-Monthly Results in pCi/L +/- 2 Sigma Ba-140 Cs-134 Cs-137 Sample Type Milk Milk Milk Milk Milk Milk Milk Collection Date 7/9/0 1 7/23/01 8/6/01 8/20/01 9/4/01 9/17/01 10/8/01 1/8/01 2/5/01 3/5/01 4/9/01 4/23/01 in-
-
H-
-
-
-
< 45
< 33
< 16
< 15
< 14
< 10
< 33 16
< 25
< 21
< 32
< I1
< 4
< 5
< 6
< 4
< 4
< 2
< 2
< 4
< 5
< 4
< 3
< 3
< 5
< 4
< 6
< 4
< 4
< 4
< 4
< 5
< 4
< 4
< 4
< 3 Milk Milk Milk Milk Milk K-40 1,757 +/-152 1,866 +/- 125 1,835 +/- 193 1,652 +/- 123 1,751 +/- 122 1,678 +/-91 1,585 +/- 119 1,470 +/- 124 1,238 +/- 120 1,285 +/- 135 1,291 +/- 122 1,455 +/- 129 La-140
< 7
< II
< 5
< 3
< I
< 3
< 6
< 3
< 3
< 3
< 9
< 3
-t-
r--
Milk Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Bi-Monthly Results in pCi/L +/- 2 Sigma Location Sample Type Collection Date Ba-140 Cs-134 Cs-137 Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk 5/7/01
" 5/21/01 6/4/01 6/18/01 7/9/01 7/23/01 8/6/01 8/20/01 9/4/01 9/17/01 10/8/01 10/22/01
< 35
< 21
< 28
< 28
< 41
< 33
< 22 15
< I1
< 28
< 32
< 35
< 6
< 3
< 3
< 2
< 2
< 3
< 3
< 4
< 4
< 2
< 2
< 4
< 6
< 4
< 5
< 3
< I
< 3
< 3
< 7
< 4
< 4
< 5
< 4 K-40 La-140 1,290 +/- 157 1,274 +/- 111 1,238 +/- 164 1,223 +/- 90 1,170+/-44 1,298 +/- 79 1,135 +/- 122 1,237 +/- 165 1,312 +/- 115 1,331 +/- 110 1,260+/- 105 1,335 +/- 99
< 7
< 4
< 4
< 2
< 6
< 7
< 4
< 4
< 4
< 4
< 10
< 11
Milk Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Bi-Monthly Results in pCi/L +/- 2 Sigma Location Sample Type 71 Milk 71 Milk Collection Date 1115101 12/3/01 Ba-140
< 22
< 26 Cs-134
< 2
< 6 Cs-137
< 2 K-40 La-140 1,275 +/-41 1,290 +/- 155
< 4
< 3
(
(
I I
I Milk Iodine Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Bi-Monthly Results in pCi/L +/- 2 Sigma Location 51 51 51 51 51 51 51 51 51 51 51 51 51 51 51 51 51 51 51 61 61 61 61 61 61 61 61 61 61 61 61 61 61 71 71 71 71 71 71 71 4/9/01 4/23/01 5/7/01 5/23/01 6/4/01 6/18/01 7/9/01 7/23/01 8/6/01 8/20/01 9/4/01 9/17/01 10/8/01 10/22/01 1/8/01 2/5/01 3/5/01 4/9/01 4/23/01 5/7/01 5/21/01 Sample Type Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk 0.30 0.26 0.43 0.32 0.26 0.36 0.27 0.24 0.23 0.18 0.42 0.34 0.25 0.37 0.33 0.43 0.33 0.24 0.44 0.35 Collection Dat 1/8/01 2/5/01 3/5/01 4/10/01 4/23/01 5/7/01 5/21/01 6/4/01 6/18/01 7/9/01 7/23/01 8/6/01 8/20/01 9/5/01 9/17/01 10/8/01 10/22/01 11/5/01 12/3/01 1-131
< 0.28
< 0,36
< 0.22
< 0.26
< 0.29
< 0.34
< 0.44
< 0.26
< 0.25
< 0.35
< 0.24
< 0.26
< 0.36
< 0.28
< 0.25
< 0.25
< 0.29
< 0.30 Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk Milk.
Milk Milk Milk Milk Milk Milk Milk
Milk Iodine Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Bi-Monthly Results in pCi/L +/- 2 Sigma Location Sample Type Collection Dat 1-131 71 Milk 6/4/01
< 0.24 71 Milk 6/18/01
< 0.29 71 Milk 7/9/01
< 0.27 71 Milk 7/23/01
< 0.45 71 Milk 8/6/01
< 0.24 71 Milk 8/20/01
< 0.21 71 Milk 9/4/01
< 0.48 71 Milk 9/17/01
< 0.27 71 Milk 10/8/01
< 0.29 71 Milk 10/22/01
< 0.27 71 Milk 11/5/01
< 0.20 71 Milk 12/3/01
< 0.33 S....----: _
-_rH
-HP H -
Sediment Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Bi-Annually Results in pCi/kg dry +/- 2 Sigma Location Sample Type Collection Date Co-58 Co-60 Cs-134 25 Sediment 5/30/01
< 26.13
< 17.25
< 25.62 25 Sediment 10/8/01 12.74
< 9.24
< 16.85 26 26 Sediment Sediment 5/30/01 10/8/01 18.55 36.52 8.76 28.13 10.42 41.89 Cs-137 K-40 292.05 +/- 36.41 16,790.00 +1-763.70 LLD 11,865.00+!- 331.50 LLD
< 35.04 12,569.00 +/- 573.80 11,939.00+/- 793.50 393.47 +/- 36.97 775.19 +/-47.12 210.75 +/- 27.30 1,388.10 +/- 64.71
< 7.73
< 15.50 14,214.00 +/- 658.90 23,983.00 +/- 845.90 11,639.00 +/-519.00 28,881.00 +/- 1,048.00 8,557.30 +/- 417.90 10,127.00 +/- 646.80 27 27 32 32 63 63 Sediment Sediment Sediment Sediment Sediment Sediment 5/30/01 10/8/01 5/30/01 10/8/01 5/30/01 10/8/01 20.72 13.52 14.27 33.88 14.65 34.01 13.65 26.79 6.76 20.06 11.22 10.18 18.49 39.84 15.21 19.98 10.56 30.51
Sediment Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Bi-Annually Results in pCi/kg dry +/- 2 Sigma Location Sample Type 64 Sediment 64 Sediment 65 Sediment Collection Date 5/30/01 10/8/01 5/30/01 Co-58 12.65 12.31
< 17.38 Co-60
< 8.87
< 6.66 12.62 Cs-134
< 8.36
< 8.15 LLD K-40 8,663.50 +/- 417.20 6,494.20 +/- 331.35 15,554.00 +/- 666.50 16.81
< 9.73 12.37 65 Sediment 10/8/01 11.13 7,414.65 +/- 380.37
TLD Gamma Dose Detail Report 2001 Radiological Environmrental Monitoring Program Detail Data Pcrry Nuclear Power Plant, Lake County Ohio Docket no. :50-440/50-441 Sample Frequency is: Quarterly Location Sample Type I
TLD I
TLD I
TLD I
TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD Collection Period 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 Exposure 12.63
+/
14.67
+/
15.62
+/
15.48
+/-
16.27
+/
15.04
+/
15.79
+/
15.26
+/
15.75
+/
15.71
+/
15.73
+/
13.45
+/
13.95
+/
13.50
+/
12.94
+/
13.98
+/
17.19
+/
16.65
+/
17.95
+/
17.00
+/
15.04
+/
14.72
+/
15.36
+/
14.75
+/
12.36 12.33
+/
12.99
+/
13.01
+/
11.26
+/
13,46
+/
12.21
+/
14.09
+/
17.20
+/
17.36
+/
18.07
+/-
0.40 0.23 0.66 0.48 0.23 0.23 0.38 0.45 0.22 0.27 0.36 0.23 0.23 0.38 0.36 0.35 0.35 0.25 0.34 0.22 0.28 0.23 0.61 0.33 0.30 0,21 0.37 0.20 0.23 0.36 0.33 0.21 0.26 0.35 0.42
TLD Gamma Dose Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Quarterly Collection Period 10/2/01 to 1/3/02 Location 10 12 11 11 12 12 12 12 13 13 13 13 14 14 14 14 15 15 15 15 Exposure 18.05
+/-
0.28 TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD 1/4/01 to 4/5/01 TLD 4/5/01 to 7/9/01 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to:
10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 21.51
+/-
0.44 19.43
+/-
0.24 S..
H -
i"
?- ---
16.27 15.42 17.60 14.13 15.88 15.44 17.24 15.44 16.98 14.83 17.72 15.74 13.59 14.31 13.79 15.65 14.82 13.47 14.35 15.43 19.47 17.74 20.05 18.81 17.70 17.40 18.95 17.78 15.85 14.76 15.87 15.48 21 21 21 21 23 23 23 23 24 24 24 24 29 29 Sample Type TLD 0.23 0.22 0.38 0.26 0.33 0.32 0.29 0.45 0.39 0.21 0.30 0.43 0.20 0.21 0.31 0.40 0.26 0.41 0.42 0.49 0.23 0.33 0.48 0.26 0.47 0.26 0.37 0.20 0.23 0.27 0.43 0.46
i fLD Uamma Lose Detail Report 22001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Quarterly Location 29 29 30 30 30 30 31 31 31 31 33 33 33 33 35 35 35 35 36 36 36 36 53 53 53 53 54 54 54 54 55 55 55 55 I
I I
Sample Type TLD TLD 1/4/01 to 4/5/01 14.37
+/-
0.24 TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD TLD Collection Period 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to:
7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 Exposure 20.35
+/-
0.36 19.83
+/-
0.37 15.35
+/-
0.24 15.43
+/-
0.23 17.55
+/-
0.33 17.94
+/-
0.22 17.34
+/-
0.27 19.03
+/-
0.26 18.65
+/-
0.38 19.57
+/-
0.31 18.20
+/-
0.20 19.83
+/-
0.22 18.56
+/-
0.33 19.88
+/-
0.33 12.99
+/-
0.43 15.23
+/-
0.25 13.65
+/-
0.33 14.86
+/-
0.30 17.91
+/-
0.20 18.77
+/-
0.23 20.32
+/-
0.49 18.63
+/-
0.21 14.03
+/-
0.25 16.27
+/-
0.22 15,26
+/-
0.45 15.87
+/-
0.33 13.07
+/-
0.42 15.47
+/-
0.21 16.59
+/-
2.20 15.70
+/-
0.31 14.43
+/r 0.24 17.24
+/-
0.27 15.58
+/-
0.52 17.27
+/-
0.27 56 TLD
TLD Gamma Dose Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Quarterly Collection Period 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 Exposure 14.55
+-0.22 15.43
+/-
0.60 14.88
+/-
0.33 14.89
+/-
0.28 14.42
+/-
0.22 15.39
+/-
0.37 15.18
+/-
0.49 Location 56 56 56 58 58 58 58 Sample Type TLD TLD TLD TLD TLD TLD TLD t
fLD (
iamma.ose Det~n Keport I zutf I Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Quarterly Location I
I I
1 3
3 3
3 4
4 4
4 5
5 5
5 6
6 6
6 7
7 7
7 8
8 8
8 9
9 9
9 10 10 10 10 TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB Exposure Sample Type TLB TLB TLB TLB to 4/5/01 to 7/9/01 to 10/2/01 to 1/3/02 to 4/5/01 to 7/9/01 to 10/2/01 to 1/3/02 to 4/5/01 to 7/9/01 to 10/2/01 to 1/3/02 to 4/5/01 to 7/9/01 to 10/2/01 to 1/3/02 to 4/5/01 to 7/9/01 to 10/2/01 to 1/3/02 Collection Period 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 11.74 14.58 14.89 15.74 13.91 15.28 16.60 15.57 14.62 15.78 16.85 15.55 15.18 14.94 15.59 15.17 15.28 17.58 17.83 16.87 14.67 18.46 15,42 15.69 13.64 13.42 15.04 13.71 13.48 13.84 14.97 14.03 15.88 17.62 18.24 18.24
(
I
+/
+/
+/
+/
+/-
0.28 0.23 0.31 0.60 0.21 0.25 2,05 0.52 0.25 0.24 0.24 0.55 0.22 0.25 0.27 0.35 0.98 0.38 0.22 0.19 0.20 0.23 0.48 0.51 0.23 0.23 0.59 0.20 0.19 0.24 0.49 0.38 0.42 0,37 0.24 0.28 1/4/01 4/5/01 7/9/01 10/2/01 1/4/01 4/5/01 7/9/01 10/2/01 1/4/01 4/5/01 7/9/01 10/2/01 1/4/01 4/5/01 7/9/01 10/2/01 1/4/01 4/5/01 7/9/01 10/2/01
TLD Gamma Dose Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Quarterly Location Sample Type 11 11 11 12 12 12 12 13 13 13 13 14 14 14 14 15 15 15 15 21 21 21 21 23 23 23 23 24 24 24 24 29 29 29 TLB TLB TLB TLB TLB TLB TLB TLB TI1B TLB TLB TLB TLB TLB
"[LB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB Collection Period 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to
-7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 Exposure 13.88 15.68 15.41 15.33 14.23 15.63 15.82 15.93 13.13 14.82 14.67 15.08 11.80 14.60 12.49 13.86 10.64 13.28 11.09 13.11 15.94 17.61 17.53 17.21 13.27 16.52 14.75 16.86 13.51 14.87 14.28 14.45 TLB 1/4/01 to 4/5/01 TLB 4/5/01 to 7/9/01 TLB 7/9/01 to 10/2/01 18.10 20.08 19.97 H---
+/-
0.20
+/-
0.25
+/-
0.51
+/-
0.64
+/-
0.21
+/-
0.25
+/-
0.40
+/-
0.34
+/-
0.27
+/-
0.22
+/-
0.38
+/-
0.25
+/-
0.31
+/-
0.23
+/-
0.28
+/-
0.29
+/-
0.23
+/-
0.28
+/-
0.21
+/-
0.24
+/-
0.45
+/-
0.42
+/-
0.23
+/-
0.22
+/-
0.27
+/-
0.24
+/-
0.39
+/-
0.21
+/-
0.23
+/-
0.24
+/-
0.32
+/-
0.39
+/-
0.23
+/-
0.25
+/-
0.33
S/
(
I ITLD Gamma Dose Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Quarterly Exposure 20.01
+/-
Location 29 30 30 30 30 31 31 31 31 33 33 33 33 35 35 35 35 36 36 36 36 53 53 53 53 54 54 54 54 55 55 55 55 Sample Type TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB "TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB TLB Collection Period 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 tQ 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 56 TLB 56 TLB 1/4/01 to 4/5/01 13.92
+/-
0.22 4/5/01 to 7/9/01 13.53
+/-
0.32 I
I 15.16 16.08 17.10 17.99 18.15 19.81 19.80 19,74 19.99 21.56 21.67 20.82 14.70 16.04 15.80 15.56 19.78 19.37 21.29 19.74 15.86 16.55 17.31 16.94 15.13 16.08 15.63 17.17 14.69 16.85 17.36 16.13
+/-
0.42 0.23 0.25 0.25 0.26 0.22 0.25 0.39 0.53 0.43 0.37 0.21 0.20 0.22 0.25 0.34 0.46 0.35 0.24 0.24 0.35 0,27 0.25 0.26 0.22 0.26 0.24 0.61 0.23 0.21 0.28 0.34 0.25
TLD Gamma Dose Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Quarterly Collection Period 7/9/01 to 10/2/01 10/2/01 to 1/3/02 1/4/01 to 4/5/01 4/5/01 to 7/9/01 7/9/01 to 10/2/01 10/2/01 to 1/3/02 Exposure 15.18
+/-
0,47 13.70
+/-
0.41 13.91
+/-
0.21 14.93
+/-
0.24 14.54
+/-
0.24 14.31
+/-
0.30 I-b-
L-
Location 56 56 58 58 58 58 Sample Type TLB TLB TLB TLB TLB TLB
TLD Gamma Dose Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Annual Location 1
3 4
5 6
7 8
9 10 11 12 13 14 15 21 23 24 29 30 31 33 35 Sample Type TLA TLA TLA TLA TLA TLA TLA TLA TLA TLA TLA TLA TLA TLA TLA TLA TLA TLA TLA TLA TLA TLA Collection Period 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02
-1/4/01 to 1/3/02 1/4/01 to
.1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 Exposure 48.31
+/
47.85
+/
54.94
+/
48.98
+/
58.34
+/
54.60
+/
47.87
+/
48.82
+/
70.48
+/
50.54
+/
57.11
+/
52.17
+/
51.76
+/
51.52
+/
65.31
+/
62.31
+/
51.49
+/
62.47
+/
53.98
+/
65.03
+/-/
67.02
+/
55.82
+/-
0.63 0.79 1.09 0.66 0.63 1.99 0.78 1.06 1.58 0.66 0.98 0.70 1.02 1.15 0,65 0.77 1.03 0.64 0.62 0.84 0.67 0.68
TLD Gamma Dose Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Annual Collection Period 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 1/4/01 to 1/3/02 Exposure 75.22
+/-
1.51 58.96
+/-
0.62 55.79
+/-
0.78 51.12
+/-
1.09 48.54
+/-
0.82 Location 36 53 54 55 56 58 Sample Type TLA TLA TLA TLA TLA TLA S..
I.
Water Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Monthly Results in pCi/L +/- 2 Sigma Location Sample Type Collection Period Ba-140 Co-58 Co-60 Cs-134 Cs-137 Fe-59 La-140 Mn-54 Nb-95 Zn-65 Zr-95 28 Water 12/28/00 to 1/25/01
< 14.91
< 2.63
< 4.66
< 3.05
< 3.83
< 4.80
< 4.71
< 3.07
< 6.45
< 9.50
< 11.42 28 Water 2/22/01 to 2/22/01
< 6.97
< 1.59
< 2.02
< 2.28
< 1.28
< 4.27
< 1.27
< 1.26
< 2.46
< 3.36
< 5.42 28 Water 3/29/01 to 3/29/01
< 21.74
< 3.28 1.65
< 4.02
< 2.75
< 3.54
< 4.88
< 2.64
< 3.64
< 3.96
< 4.13 28 Water 3/29/01 to 4/26/01
< 22.88
< 3.09 1.37
< 2.82
< 2.89
< 1.75
< 4.00
< 3.04
< 3.49
< 4.39
< 4.21 28 Water 4/26/01 to 5/29/01
< 44.85
< 2.71 1.53
< 2.95
< 2.01
< 6.07
< 5.32
< 2.26
< 3.93
< 3.40
< 3.60 28 Water 5/29/01 to 6/28/01
< 42.83
< 2.91 1.64
< 3.02
< 1.86
< 8.43
< 10.06
< 2.83
< 3.95
< 5.96
< 8.23 28 Water 7/26/01 to 7/26/01
< 40.70
< 2.40
< 2.30
< 3.64
< 3.31
< 6.83
< 10.27 1.79
< 5.47
< 5.43
< 6.03 28 Water 7/26/01 to 8/30/01
< 16.26
< 2.43
< 2.75
< 3.27
< 2.13
< 3.93
< 2.11
< 2.63
< 3.14
< 3.43
< 4.73 28 Water 8/30/01 to 9/27/01
< 20.31
< 2.15
< 3.13 1.41
< 2.87
< 6.09
< 2.59
< 3.01
< 3.28
< 4.07
< 7.14 28 Water 10/25/01 to 10/25/01
< 28.87
< 4.97
< 5.01
< 5.54
< 4.45
< 12.06
< 8.77
< 2.32
< 5.61
< 4.82
< 4.54 28 Water 10/25/01 to 11/29/01
< 16.56
< 2.21
< 4.62
< 3.33
< 5.24
< 8.13"
< 5.09
< 3.31
< 2.82
< 6.19
< 6.51 28 Water 11/29/01 to 12/27/01
< 16.79
< 2.20
< 2.99
< 2.63
< 2.42
< 6.75
< 2.45
< 2.69 1.93
< 2.52
< 3.37
Water Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. 50-440/50-441 Sample Frequency is: Monthly Results in pCi/L +/- 2 Sigma Location Sample Type Collection Period Ba-140 Co-58 Co-60 Cs-134 Cs-137 Fe-59 La-140 Mn-54 Nb-95 Zn-65 Zr-95 34 Water 12/28/00 to 1/25/01
< 18.77
< 5.37
< 4.33
< 4.86
< 3.24
< 6.32
< 2.66
< 5.51
< 4.45
< 3.86
< 8.71 34 Water 1/25/01 to 2/22/01
< 10.18
< 2.41
< 1.16
< 2.87
< 2.62
< 5.75
< 4.62
< 2.14
< 1.89
< 2.49
< 5.88 34 Water 2/22/01 to 3/29/01
< 17.14
< 4.14
< 1.30
< 3.69
< 2.67
< 4.06
< 2.52 1.83
< 4.19
< 3.45
< 4.13 34 Water 3/29/01 to 4/26/01
< 31.71
< 2.35
< 2.24
< 2.96
< 3.02
< 4.18
< 4.29
< 1.96
< 2.03
< 5.27
< 7.94 34 Water 4/26/01 to 5/29/01
< 37.29
< 3.79
< 3.59
< 2.65
< 2.88
< 4.15
< 5.40
< 2.20
< 2.92
< 3.70
< 4.70 34 Water 5/29/01 to 6/28/01
< 36.33
< 2.66 1.22
< 2.99
< 3.62
< 5.98
< 6.22
< 2.48
< 4.11
< 5.94
< 5.11 34 Water 6/28/01 to 7/26/01
< 36.00
< 2.26 1.64
< 2.17
< 2.29
< 4.25
< 4.48
< 2.08
< 4.24
< 5.77
< 4.81 34 Water 7/26/01 to 8/30/01
< 20.41
< 2.29
< 2.63
< 3.35
< 1.26
< 6.39
< 5.10
< 3.64
< 3.02
< 2.77
< 5.29 34 Water 8/30/01 to 9/27/01
< 12.29
< 2.56
< 2.53
< 3.00
< 2.48
< 3.85
< 1.91
< 3.03
< 1.39
< 3.09
< 4.36 34 Water 9/27/01 to 10/25/01
< 21.52
< 3.91
< 3.98
< 4.17
< 4.03
< 6.41
< 2.37
< 5.08
< 4.98
< 5.37
< 4.70 34 Water 10/25/01 to 11/29/01
< 17.56
< 2.73
< 3.47
< 2.60
< 4.36
< 3.93
< 2.95
< 3.04
< 3.66
< 2.63
< 5.45 34 Water 11/29/01 to 12/27/01
< 22.49
< 2.35
< 7.78
< 4.36
< 4.79
< 7.63
< 8.47
< 3.99
< 4.49 11.24 11.90
Water Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Monthly Results in pCi/L +/- 2 Sigma Location Sample Type Collection Period Ba-140 Co-58 Co-60 Cs-134 Cs-137 Fe-59 La-140 Mn-54 Nb-95 Zn-65 Zr-95 36 Water 12/28/00 to 1/25/01
< 9.86
< 2.72
< 1.77
< 2.55
< 1.63
< 3.92
< 3.64
< 2.33
< 2.12 1.54
< 4.87 36 Water U/25/01 to 2/22/01 10.25
< 2.85
< 1.85
< 1.35
< 3.41
< 2.25
< 2.11
< 2.36
< 3.87
< 4.27
< 6.16 36 Water 2/22/01 to 3/29/01
< 16.72
< 2.37
< 1.23
< 3.05
< 2.24
< 3.24
<.3.00
< 2.83
< 3.14
< 2.89
< 5.89 36 Water 3/29/01 to 4/26/01
< 28.95
< 2.29
< 1.85
< 4.15
< 3.53
< 3.48
< 10.26
< 2.34
< 3.92
< 5.75
< 6.48 36 Water 4/26/01 to 5/29/01
< 30.28
< 2.64
< 1.29
< 2.31
< 2.51
< 5.77
< 3.74
< 2.38
< 2.69
< 4.85 1.68 36 Water 5/29/01 to 6/28/01
< 43,92
< 3.00
< 1.52
< 2.18
< 2.53
< 5.24
< 8.68
< 2.39
< 5.12
< 3.37
< 5.90 36 Water 6/28/01 to 7/26/01
< 38.28
< 2.86
< 2.26
< 3.12
< 3.23
< 4.43
< 8.75
< 2.67
< 4.14
< 3.46
< 6.41 36 Water 7/26/01 to 8/30/01
< 35.02
< 4.80
< 2.48
< 4.57
< 4.93
< 5.59
< 8.79
< 5.50
< 4.55
< 3.72
< 8.08 36 Water 8/30/01 to 9/27/01
< 13.16
< 2.21
< 2.84
< 2.55
< 3.30
< 4.10
< 4.36
< 2.72
< 2.07
< 4.91
< 8.77 36 Water 9/27/01 to 10/25/01
< 43.84
< 5.37
< 2.63
< 5.67
< 5.66
< 5.84
< 3.97
< 5.00
< 2.78
< 7.11
< 10.21 36 Water 10/25/01 to 11/29/01
< 23.87
< 4.04
< 1.87
< 4.84
< 3.88
< 4.40
< 2.56
< 5.46
< 3.95
< 2.79
< 9.68 36 Water 11/29/01 to 12/27/01
< 26.20
< 4.00
< 2.75
< 4.92
< 4.02
< 7.44
< 4.42
< 6.28
< 3.92
< 4.87
< 10.40
Water Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Monthly Results in pCi/L +/- 2 Sigma Location Sample Type 59 59 59 59 59 59 59 59 59 59 60 60 Water Water Water Water Water Water Water Water Water Water Water Water Collection Period 3/7/01 to 3/29/01 3/29/01 to 4/26/01 Ba-140 Fe-59 Zr-95
< 15.38
< 2.98
< 5.57
< 33.18
< 2.94
< 6.32 4/26/01 to 5/29/01
< 25.90
< 5.61
< 3.53 5/29/01 to 6/28/01
< 23.59
< 5.26
< 2.90 6/28/01 to 7/26/01
< 39.10
< 4.15
< 3.60 7/26/01 to 8/30/01
< 18.79
< 9.60
< 4.82 8/30/01 to 9/27/01
< 14.28
< 3.41
< 3.18 9/27/01 to 10/25/01 10/25/01 to 11/29/01 11/29/01 to 12/27/01 3/7/01 to 3/29/01 3/29/01 to 4/26/01
< 27.09
< 6.69
< 5.77
< 21.47
< 4.86
< 7.71
< 17.26
< 3.93
- 4.72
< 15.28
< 3.34
< 6.38
< 18.97
< 4.32
< 4.86 H-H-
Cs-137 Zn-65
< 2.26
< 4.07 Co-58 La-140
< 3.76
< 3.88
< 3.72
< 6.75
< 3.33
< 4.07 1.51
< 3.65
< 3.04
< 7.83
< 4.23
< 4.09
< 2.47
< 3.23
< 5.29
< 3.13
< 4.07
< 3.37
< 1.92
< 2.97 1.83
< 4.06
< 2.42
< 2.95
< 2.92
< 2.08
< 2.77
< 2.63
< 2.40
< 2.58
< 2.70
< 4.12
< 4.15
< 1.86
< 2.83
< 2.33
< 3.21
< 1.77
< 3.07
< 2.48
< 3.33
< 1.68
< 2.45
< 2.29
< 3.73 Cs-134 Nb-95
- 3.98
< 2.22
< 2.40
< 3.65
< 1.96
< 3.12
- 2.32
< 3.67
< 1.72
< 3.60
< 2.81
< 3.67
< 2.39
< 3.36
< 3.65
< 4.92
< 4.98
< 3.68
< 3.58
< 2.36
< 3.51
< 2.13
< 3.49
< 5.86
< 2.77
< 2.93
< 3.33
< 3.38
< 2.33
< 2.37
< 2.90
< 4.33
< 3.76
< 4.07
< 2.13
< 3.44
< 4.98
< 8.18
< 3.65
< 4.27
< 2.49
< 4.82
< 2.52
< 1.97
- 2.74
< 3.36
Water Gamma Spectral Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. :50-440/50-441 Sample Frequency is: Monthly Results in pCiIL +/-
2 Sigma Location Sample Type 60 60 60 60 60 60 60 60 Water Water Water Water Water Water Water Water Collection Period 4/26/01 to 5/29/01 5/29/01 to 6/28/01 6/28/01 to 7/26/01 7/26/01 to 8/30/01 8/30/01 to 9/27/01 9/27/01 to 10/25/01 10/25/01 to 11/29/01 11/29/01 to 12/27/01 Cs-134 Nb-95
< 2.77
< 5.28 Cs-137 Zn-65
< 3.11
< 6.03 Ba-140 Fe-59 Zr-95
< 25.18
< 7.94
< 6.66
< 35.71
< 4.06
< 7.78
< 34.39
< 3.93
- 3.29 18.19
< 3.91
< 4.68
< 15.92
< 3.41 1.61
< 36.97
< 5.71
< 8.06
< 20.26
< 4.99
< 2.89
< 19.75
< 4.87
- 5.50 Co-58 La-140
< 2.90
< 6.98
< 2.90
< 9.26
< 2.58
< 3.94
< 3.35
< 1.61
< 2.43
< 2.58
< 3.26
< 4.28
< 2.91
< 3.26
< 1.47
< 1.88
< 3.89
< 2.08
< 2.45
< 1.70 1.61
< 2.45
< 2.27
< 2.30
< 2.45
< 3.91
< 4.23
< 4.10
< 3.33
< 2.23 1.86
< 3.11
< 3.85
< 1.84
< 2.92
< 2.80
< 4.10
< 2.78
< 2.42
< 6.16
< 3.72
< 4.27
< 3.22
< 3.57
< 3.21
< 2.72
< 4.05
< 1.69
< 2.17
< 3.79
< 3.28
< 2.59
< 3.79
< 6.60
< 2.93
< 3.74
< 7.46
< 2.67
< 2.78
Collection Period 12/28/00 to 1/25/01 1/25/01 to 2/22/01 2/22/01 to 2/22/01 2/22/01 to 3/29/01 3/7/01 to 3/29/01 3/29/01 to 3/29/01 3/29/01 to 4/26/01 4/26/01 to 5/29/01 5/29/01 to 6/28/01 6/28/01 to 7/26/01 7/26/01 to 7/26/01 7/26/01 to 8/30/01 8/30/01 to 9/27/01 Sample Type Water Water Water Water Water Water Water Water Water Water Water Water Water Water Gross Beta Detail Report 2001 Radiological Environmental Monitoring Program Data Summary Perry Nuclear Power Plant, Lake County Ohio Docket no. :50-440/50-441 Sample Frequency is: Monthly Results in pCi/L +/- 2 Sigma Location 28 34 36 59 LLD LLD LLD LLD LLD 60 LLD LLD LLD LLD 3.06 +/- 0.59 LLD LLD LLD LLD LLD LLD LLD 3.42 +/- 0.59 LLD LLD LLD LLD LLD LLD LLD LLD 3.21 +/- 0.63 LLD LLD LLD LLD LLD LLD LLD LLD 3.62 +/- 0.65 LLD LLD LLD LLD 3.78 +/- 0.72
~-
-__'z--*
r----
Water Gross Beta Detail Report 2001 Radiological Environmental Monitoring Program Data Summary Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Monthly Results in pCi/L +/-/- 2 Sigma Location 28 Collection Period 9/27/01 to 10/25/01 10/25/01 to 10/25/01 10/25/01 to 11/29/01 Sample Type Water Water Water 34 LLD LLD 3.48 +/- 0.71 LID LLD LLD LLD 36 LLD 59 60 LLD LLD LLD LLD 3.86 +/- 0.66 I
i i
i 11/29/01 to 12/27/01 Water 3.40 +/- 0.59 4.15 +/- 0.59
Water Tritium Detail Report 2001 Radiological Environmental Monitoring Program Detail Data Perry Nuclear Power Plant, Lake County Ohio Docket no. : 50-440/50-441 Sample Frequency is: Quarterly Results in pCi/L +/- 2 Sigma Collection Date 3/29/01 6/28/01 9/27/01 12/27/01 Location 28 28 28 28 34 34 34 34 36 36 36 36 59 59 59 59 60 60 60 60 Sample Type Water Water Water Water 3/29/01 6/28/01 9/27/01 12/27/01 3/29/01 6/28/01 9/27/01
.12/27/01 3/29/01 6/28/01 9/27/01 12/27/01 3/29/01 6/28/01 9/27/01 12/27/01 H-3 186.37 152.63 156.26 156.66 186.37 152.63 156.26 LLD 183.50 152.63 156.26 156.66 186.37 152.63 156.26 156.66 186.37 152.63 156.26 156.66 Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT APPENDIX D, 2001 ABNORMAL GASEOUS RELEASE DOSE
SUMMARY
AND METEOROLOGICAL DATA Appendix D Page 44
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT SITE: PERR*
USER: CLN EFFLUENT Y
UNIT: UNIT 1 01
SUMMARY
OF MAXIMUM INDIVIDUAL DOSES LAST ACCUMULATIONS FOR PERIODS:
LIQUID 01010101-01112524 GASEOUS 01120307-01120308 AIR 01120307-01120308 APPLICABLE ESTIMATED AGE LOCATION
% OF ORGAN DOSE GROUP DIST DIR APPLICABLE (M) (TOWARD)
LIMIT MREM)
TOTAL BODY LIVER 2.27E-03 2.95E-03 ADULT CHILD RECEPTOR 1 RECEPTOR 1 NOBLE GAS AIR DOSE 1.58E-07 294 N
1.6E-06 1.0E+01 (GAMMA-MRAD)
NOBLE GAS AIR DOSE 2.92E-07 294 N
1.5E-06 2.OE+01 (BETA-MRAD)
NOBLE GAS T.BODY 9.84E-08 ALL 294 N
2.OE-06 5.OE+00 NOBLE GAS SKIN 2.65E-07 ALL 294 N
1.8E-06 1.5E+01 IODINE&THYROID PARTICULATES 3.70E-07 CHILD 294 N
2.5E-06 1.5E+01 I
I Appendix D Page 45 12101101 LIMIT (MREM)
LIQUID LIQUID 1
I L
I I
7.6E-02 2.9E-02 3.OE+00 1.0E+01 I
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT SITE: PERRY USER: CLN EFFLUENT UNIT: UNIT 1 01
SUMMARY
OF MAXIMUM INDIVIDUAL DOSES LAST ACCUMULATIONS FOR PERIODS:
LIQUID 01010101-01112524 GASEOUS 01100101-01120308 AIR 01100101-01120308 APPLICABLE ESTIMATED AGE LOCATION
% OF ORGAN DOSE GROUP DIST DIR APPLICABLE (MREM)
(M)
(TOWARD)
LIMIT LIQUID TOTAL BODY 2.27E-03 ADULT RECEPTOR 1 7.6E-02 3.OE+00 LIQUID LIVER 2.95E-03 CHILD RECEPTOR 1 2.9E-02 1.OE+01 NOBLE GAS AIR DOSE 2.66E-04 402 NNE 2.7E-03 1.OE+01 (GAMMA-MRAD)
NOBLE GAS AIR DOSE 2.16E-04 273 NW 1.1E-03 2.0E+01 (BETA-MRAD)
NOBLE GAS T.BODY 1.03E-04 ALL 294 N
2.1E-03 5.OE+00 NOBLE GAS SKIN 2.32E-04 ALL 294 N
1.5E-03 1.5E+01 IODINE&THYROID PARTICULATES 1.00E-04 CHILD 294 N
6.7E-04 1.5E+01 Appendix D Page 46 12050753 LIMIT MREM)
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT SITE: PERR' USER: CLN EFFLUENT UNIT: UNIT 1 01
SUMMARY
OF MAXIMUM INDIVIDUAL DOSES LAST ACCUMULATIONS FOR PERIODS:
LIQUID 01010101-01112524 GASEOUS 01100101-01120308 AIR 01100101-01120308 APPLICABLE ESTIMATED AGE LOCATION
% OF ORGAN DOSE GROUP DIST DIR APPLICABLE (MREM)
(M) (TOWARD)
LIMIT 12050753 I
I LIMIT MREM)
LIQUID TOTAL BODY 2.27E-03 ADULT RECEPTOR I 7.6E-02 3.OE+00 LIQUID LIVER 2.95E-03 CHILD RECEPTOR 1 2.9E-02 1.0E+01 NOBLE GAS AIR DOSE 3.02E-02 294 N
3.0E-01 1.OE+01 (GAMMA-MRAD)
NOBLE GAS AIR DOSE 4.33E-02 294 N
2.2E-01 2.OE+01 (BETA-MRAD)
NOBLE GAS T.BODY 6.14E-03 ALL 283 WNW 1.2E-01 5.0E+00 NOBLE GAS SKIN 1.64E-02 ALL 283 WNW 1.IE-01 1.5E+01 IODINE&THYROID PARTICULATES 1.94E-02 CHILD 294 N
1.3E-01 1.5E+01 Appendix D Page 47 L
I 1
I I.
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT SITE: PERRY UNIT: UNIT I HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD =
01120301-01120324 STABILITY CLASS A
DT/DZ 0112050753 ELEVATION:
SPEED: SPD1OP DIRECTION: DIRIOP LAPSE: DT50M WIND WIND SPEED(MPH)
DIRECTION 1-3 4-7 8-12 13-18 19-24
>24 TOTAL N
0 0
0 0
0 0
0 NNE 0
0 0
0 0
0 0
NE 0
0 0
0 0
0 0
ENE 0
0 0
0 0
0 0
E 0
0 0
0 0
0 0
ESE 0
0 0
0 0
0 0
SE 0
0 0
0 0
0 0
SSE 0
0 0
0 0
0 0
S 0
0 0
0 0
0 0
SSW 0
0 0
0 0
0 0
SW 0
0 0
0 0
0 0
WSW 0
0 0
0 0
0 0
W 0
0 0
0 0
0 0
WNW 0
0 0
0 0
0 0
NW 0
0 0
0 0
0 0
NNW 0
0 0
0 0
0 0
TOTAL 0
0 0
0 0
0 0
PERIODS OF CALM (HOURS):
VARIABLE DIRECTION HOURS OF MISSING DATA:
0 0
0 Appendix D Page 48
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT SITE: PERRY UNIT: UNIT 1 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD =
01120301-01120324 0112050753 STABILITY CLASS ELEVATION:
B DT/DZ SPEED: SPDIOP DIRECTION: DIR1OP LAPSE: DT50M WIND WIND SPEED(MPH)
DIRECTION 1-3 4-7 8-12 13-18 19-24
>24 TOTAL N
0 0
0 0
0 0
0 NNE 0
0 0
0 0
0 0
NE 0
0 0
0 0
0 0
ENE 0
0 0
0 0
0 0
E 0
0 0
0 0
0 0
ESE 0
0 0
0 0
0 0
SE 0
0 0
0 0
0 0
SSE 0
0 0
0 0
0 0
S 0
0 0
0 0
0 0
SSW 0
0 0
0 0
0 0
SW 0
0 0
0 0
0 0
WSW 0
0 0
0 0
0 0
W 0
0 0
0 0
0 0
WNW 0
0 0
0 0
0 0
NW 0
0 0
0 0
0 0
NNW 0
0 0
0 0
0 0
TOTAL 0
0 PERIODS OF CALM (HOURS):
VARIABLE DIRECTION HOURS OF MISSING DATA:
0 0
0 0
0 0
0 0
I Appendix D Page 49 I,
1 I
I 4
L I
I 1
I I
I 3 1
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT SITE: PERRY UNIT: UNIT 1 HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD =
01120301-01120324 STABILITY CLASS ELEVATION:
C DT/DZ SPEED: SPDIOP DIRECTION: DIRIOP LAPSE: DT50M WIND WIND SPEED(MPH)
DIRECTION 1-3 4-7 8-12 13-18 19-24
>24 TOTAL N
0 0
0 0
0 0
0 NNE 0
0 0
0 0
0 0
NE 0
0 0
0 0
0 0
ENE 0
0 0
0 0
0 0
E 0
0 0
0 0
0 0
ESE 0
0 0
0 0
0 0
SE 0
0 0
0 0
0 0
SSE 0
0 0
.0 0
0 0
S 0
0 0
0 0
0 0
SSW 0
0 0
0 0
0 0
SW 0
0 0
0 0
0 0
WSW 0
0 0
0 0
0 0
W
.0 0
0 0
0 0
0 WNW 0
0 0
0 0
0 0
NW 0
0 0
0 0
0 0
NNW 0
0 0
0 0
0 0
N N 0..
TOTAL 0
0 PERIODS OF CALM (HOURS):
VARIABLE DIRECTION HOURS OF MISSING DATA:
0 0
0 0
0 0
0 0
Appendix D Page 50 0112050753
I ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT SITE: PERRY UNIT: UNIT I HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD =
01120301-01120324 STABILITY CLASS D
DT/DZ
.1 0112050753 1
ELEVATION:
SPEED: SPD10P DIRECTION: DIRIOP LAPSE: DT50M WIND WIND SPEED(MPH)
DIRECTION 1-3 4-7 8-12 13-18 19-24
>24 TOTAL N
0 0
0 0
0 0
0 NNE 0
0 0
0 0
0 0
NE 0
0 0
0 0
0 0
ENE 0
0 0
0 0
0 0
E 0
0 0
0 0
0 0
ESE 0
0 0
0 0
0 0
SE 0
0 0
0 0
0 0
SSE 0
0 0
0 0
0 0
S 0
0 0
0 0
0 0
SSW 0
0 0
0 0
0 0
SW 0
0 2
0 0
0 2
WSW 0
1 0
1 0
0 2
W 0
0 2
0 0
0 2
WNW 0
0 0
0 0
0 0
NW 0
0 0
0 0
0 0
NNW 0
0 0
0 0
0 0
TOTAL 0
1 PERIODS OF CALM (HOURS):
VARIABLE DIRECTION HOURS OF MISSING DATA:
4 0
0 0.
1 0
0 6
d d
Appendix D Page 51 IL
£ 1.
I I1 I
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT SITE: PERRY UNIT: UNIT I HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD =
01120301-01120324 0112050753 STABILITY CLASS ELEVATION:
E DT/DZ SPEED: SPD1OP DIRECTION: DIRIOP LAPSE: DT50M WIND WIND SPEED(MPH)
DIRECTION 1-3 4-7 8-12 13-18 19-24
>24 TOTAL N...............0...............0...............
0...............
0...............0...............
0 0......
N 0
0 0
0 0
0 0
NNE 0
0 0
0 0
0 0
NE 0
0 0
0 0
0 0
ENE 0
0 0
0 0
0 0
E 0
0 0
0 0
0 0
ESE 0
0 0
0 0
0 0
SE 0
0 0
0 0
0 0
SSE 0
0 0
0 0
0 0
S 0
1 5
0 "0
0 6
SSW 0
1 3
0 0
0 4
SW 0
0 0
0 0
0 0
WSW 1
1 0
0 0
0 2
W 0
0 0
0 0
0 0
WNW 0
0 0
0 0
0 0
NW 0
0 0
0 0
0 0
NNW 0
0 0
0 0
0 0
TOTAL 1
3 PERIODS OF CALM (HOURS):
VARIABLE DIRECTION HOURS OF MISSING DATA:
8 0
0 0
12 0
0 0
Appendix D Page 52
I-ANNuAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT SITE: PERRY UNIT: UNIT I HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD 01120301-01120324 STABILITY CLASS F
DT/DZ 0112050753 ELEVATION:
SPEED: SPD10P DIRECTION: DIRIOP LAPSE: DT50M WIND WIND SPEED(MPH)
DIRECTION 1-3 4-7 8-12 13-18 19-24
>24 TOTAL N
0 0
0 0
0 0
0 NNE 0
0 0
0 0
0 0
NE 0
0 0
0 0
0 0
ENE 0
0 0
0 0
0 0
E 0
0 0
0 0
0 0
ESE 0
0 0
0 0
0 0
SE 1
0 0
0 0
0 1
SSE 0
0 0
0 0
0 0
S 0
0 0
0 0
0 0
SSW 0
0 0
0 0
0 0
SW 0
0 0
0 0
0 0
WSW 0
0 0
0 0
0 0
W 0
0 0
0 0
0 0
WNW 0
0 0
0 0
0 0
NW 0
0 0
0 0
0 0
NNW 0
0 0
0 0
0 0
TOTAL 1
0 0
0 0
0 1
PERIODS OF CALM (HOURS):
VARIABLE DIRECTION HOURS OF MISSING DATA:
0 0
0 Appendix D Page 53 I
1 I
I I
]1
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT SITE: PERRY UNIT: UNIT I HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD =
01120301-01120324 0112050753 STABILITY CLASS ELEVATION:
G DT/DZ SPEED: SPDIOP DIRECTION: DIR1OP LAPSE: DT50M WIND WIND SPEED(MPH)
DIRECTION 1-3 4-7 8-12 13-18 19-24
>24 TOTAL N
0 0
0 0
0 0
0 NNE 0
0 0
0 0
0 0
NE 0
0 0
0 0
0 0
ENE 0
0 0
0 0
0 0
E 0
0 0
0 0
0 0
ESE 0
0 0
0 0
0 0
SE 1
0 0
0 0
0 1
SSE 1
0 0
0 0
0 1
S 2
0 0
0 0
0 2
SSW 1
0 0
0 0
0 1
SW 0
0 0
0 0
0 0
WSW 0
0 0
0 0
0 0
W 0
0 0
0 0
0 0
WNW 0
0 0
0 0
0 0
NW 0
0 0
0 0
0 0
NNW 0
0 0
0 0
0 0
T O T AL..............................................0...........0............0...........0............0...........5.....
TOTAL 5
0 0
0 0
0 5
PERIODS OF CALM (HOURS):
VARIABLE DIRECTION HOURS OF MISSING DATA:
0 0
0 Appendix D Page 54
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT SITE: PERRY UNIT: UNIT I HOURS AT EACH WIND SPEED AND DIRECTION PERIOD OF RECORD =
01120301-01120324 STABILITY CLASS ALL DT/DZ 0112050753 ELEVATION:
SPEED: SPD I OP DIRECTION: DIR1OP LAPSE: DT50M WIND WIND SPEED(MPH)
DIRECTION 1-3 4-7 8-12 13-18 19-24
>24 TOTAL N
0 0
0 0
0 0
0 NNE 0
0 0
0 0
0 0
NE 0
0 0
0 0
0 0
ENE 0
0 0
0 0
0 0
E 0
0 0
0 0
0 0
ESE 0
0 0
0 0
0 0
SE 2
0 0
0 0
0 2
SSE 1
0 0
0 0
0 1
S 2
1 5
0 0
0 8
SSW 1
1 3
0 0
0 5
SW 0
0 2
0 0
0 2
WSW 1
2 0
1 0
0 4
W 0
0 2
0 0
0 2
WNW 0
0 0
0 0
0 0
NW 0
0 0
0 0
0 0
NNW 0
0 0
0 0
0 0
TOTAL 7
4 12 1
0 0
24 PERIODS OF CALM (HOURS):
VARIABLE DIRECTION HOURS OF MISSING DATA:
0 0
0 Appendix D Page 55 LL I
I
'I I.
I
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT APPENDIX E, 2000 AEERR CORRECTIONS Appendix E Page 56
ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Twenty-seven (27) fish samples were collected and analyzed by gamma spectral analysis in 2000.
Sixteen (16) species of fish were represented, including walleye, drum, carp, quilback sucker, spotted sucker, white sucker, redhorse sucker, round gobi, steelhead, catfish, yellow perch, white perch, gizzard shad, smallmouth bass, rock bass and white bass. As expected, naturally occurring potassium-40 was found in all samples. No other radionuclides were detected above the LLD.
Direct Radiation Monitoring Thermoluminscent Dosimeter (TLD)
Environmental radiation is measured directly at twenty-eight locations around the PNPP site, two of which are control locations. The locations are positioned in two 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. The control locations are over ten miles from the plant in the two least prevalent wind directions. Each location is equipped with three TLDs, two of which are changed quarterly and one is changed annually.
A total of 252 TLDs were collected and analyzed in 2000. This included 224 collected on a quarterly basis, and twenty-eight (28) collected annually. In 2000, the annual average dose for all indicator locations was 59.59 mrem, and 56.97 mrem for all control locations. Referring to Figure 8, the average quarterly dose for all indicator locations was 15.2 mrem, and F1 15.2 mrem for the control locations. Prior to 1988, the TLD results were higher due to a change in vendor laboratory services. A comprehensive explanation of this difference was provided in the 1988 Annual Environmental Operating Report.
Figure 10: Average Quarterly TLD Dose
Ž5 20-m lý dia r
Yea ar C o ntrolI Conclusion Sediment samples continue to confirm cobalt-60 in the northwest drain impoundment. The activity level was just above the detection limits. Samples taken upstream did not find mny additional activity or the source. Additional monitoring is being performed to monitor this location. An environmental evaluation determined that there would be less impact upon the environment by leaving this material in place. Atmospheric monitoring results were consistent with past results. The prevalent radionuclide 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 sediment samples 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.
Finally, direct radiation measurements are consistent with past data.
AC E
ID CindAppendi YEa Pager57
Table A-I.
Interlaboratory Comparison Crosscheck program, Environmental Resource Associates (ERA)Y.
Concentration in pa/qb Sample Date Type Collected Analysis Laboratory results
+/-2 Sigmac ERA Result is. N=1 STW-863 WATER Jan, 2000 Gr. Alpha 39.3 t 5.2 25.4:+/- 6.4 14.5-36.3 The analysis was repeated and recalculated with Am-241 efficiency; result of reanalysis 29.32 +/- 5.79 pCi/I Internal spike program results do not indicate a problem.
STW-863 WATER Jan,2000 Gr. Beta 40.7:+/- 1.2 42.1:+/-4.2 33.4-50.8 STW-866 WATER Jan, 2000 Sr-89 17.1.+/-2.
22.5.t5.0 13.8-31.2 STW-866 WATER Jan, 2000 Sr-90 8.1 t 0.6 9.6 +/- 5.0 0.9 - 18.3 STW-868 WATER Feb. 2000 Ra-226 76 +/- 05 8.3.+/- 1.2 6.1-10.4 STW-868 WATER Feb, 2000 Ra-228 5.6 +/- 1.0 2.3 +/- 0.6 1.3-3.2 Result of reanalysis: 6.34 +/- 0.94. Activity confirmed by gamma spectoscopy (6.00+/- 1.42 pCi/L).
The probable cause was a possible error in dilution. Sufficient spiked'sample was not available to
,[ ha've trhe dilution steps re-performed.
STW-868 WATER Feb, 2000 Uranium 5.4+/- 0.2 6.1:+/-L3.0 0.9-11.3 STW-869 WATER Mar, 2000 H-3 23,500.0 +/- 306.0 23,800.0 +/- 2,380.0 19,800.0 - 27,800.(
STW-867 WATER Mar,2000 Gr. Alpha
&3.6+/-5.8 58.4+/-5.8 33.3-83.5 Results were recalculated with Am-241 efficiency, 57.80 +/- 5.73 pCi/L. Refer to STW-863.
WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER WATER Mar, 2000 Mar, 2000 Apr, 2000 Apr, 2000 Apr, 2000 Apr, 2000 Apr, 2000 Apr, 2000 Apr, 2000 Apr, 2000 Apr, 2000 Gr. Beta 1-131 Gr. Alpha Ra-226 Ra-228 Co-60 Cs-134 Cs-137 Gr. Beta Sr-89 Sr-90 15.4 +/- 0.9 18.7 +/- 0.6 52.3+/-t2.3 17.5+/-1.1 3.7+/-0.4 19.2.+/-0.6 81.0+/-t1.3 119.0 +/- 2.6 276.0:+/- 9.6 32.3+/-3.3 11.3+/- 1.0 16.8 +/- 1.7 19.9 +/- 2.0 54.0 +/- 13.5 18.6 +/- 2.8 3.6 +/- 0.9 16.9 +/-5.0 86.4 +/- 5.0 123.0 +/- 6.2 289.0 +/- 43.4 50.7.+/-5.0 32.8.+/-5.0 8.1 - 25.5 18.1 - 28.5 30.8-77.2 13.8-23.4 2.0 - 5.1 8.2-25.6 77.7-95.1 112.0 -134.0 214.0- 364.0 42.0-59.4 24.1-41.5 An error was found in calculation. Result of recalculation: Sr-89, 55.5+/- 7.2 pCi/L / Sr-90, 30.7 +/- 3.0 pCi/L.
Results of reanalysis: Sr-89, 47.4 +/- 14.5 pCi/L / Sr-90, 33.0 +/- 1.35 pCi/L Both results are within limits.
STW-879 WATER Jun,2000 Ba-133 22.4+/-2.1 25.5:+/- 5.0 16.8-342 STW-879 WATER Jun,2000 Co-60 69.9 +/-.3.7 65.6 +/- 5.0 56.9-74-3 STW-879 WATER Jun, 2000 Cs-134 13.5 +/- 0.8 13.8 +/- 5.0 5.1 - 22.5 STW-879 WATER Jun,2000 Cs-137 232.0+/-7.8 238.0+/-11.9 217.0- 259.0 STW-879 WATER Jun,2000 Zn-65 50.9 +/-3.8 54.6+/- 55.
45.3-63.9 STW-880 WATER Jun,2000 Ra-226 2.8 +/-0.2 3.0 +/-0.5 2.2-3.8 STW-880 WATER Jun, 2000 Ra-228 10.0 +/- 0.9 13.0 +/- 3.3 7.4 - 18.6 STW-880 WATER Jun, 2000 Uranium 57.0 +/- 4.4 63.4 +/- 6.3 52.6-74.2 STW-883 WATER Jul, 2000 Gr. Alpha 6.9+/-1.1 7.2+/-5.0 0.0- 15.9 STW-883 WATER Jul, 2000 Gr. Beta 88.8+/-9.8 87-5 +/-10.0 70.2-105.0 STW-884 WATER Aug,2000 H-3 8,740.0_. 174.0 8,320.0 +/- 832.0 6,910.0 - 9,730.0 STW-891 WATER Sep, 2000 Ra-226 17.9+/-1.3 18.9:+/-2.8 14.0-23.8 STW-891 WATER Sep, 2000 Ra-228 5.7_+/-_0.5 6.2 +/- 1.6 3.5-8.8 Al-1 Lab Code Control T.
STW-867 STW-876 STW-877 STW-877 STW-877 STW-878 STW-878 STW-878 STW-878 STW-878 STW-878 is, N=1
t 4PPO S0ýý For more information, write:
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