ML051240116
| ML051240116 | |
| Person / Time | |
|---|---|
| Site: | Fermi  |
| Issue date: | 12/31/2004 |
| From: | DTE Energy |
| To: | Document Control Desk, Office of Nuclear Reactor Regulation |
| References | |
| NRC-05-0034 | |
| Download: ML051240116 (139) | |
Text
FERMI 2 NUCLEAR POWER PLANT DETROIT EDISON COMPANY OPERATING LICENSE NO. NPF - 43 Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report for the period of January 1, 2004 through December 31, 2004 Prepared by:
Fermi 2 Radiological Engineering
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Table of Contents Page Executive Summary I
Introduction 2
Noble Gases 2
Jodines and Particulates 2
Tritium 3
Plant Effluent Monitoring 3
Exposure Pathways to People 4
Dose Assessment 5
Preoperational Surveillance Program 6
Operational Surveillance Program Objectives 7
Program Overview 7
Sample Analysis 8
Quality Assurance 10 Radioactive Effluent Monitoring Results 12 Radiological Environmental Monitoring Program Results 16 Direct Radiation Monitoring 16 Thermoluminescent Dosimeters 16 Atmospheric Monitoring 17 Air Sampling 18 Terrestrial Monitoring 20 Milk Sampling 20 Groundwater Sampling 21 Garden Sampling 22 Aquatic Monitoring 23 Drinking Water Sampling 23 Surface Water Sampling 25 Sediment Sampling 26 Fish Sampling 28 Land Use Census 30 2004 Land Use Census Results 31 Appendix A Sampling Locations A-i Appendix B Environmental Data Summary B-1 ii
Fermi2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Table of Contents Page Appendix C Environmental Data Tables C-l Appendix D Environmental Program Execution D-1 Direct Radiation Monitoring D-l Atmospheric Monitoring D-l Terrestrial Monitoring D-2 Milk Sampling D-2 Garden Sampling D-2 Groundwater Sampling D-2 Aquatic Monitoring D-2 Drinking Water Sampling D-2 Surface Water Sampling D-3 Sediment Sampling D-3 Fish Sampling D-3 Appendix E Effluent and Radwaste Data Regulatory Limitsfor Radioactive Effluents E-l Gaseous Effluents E-1 Liquid Effluents E-2 Measurements and Approximations of TotalActivity in Radioactive Effluents E-3 Gaseous Effluents E-3 Fission and Activation Gases E-3 Radioiodines E-3 Particulates E-4 Tritium E-4 Gross Alpha E-5 Liquid Effluents E-5 Statistical Measurement Uncertainties E-5 iii
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Table of Contents Page Gaseous Release by Individual Nuclide E-5 Particulate Radionuclides E-6 Noble Gases E-6 Radioiodines E-7 Shipments of Radwaste E-7 Class A Resin E-8 Class B Resin E-9 Class C Resin E-9 Dry compressible waste, contaminated equipment, etc.
E-10 Irradiated components, control rods, etc.
E-10 Other E-10 Appendix F Interlaboratory Comparison Data, Framatome ANP Environmental Laboratoriy's Quality Assurance Programs Interlaboratory Comparison Program for 2004 F-i Appendix G Meteorological Data G-1 Appendix H Plant Related Isotope Detected in Environmental Air Sampling Media H-I I.
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Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report List of Figures Page Figure 1 Fermi 2 Annual Average TLD Gamma Exposure 17 Figure 2 Historical Gross Beta and Iodine-131 Activity in Air Samples 19 Figure 3 Fermi 2 Air Particulate Gross Beta for 2004 19 Figure 4 Historical Strontium-90 Activity in Local Milk Samples 21 Figure 5 Historical Gross Beta Activity in Drinking Water Samples 25 Figure 6 Historical Cesium-137 Activity in Sediment Samples 28 Map I Sampling Locations By Station Number (within 1 mile)
App.-A Map 2 Sampling Locations By Station Number (I to 5 miles)
App.-A Map 3 Sampling Locations By Station Number (greater than 5 miles)
App.-A I
Fermi2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report List of Tables Page Table I Fission and Activation Gases (Noble Gases) Summary 12 Table 2 Radioiodines Summary 13 Table 3 Particulates Summary 13 Table 4 Tritium Summary 13 Table 5 2004 Gaseous Effluent Dose to Receptor with Highest Single Organ Dose 14 Table 6 Solid Waste Received at Burial Sites 15 Table 7 Solid Waste Shipments 15 Table 8 2004 Average Gross Beta Concentrations in Air Particulates 18 Table 9 Closest Residences 32 Table 10 Closest Gardens 33 Table 11 Milk Locations 34 Table 12 Closest Meat Locations 35 Table A-I Direct Radiation Sample Locations A-l Table A-2 Air Particulate and Air Iodine Sample Locations A-7 Table A-3 Milk Sample Locations A-7 Table A-4 Garden -Sample Locations A-8 Table A-5 Drinking Water Sample Locations A-8 Table A-6 Surface Water Sample Locations A-9 Table A-7 Groundwater Sample Locations A-9 Table A-8 Sediment Sample Locations A-10 Table A-9 Fish Sample Locations A-10 Table B-I Radiological Environmental Monitoring Program Summary B-I vi
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Executive Summary This report is published to provide information regarding radioactive effluent and environmental monitoring at the Fermi 2 Nuclear Power Plant. The 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report covers the period from January 1, 2004 through December 31, 2004.
The Radioactive Effluent Release and Radiological Environmental Operating Report is produced annually, as required by the Nuclear Regulatory Commission, to present detailed results of extensive monitoring of plant releases and measuring of radiation in the environment around the plant. This report also includes details of the independent oversight incorporated into the Radiological Effluent and Environmental Monitoring Programs to ensure program accuracy.
This report describes both the continual environmental radiation monitoring and effluent monitoring of plant systems. Both types of monitoring indicate that the operation of Fermi 2 does not result in significant radiation exposure of people or the environment surrounding Fermi 2 and is well below the applicable levels set by the Nuclear Regulatory Commission (NRC) and the Environmental Protection Agency (EPA).
There were no releases of liquid radioactive effluents from Fermi 2 in 2004. In fact, there has not been a liquid radioactive discharge from Fermi 2 since 1994.
The highest potential single organ dose to a person living offsite due to iodines and particulates released from the plant was calculated to be 0.1 mrem, which is less than 1%
of the applicable limit found in 10 CFR 50, Appendix I.
Also during 2004, there was no measurable direct radiation dose due to Fermi 2 beyond the site boundary as shown by offsite thermoluminescent dosimeters (TLD) readings.
The offsite dose due to effluents is an extremely small fraction of the 40 CFR 190 limits.
Therefore, the combined direct radiation and effluent dose due to Fermi 2 was in compliance with 40 CFR 190 in 2004.
Environmental samples collected in 2004 showed no radioactivity attributable to the operation of Fermi 2. The results of environmental sampling show that radioactivity levels have not increased from the background radioactivity detected prior to the operation of Fermi 2. The operation of Fermi 2 continues to have no measurable radiological impact upon the environment.
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Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Introduction During the normal operation of a nuclear power plant, most of the fission products are retained within the fuel and fuel cladding. However, small amounts of radioactive fission products and trace amounts of the component and structure surfaces which have been activated are present in the primary coolant water. The four types of radioactive material released are noble gases, iodine, particulates, and tritium.
Noble Gases Some of the fission products released in airborne effluents are radioactive radionuclides of noble gases, such as xenon and krypton. These noble gases are released continuously at low levels while the reactor is operating, and releases may be increased when the reactor is depressurized or when there are leaks in the fuel cladding. Noble gas releases to the environment are reduced by plant systems which delay release of these gases from the plant, which allows a portion of the noble gas activity to decay within plant systems after it is released from the fuel.
Noble gases are biologically and chemically nonreactive. They do not concentrate in humans or other organisms. They contribute to human radiation dose by being an external source of radiation exposure to the body. They are'readily dispersed in the atmosphere.
Iodines and Particulates Fermi 2 is required to calculate offsite dose due to releases of iodine-131 and iodine-133, which are radioisotopes of iodine with half lives of 8 days and I day, respectively, and particulates with half-lives greater than 8 days in gaseous and liquid effluents, and tritium. The principal radioactive particulates released are fission products (e.g., yttrium-91m and barium-139) and activation products (e.g., cobalt-58 and cobalt-60). Annual releases of these radionuclides are small. Factors such as their high chemical reactivity and solubility in water, combined with the high efficiency of gaseous and liquid processing and radwaste systems, minimize their discharge.
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Fermi2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report The main contribution of radioactive iodine to human radiation dose is to the thyroid gland, where the body concentrates iodine. This exposure results from inhalation or ingestion of these iodines. Radioactive cesiums and cobalts, when ingested or inhaled, contribute to radiation exposure of tissues such as the muscle, liver, and intestines. These iodines and particulates are also a source of external radiation exposure if deposited on the ground.
Tritium Tritium, a radioactive isotope of hydrogen, is the predominant radionuclide in liquid effluents. It is also present in gaseous effluents, and is routinely detected at Fermi 2.
Tritium is produced in the reactor coolant as a result of neutron interaction with deuterium (also a hydrogen isotope) present in the water, and it is also a fission product.
Plant Effluent Monitoring Effluents are strictly monitored to ensure that radioactivity released to the environment is as low as reasonably achievable and does not exceed regulatory limits. Effluent control includes the operation of monitoring systems, in-plant and environmental sampling and analyses programs, quality assurance programs for effluent and environmental programs, and procedures covering all aspects of effluent and environmental monitoring.
The radioactive waste treatment systems at Fermi 2 are designed to collect, process, and/or delay the release of liquid and gaseous wastes which contain radioactivity. For example, the 2.0 and 2.2 minute holdup pipes delay the release of radioactive gases so that radioactive decay can occur prior to release. The offgas system provides additional delay for such gases.
Radioactivity monitoring systems are used to ensure that all releases are below regulatory limits. These instruments provide a continuous indication of the radioactivity present at the release points. Each instrument is equipped with alarms and indicators in the control room. The alarm setpoints are low enough to ensure that applicable limits will not be exceeded. In some cases, these alarms restrict the release. For example, if the liquid radwaste effluent monitor alarms, a release in progress is automatically stopped. Also, several alarms cause building ventilation systems to be shut down and/or gaseous releases to be diverted to the standby gas treatment system.
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Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report All wastes are evaluated to identify the specific concentrations of radionuclides being released. Sampling and analysis provide a more sensitive and precise method of determining effluent composition than monitoring instruments.
A meteorological tower is located on the Fermi 2 site. It is linked to computers which record the meteorological data. This data is used in calculating dispersion and deposition factors, which are essentially dilution factors between plant release points and points offsite. Coupled with the effluent release data, these factors are used to calculate dose to the public.
Beyond the plant, devices maintained in conjunction with the Radiological Environmental Monitoring Program constantly sample the air in the surrounding environment. Frequent samples of other environmental media, such as water and vegetation, are also taken to determine if buildup of deposited radioactive material has occurred in the area.
Exposure Pathways to People Radiological exposure pathways define the methods by which people may become exposed to radioactive material. The major pathways of concern are those which could cause the highest calculated.radiation dose. :These projected pathways are determined from the type and amount of radioactive material released, the environmental transport mechanism, and the use of the environment. The environmental transport mechanism includes consideration of physical factors, such as the hydrological (water) and meteorological (weather) characteristics of the area.
An important factor in evaluating the exposure pathways is the use of the environment.
This is evaluated in the annual Land Use Census. Many factors are considered, such as the locations of homes, gardens, and milk or meat animals in the area.
The release of radioactive gaseous effluents involves pathways such as external whole body exposure, deposition of radioactive material on plants, deposition on soil, inhalation and ingestion by animals raised for human consumption, and inhalation by humans. The release of radioactive material in liquid effluents involves pathways such as drinking water and fish consumption.
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Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Although radionuclides can reach humans by many different pathways, some result in greater dose than others. The most significant pathway is the exposure pathway which will provide the greatest dose to a population, or to a specific individual. Identification of the most significant pathway depends on the radionuclides involved, the age and diet of the individual, and the location of the individual's residence. The doses calculated may be delivered to the whole body or to a specific organ. The organ receiving the greatest fraction of the dose is important in determining compliance with dose limits.
Dose Assessment Dose is energy deposited by radiation in an exposed individual. Whole body exposure to radiation involves the exposure of all organs. Most exposures due to external sources of radiation are of this type. Both non-radioactive and radioactive elements can enter the body through inhalation or ingestion. When they do, they are usually not distributed evenly. For example, iodine concentrates in the thyroid gland, cesium collects in muscle and liver tissue, and strontium collects in bone tissue.
The total dose to organs from a given radionuclide depends on the amount of radioactive material present in the organ and the amount of time that the radionuclide remains in the organ. Some radionuclides remain for very short times due to their rapid radioactive decay and/or elimination rate from the body, while other radionuclides may remain in the body for longer periods of time. Also the form of the radionuclide (soluble vs. insoluble) and the method of uptake also influence residence times in the body.
The dose to the general public in the area surrounding Fermi 2 is calculated for periods of gaseous release and for each liquid release. The dose due to radioactive material released in gaseous effluents is calculated using factors such as the amount of radioactive material released, the concentration beyond the site boundary, the locations of exposure pathways (cow milk, goat milk, vegetable gardens and residences), and usage factors (inhalation and food consumption). The dose due to radioactive material released in liquid effluents is calculated using factors such as the total volume of liquid, the total volume of dilution water, near field dilution, and usage factors (water and fish consumption). These calculations produce a conservative estimation of the dose.
The Radiological Environmental Monitoring Program (REMP) was established at Fermi 2 for several reasons: to provide a supplementary check on the effluent controls, to assess the radiological impact of the plant's operation on the surrounding area, and to determine compliance with applicable radiation protection guides and standards. The REMP was established in 1978, seven years before the plant became operational. This preoperational surveillance program was established to describe and quantify the 5
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report radioactivity, and its variability, in the area prior to the operation of Fermi 2. After Fermi 2 became operational in 1985, the operational surveillance program continued to measure radiation and radioactivity in the surrounding areas.
A variety of environmental samples are collected as part of the REMP at Fermi 2. The selection of sample types is based on the established pathways for the transfer of radionuclides through the environment to humans. The selection of sampling locations is based on sample availability, local meteorological and hydrological characteristics, local population characteristics, and land usage in the area of interest. The selection of sampling frequencies for the various environmental media is based on the radionuclides of interest, their respective half-lives, and their behavior in both the biological and physical environment.
Preoperational Surveillance Program The federal government requires nuclear facilities to conduct radiological environmental monitoring prior to constructing the facility. This preoperational surveillance program is aimed at collecting the data needed to identify pathways, including selection of the radioisotope and sample media combinations to be included in the environmental surveillance program conducted after facility operation begins. Radiochemical analyses performed on the environmental samples should include not only those nuclides expected to be released during facility operation, but should also include typical radionuclides from nuclear weapons testing and natural background radioactivity. All environmental media with a potential to be affected by facility operation, as well as those media directly in the major pathways, should be sampled on at least an annual basis during the preoperational phase of the environmental surveillance program.
The preoperational surveillance design, including nuclide/media combinations, sampling frequencies and locations, collection techniques, and radioanalyses performed, should be carefully considered and incorporated in the design of the operational surveillance program. In this manner, data can be compared in a variety of ways (for example, from year to year, location to location, etc.) in order to detect any radiological impact the facility has on the surrounding environment. Data collection during the preoperational phase should be planned to provide a comprehensive database for evaluating any future changes in the environment surrounding the nuclear facility.
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Fermi 2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report Fermi 2 began its preoperational environmental surveillance program seven years before the plant began operating in 1985. Data accumulated during those early years provide an extensive database from which environmental monitoring personnel are able to identify trends in the radiological characteristics of the local environment. The environmental surveillance program at Fermi 2 will continue after the plant has reached the end of its economically useful life and decommissioning has begun.
Operational Surveillance Program Objectives The operational phase of the environmental surveillance program at Fermi 2 was designed with the following objectives in mind:
to determine whether any significant increase occurs in the concentration of radionuclides in major pathways; to identify and evaluate the buildup, if any, of radionuclides in the local environment, or any changes in normal background radiation levels; to verify the adequacy of the plant's controls for the release of radioactive materials; to fulfill the obligations of the radiological surveillance sections of Fermi 2's Offsite Dose Calculation Manual.
Program Overview The Radiological Environmental Monitoring Program (REMP) at Fermi 2 is conducted in accordance with Title 10, Code of Federal Regulations, Part 50; NRC Regulatory Guide 4.8; the Fermi 2 Offsite Dose Calculation Manual (ODCM); and plant operating procedures. Samples are collected either weekly, monthly, quarterly, semiannually, or annually, depending upon the sample type and nature of the radionuclides of interest.
Environmental samples collected by Fermi 2 personnel are divided into four general types:
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Fermi 2-2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report
- direct radiation -- measured by thermoluminescent dosimeters (TLDs).
- atmospheric -- including samples of airborne particulates and airborne radioiodine.
terrestrial -- including samples of milk, groundwater, and broad leaf vegetation.
- aquatic -- including samples of drinking water, surface water, fish, and shoreline and bottom sediments.
REMP samples are collected onsite and offsite up to 20 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 the effects caused by the operation of Fermi 2. Generally, they are located within ten miles of the plant.
Control locations are those which should be unaffected by plant operations. Typically, these are more than ten miles away from the plant. Data obtained from the indicator locations are compared with data from the control locations. This comparison allows REMP personnel to take into account naturally occurring background radiation or fallout from weapons testing in evaluating any radiological impact Fermi 2 has on the surrounding environment. Data from indicator and control locations are also compared with preoperational data to determine whether significant variations or trends exist.
Sample Analysis When environmental samples are analyzed, several types of measurements may be performed to provide information about the radionuclides present. The major analyses that are performed on environmental samples collected for the Fermi 2 REMP include:
Gross beta analysis measures the total amount of beta emitting radioactive material present in a sample. Beta radiation may be released by many different radionuclides.
Since beta decay gives a continuous energy spectrum rather than the discrete lines or "peaks" associated with gamma radiation, identification of specific beta emitting nuclides is much more difficult. Therefore, gross beta analysis only indicates whether the sample contains normal or abnormal concentrations of beta emitting radionuclides; it does not identify specific radionuclides. Gross beta analysis merely acts as a tool to identify samples that may require further analysis.
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Fermi 2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report Gamma spectral analysis provides more specific information than does gross beta analysis. Gamma spectral analysis identifies each gamma emitting radionuclide present in the sample, and the amount of each nuclide present. Each radionuclide has a very specific "fingerprint" that allows for swift and accurate identification. For example, gamma spectral analysis can be used to identify the presence and amount of iodine-1 31 in a sample. Iodine-131 is a man-made radioactive isotope of iodine that may be present in the environment as a result of fallout from nuclear weapons testing, routine medical, or routine releases from nuclear power stations.
Tritium analysis indicates whether a sample contains the radionuclide tritium (H-3) and the amount present. Tritium is an isotope of hydrogen that emits low energy beta particles.
Strontium analysis identifies the presence and amount of strontium-89 and strontium-90 in a sample. These man-made radionuclides are found in the environment mainly as a result of fallout from nuclear weapons testing. Strontium is usually incorporated into the calcium pool of the biosphere. In other words, strontium tends to replace calcium in living organisms and becomes incorporated in bone tissue. The principle strontium exposure pathway is via milk produced by cattle grazed on pastures exposed to deposition from airborne releases.
Gamma Doses measured by thermoluminescent dosimeters while in the field are determined by a special laboratory procedure.
Often samples will contain little radioactivity, and may be below the lower limit of detection for the particular type of analysis used. The lower limit of detection (LLD) is the smallest amount of sample activity which can be detected with a reasonable degree of confidence, at a predetermined level. When a measurement of radioactivity is reported as less than LLD (<LLD), it means that the radioactivity is so low that it cannot be accurately measured with any degree of confidence by that particular method for an individual analysis.
Many radionuclides are present in the environment due to sources such as cosmic radiation and fallout from nuclear weapons testing. Some of the radionuclides present are:
- tritium, present as a result of the interaction of cosmic radiation with the upper atmosphere, as a result of routine release from' nuclear facilities, and due to fallout from past atmospheric nuclear weapons testing.
- beryllium-7, present as a result of the interaction of cosmic radiation with the upper atmosphere.
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Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report
- cesium-137, a man-made radionuclide which has been deposited in the environment, (for example, in surface soils) as a result of fallout from nuclear weapons testing and routine releases from nuclear facilities.
- potassium-40, a naturally occurring radionuclide normally found throughout the environment (including humans).
- fallout radionuclides from nuclear weapons
- testing, including strontium-89, strontium-90, cesium-137, cerium-141, cerium-144, and ruthenium-106.
These radionuclides may also be released in minute amounts from nuclear facilities.
The radionuclides listed above are expected to be present in many of the environmental samples collected in the vicinity of the Fermi 2. The contribution of radionuclides from the operation of Fermi 2 is assessed by comparing sample results with preoperational data, operational data from previous years, control location data, and the types and amounts of radioactivity normally released from the Fermi 2 in liquid and gaseous effluents.
Quality Assurance An important part of the environmental monitoring program at Fermi 2 is the Quality Assurance (QA) program. It is conducted in accordance with the guidelines specified in NRC Regulatory Guide 4.15, "Quality Assurance for Radiological Monitoring Programs."
The QA program is designed to identify possible deficiencies in the REMP so that corrective actions can be initiated promptly. Fermi 2's Quality Assurance program also provides confidence in the results of the REMP through:
- performing regular audits of the REMP, including a careful examination of sample collection techniques and record keeping;
- performing audits of the vendor laboratory which analyzes the environmental samples;
- requiring the analytical vendor laboratory to participate in an approved Cross-Check Program; 10
Fermi2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report
- splitting samples prior to analysis by an independent laboratory and then comparing the results for agreement, and finally;
- requiring the analytical laboratory to perform in-house spiked sample analyses.
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Fermi 2-2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Radioactive Effluent Monitoring Results This section summarizes the results of effluent monitoring and offsite dose calculation for the year 2004, as well as a listing of radioactivity contained in Fermi 2 waste shipped for burial. Calculated offsite doses are compared with Nuclear Regulatory Commission limits, and these limits are summarized in Appendix E. Appendix E also contains a detailed discussion of the methods used to determine quantities of radioactivity released in effluents, the types of solid radwaste, as well as tables of individual radionuclides released in effluents and shipped as solid radwaste.
There were no releases of liquid radioactive effluents from Fermi 2 in 2004. In fact, there has not been a liquid radioactive discharge from Fermi 2 since 1994. The 2004 gaseous effluent releases are summarized in the following tables. There were no abnormal releases of radioactive material, i.e., releases not performed in accordance with the Fermi 2 license and implementing procedures, in 2004.
The data in the following tables represent continuous and batch releases. In 2004, there was one containment purge in which radioactivity was detected. Based on recorded start and stop times, this purge lasted 104 minutes.
Note that some values in the following summary tables are preceded by the "less than" symbol. These values represent the lower limit of detection (LLD) in units of microcuries per cubic centimeter (gCikcc) for individual samples, and indicate that isotopes in the applicable release category were not detected in the quarter. (For noble gases, the value
<2.5E-07 is the sum of the LLD values for 4 common noble gases isotopes listed in Appendix E.)
Table 1 - Fission and Activation Gases (Noble Gases) Summary i..Qirter 1. -
-aQrt.er2 Q He 3>
- 'Q2uarter4; Total Release
<2.5E-07
<2.5E-07
<2.5E-07
<2.5E-07 (curies)
Average Release NA NA NA NA Rate for Period (RlCi/sec) 12
Fermi2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report Table 2 - Radioiodines Summary Qae 1
Quarter i Quarte.3 Quarter 4>
Total I-131 8.232-04 1.292-03 1.062-03 1.18E-03 (curies)
Average Release 1.05E-04 1.64E-04 1.33E-04 1.48E-04 Rate for Period (gCilsec)
Table 3 - Particulates Summary Quarr 1 Q
r 2 '-;
Quart3 Quater.
i 4 Particulates with 4.05E-04 4.242-05 1.211E-04 4.20E-04 half lives > 8 days (curies)
Average 5.15E-05 5.392-06 1.52E-05 5.282-05 Release Rate for Period (gCi/sec)
Gross Alpha 3.002-08 1.32E-09 3.75E-08
<1.02-15 Radioactivity (curies)
Table 4 - Tritium Summary
uart'er.
1 Quarter 2 Quarter3
'Quarter 4
Total Release 1.99E+01 3.302+01 3.40E+01 1.462+01 (curies)_
Average Release 2.53E+00 4.20E+00 4.28E+00 1.842+00 Rate for Period (gCi/sec)
The offsite dose impact of the above releases was evaluated by calculating organ doses to the most highly exposed individual living near the plant due to I-131, I-133, tritium, and particulates with half lives greater than 8 days. This exposure is assumed to be occurring via the pathways of inhalation, vegetation ingestion, and direct radiation from material deposited on the ground. The results of this calculation are shown in the following table:
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Fermi2 2 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Table 5
'.2004. Gaseous*EffluenftDose to r g a
ngs
-Receptor with bestingleOrgan
'a i- -
> -I oses ones 3.99E-03 mrem Lver';
1.32E-02 mrem yli~oid j l.15E-01mrem dney-1.34E-02 mrem ung 2
.29E-02 mrem I-LU -.
31E-02 mrem otal body
- 1.33E-02 mrem The highest single organ dose is 1.1 5E-0 I mrem to the thyroid. This is less than 1% of the federal limit of 15 mrem specified in 10 CFR 50, Appendix I.
Another dose calculation normally performed on the above release data is that for gamma and beta air dose at the site boundary due to noble gases. However, in 2004 noble gases were not detected in gaseous effluent noble gas samples.
Title 40, Part 190 of the Code of Federal Regulations requires that dose to an individual in the unrestricted area from the uranium fuel cycle, including direct radiation dose, be limited to 25 mrem/year to the total body and 75 mrem/year to the thyroid. During 2004, there was no measurable direct radiation dose beyond the site boundary as shown by offsite TLD readings. Also, offsite dose due to effluents is an extremely small fraction of the 40 CFR 190 limits. Therefore, Fermi 2 was in compliance with 40 CFR 190 in 2004.
Potential dose to visitors at Fermi 2 due to all radioactive effluents, including noble gases, was also calculated. The Offsite Dose Calculation Manual (ODCM) considers persons visiting the Fermi 2 Visitors Center (4 hour4.62963e-5 days <br />0.00111 hours <br />6.613757e-6 weeks <br />1.522e-6 months <br />s/year), and persons ice fishing on Lake Erie near the plant (240 hour0.00278 days <br />0.0667 hours <br />3.968254e-4 weeks <br />9.132e-5 months <br />s/year), to be visitors. Using ODCM assumptions about these categories of visitors, the maximum potential dose to a visitor to Fermi 2 in 2004 was 0.004 mrem to the maximally exposed organ (thyroid) and 0.002 mrem to the total body.
Also, the dose to the entire population within a fifty mile radius of Fermi 2 (about 6 million people) was calculated. This dose was estimated to be less than one person-rem for 2004. This dose is insignificant compared to the background radiation dose to this population of approximately 1.8 million person-rem (based on an annual average individual background dose of 300 mrem).
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Fermi2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report The radioactivity and volume of Fermi 2 solid waste received at the Barnwell, SC, burial facility, or at the Envirocare, UT, facility in 2004 is summarized in the following table:
Table 6 - Solid Waste Received At Burial Sites Est-. ot'al
- nIt
'2month a-ctivity
- Type of waste.-'
peUod -
error, So Spent resins, sludges, etc.
m3 2.83E+01 curies 7.32E+0l
+/- 25 Dry compressible waste, m'
1.51 E+O I contaminated equipment, etc.
curies 3.62E-0l
+/- 25 Irradiated components, control m3 0
rods, etc.
curies 0
NA Other m3 0
curies 0
NA Radioactive solid waste shipments from Fermi 2 in 2004 (to either disposal or to intermediate processors) are summarized in the following table:
Table 7 - Solid Waste Shipments Typeof shipment!
- Numberof ' Mode' f Destination solidification process§.'
shipmentb' to apsj'ortio o-Spent resin, sludges, etc.
9 tractor trailer Chem Nuclear, Barnwell, SC with cask Studsvik, Erwin, TN Dry compressible waste, 10 tractor trailer Duratek, Oak Ridge, TN contaminated equipment, etc.
Used oil 0
NA NA Mixed waste I
tractor trailer PermifixIDSSI, Oak Ridge, TN The ODCM was not revised in 2004.
In 2004, no liquid or gaseous effluent monitoring instrumentation was out of service longer than the time limits specified in the ODCM. Also, no outside temporary tank exceeded the 10 curie content limit, and there were no major changes to radioactive waste systems in 2004.
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Fermi2-2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Radiological Environmental Monitoring Program Results Direct Radiation Monitoring Radiation is a normal component of the environment resulting primarily from natural sources, such as cosmic radiation and naturally occurring radionuclides; and to a lesser extent, from manmade sources such as fallout from past nuclear weapons testing. The earth is constantly bombarded by cosmic radiation in the form of high energy gamma rays and particulates. The earth's crust also contains natural radioactive material, such as uranium and potassium-40, which contributes to the background radiation. Direct radiation monitoring primarily measures ionizing radiation from cosmic and terrestrial sources.
Thermoluminescent Dosimeters Detroit Edison uses thermoluminescent dosimeters (TLDs) to measure direct gamma radiation in the environs of Fermi 2. In this process, ionizing radiation interacts with a phosphor which is the sensitive material in the TLD. Energy is trapped in the TLD material and can be stored for several months or years. This provides an excellent method to measure the dose received over long periods of time. The energy that was stored in the TLD as a result of interaction with radiation is released and measured by a controlled heating process in a calibrated reading system. As the TLD is heated, the phosphor releases the stored energy in the form of light. The amount of light detected is directly proportional to the amount of radiation to which the TLD was exposed. This reading process then rezeros the TLD and prepares it for reuse.
Fermi 2 has 67 TLD locations within a fifteen mile radius of the plant. Of the 67 TLD locations, 18 are located on-site and are not used for comparison with the control locations. These 18 TLDs are affected by Hydrogen Water Chemistry's sky shine and are not representative of off-site dose. The TLDs are thoroughly tested to comply with NRC Regulatory Guide 4.13 and American National Standards Institute's (ANSI) publication N545-1975, which assure accurate measurements under varying environmental conditions before being placed in the field. Indicator TLDs are located within a ten mile radius of the plant and control TLDs are located at a distance that is outside the influence of the plant. While in the field, TLDs are exposed to background radiation and, if measurable, gaseous effluents and direct radiation from Fermi 2. Environmental TLDs are exchanged and processed on a quarterly basis. The TLDs' data are reported in terms of milliroentgen per standard quarter (mR/std qtr), with a standard quarter being 91 days. Regardless of the duration of TLD exposure in the field, the data have been normalized to a standard quarter to allow convenient intercomparisons with the net value.
16
Fermi 2-2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report In 2004, the average exposure for TLDs at all off-site indicator locations was 14.6 mR/std qtr and for all control locations was 14.3 mR/std qtr. These exposures are consistent with preoperational and past operational measurements as shown in Figure 1.
Fermi 2 Annual Average TLD Gamma Exposure 25-20-
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- Indicator -a-Control Figure 1 - Fermi 2 Annual Average TLD Gamma Exposure; The similarity between indicator and control results demonstrates that the operation of Fermi 2 has not caused any abnormal gamma exposure.
Atmospheric Monitoring A potential exposure pathway to people is inhalation of airborne radioactive materials.
Detroit Edison continuously samples the ambient air surrounding Fermi 2 for radioactivity. Air sampling began in 1979 during the preoperational program. At each sampling location, a mechanical air sampler is used to draw a continuous volume of air through two filters designed to collect particulates and radioiodines. Air samples are collected weekly and analyzed for gross beta radiation and iodine-1 31 gamma radiation.
The particulate filters for each sampling location are combined on a quarterly basis to form a "composite sample" and are analyzed for gamma emitting radionuclides. There are four indicator sampling locations which were selected based on an evaluation of the predominant wind directions. A fifth sampling location is approximately fourteen miles west of the plant and is considered to be in a location unaffected by the operation of the plant. This is used as the control location.
17
Fermi 2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report Air Sampling On October 16, 1980, the People's Republic of China conducted an atmospheric nuclear weapon test. The fallout from this test was detected in Fermi 2 preoperational environmental air samples in 1981 (see Figure 2). The average gross beta for 1981 was 1.60E-I pCi/cubic meter for indicator samples and 2.40E-I pCi/cubic meter for control samples which was a factor of ten times greater than background gross beta. Gamma spectroscopic analyses of the particulate filters indicated cesium-137, cerium-141, cerium-144, ruthenium-103, ruthenium-106, zirconium-95, niobium-95, manganese-54, and antimony-125 in the atmosphere as a result of this test. In 1986, as shown in Figure 2, there was a slight increase in gross beta activity and a 2.70E-1 pCi/cubic meter "spike" in the iodine-131 activity. These elevated levels in 1986 are attributed to the nuclear accident at Chernobyl on April 26, 1986. For all other years, the iodine-131 activity was below the lower limit of detection (LLD) of 7.OE-2 pCi/cubic meter.
During 2004, two hundred and fifty-five (255) particulate air filters and charcoal cartridges were collected and analyzed for gross beta activity and iodine-131 respectively.
The average gross beta for indicator samples was 2.48E-2 pCi/cubic meter and 2.53E-2 pCi/cubic meter for control samples. The control sample collected on September 28, 2004, had a gross beta activity that was approximately 2.5 times greater than the indicating samples. This was due to agriculture activities in the area during the sampling period. None of the charcoal filters collected showed detectable levels of iodine-131.
The following table contains the annual average gross beta results of all five sample locations for 2004.
2004 Average Gross Beta Concentrations in Air Particulates (pCi/M 3 )
Table 8 Statio 3 De~scription "(secir/distance).'mi'.-AniaI Average API-1 (D)
Estral Beach (NE/1.4 mi.)
2.3 1 E-2 API-2 (D)
Site Boundary (NNW/0.6 mi.)
2.7 1E-2 API-3 (D)
Site Boundary (NW/0.6 mi.)
2.4613-2 API-4 (C)
North Custer Rd. (W/14 mi.)
2.53E-2 API-5 (I)
Site Boundary (S/1.2 mi.)
2.4513-2 (I) = Indicator Station (C) = Control Station Twenty (20) quarterly particulate filter composites were prepared and analyzed for gamma emitting radionuclides. Naturally occurring beryllium-7 was detected in both indicator and control samples.
18
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report In conclusion, the atmospheric monitoring data are consistent with preoperational and prior operational data and show no adverse long-term trends in the environment attributable to operation of Fermi 2 as illustrated in Figures 2 and 3.
IHistorical Gross Beta and Iodine-131 Activity in Air Samples 3.OE Chinese Weapons Test E 2.OE.0 1.0E-01 0.
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Fermi 2 Air Particulate Gross Beta for 2004 S
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19
Fermi2-2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Terrestrial Monitoring Radionuclides released to the atmosphere may deposit on soil and vegetation, and therefore, may eventually be incorporated into the human food chain. To assess the impact of Fermi 2 operations to humans from the ingestion pathway, samples of milk, green leafy vegetables, and groundwater are collected and analyzed for radioactivity. The following sections discuss the type and frequency of terrestrial sampling, analyses performed, and a comparison of 2004 data to previous operational and preoperational data.
Milk Sampling The milk sampling portion of the REMP is perhaps one of the most important aspects of the program. This is because a major pathway in the human food chain is the consumption of milk from grazing animals (dairy cows or goats) due to biological concentration and the short turn around time in this pathway. Milk is collected from one indicator location and one control location semimonthly when animals are in the pasture, and monthly when the animals are on stored feed. The milk is analyzed for iodine-131, gamma emitting radionuclides, and strontium-89/90. At times when milk samples are not available, grass samples are collected at both the control milk sample location and the location where milk is not available. Grass samples are analyzed for iodine-131 and other gamma emitting radionuclides.
Milk sampling began in 1979 during the preoperational program. During this time period, milk samples were analyzed for iodine-13 1 and other gamma emitting radionuclides. Cesium-137 and naturally occurring potassium-40 were the only radionuclides detected in milk samples during the preoperational program. The cesium-137 concentration averaged 3.60E+O pCi/liter and is due to past atmospheric nuclear weapons testing. In 1986, after the nuclear accident at Chernobyl, iodine-131 and cesium-137 were detected in both indicator and control milk samples. The average concentration for iodine-131 was 3.70E+0 pCi/liter and 6.60E+0 pCiAiter for cesium-137.
The analysis for strontium-89/90 began in 1988, and strontium-90 is routinely detected in both indicator and control milk samples because of past atmospheric nuclear weapons testing.
During 2004, thirty six (36) milk samples were collected and analyzed for iodine-131, gamma emitting radionuclides, and strontium-89/90. No iodine-131 was detected in any of the samples. Strontium-90 was detected in both indicator and control milk samples and is due to fallout from past atmospheric weapons testing (see Figure 4). The indicator 20
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report samples had an average strontium-90 concentration of 1.89E+0 pCi/liter and the control samples had an average concentration of 2.57E+0 pCi/liter. During 2004, no grass samples were scheduled or collected for the REMP program.
In 1970, the concentration of strontium-90 in Monroe County milk was 6.00E+0 pCi/liter according to the Michigan Department of Health's "Milk Surveillance", Radiation Data and Reports, Vol. 11-15, 1970-1974. Figure 4 shows the calculated radiological decay curve for the 1970 concentration of strontium-90 and the average concentrations since 1988. This graph illustrates that the inventory of strontium-90 in the local environment is decreasing with time and closely follows the calculated decay curve. This supports the fact that the inventory of strontium-90 in the environment is due to fallout from past atmospheric nuclear weapons testing and not the operation of Fermi 2.
Historical Strontium-90 Activity in Local Milk Samples 6.0 4.0 C. 2.0 -~f~
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Calculated Decay Figure 4 - Historical Strontium-90 Activity in Local Milk Samples; The concentration of strontium-90 in local milk samples is decreasing with time and is below the calculated decay curve. This supports the fact that strontium-90 in local milk is due to fallout from past atmospheric nuclear weapons testing and not the operation of Fermi 2.
Groundwater Sampling In areas not served by municipal water systems, water supplies for domestic use are generally obtained from private wells. The network of private wells presently in use forms the source of water for domestic and livestock purposes in farms and homes west and north of the site. However, with the construction of new water plants and distribution systems, the water use trend in the area is from groundwater to surface water.
21
Fermi2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Groundwater is collected on a quarterly basis from four wells surrounding Fermi 2. The groundwater is analyzed for gamma emitting radionuclides and tritium. Sampling location GW-4, which is located approximately 0.6 miles west northwest, is designated as the control location because it is up-gradient and is least likely to be affected by the operation of the plant. The other three sampling locations are down-gradient from Fermi 2 and designated as indicator locations.
Groundwater sampling began in 1987, during the operational period of the REMP program. From 1987 to 1996, naturally occurring potassium-40, cesium-137, and tritium were detected in both indicator and control samples. The average concentration was 7.7 1E+0 pCi/liter for cesium-137 and 1.50E+2 pCi/liter for tritium. The presence of cegium-137 and tritium in groundwater samples is due to fallout from past atmospheric nuclear weapons testing leaching into the soil and becoming incorporated into the groundwater. From 1997 to 2003, no activity was detected in groundwater samples.
In 2004, sixteen (16) groundwater samples were collected and analyzed for gamma emitting radionuclides and tritium. No activity was detected in any of these groundwater samples.
Garden Sampling Fermi 2 collects samples of broad leaf vegetables from indicator locations identified by the annual Land Use Census. Samples are also collected at a control location that is at a distance and direction which is considered to be unaffected by plant operations. Samples are collected once a month during the growing season (June through September) and are analyzed for iodine-131 and other gamma emitting radionuclides.
Vegetable sampling started in 1982. During the preoperational period from 1982 to 1985, only naturally occurring potassium-40 was detected in both indicator and control vegetable samples. During the operational period from 1985 to 1990 and 1994 to 1995, only naturally occurring potassium-40 was detected in both indicator and control vegetable samples. However, in 1991, 1992, and 1993, cesium-137 was detected in one indicator sample each year and had an average concentration of 1.2E+1 pCi/kilogram.
Cesium-1 37 may become incorporated into plants by either uptake from the soil or direct deposition on foliar surfaces. Since cesium-137 is normally not detected in gaseous effluent samples from Fermi 2, and there have been no recent atmospheric weapons testing or nuclear accidents, the incorporation of cesium-137 by direct deposition is' highly unlikely. The most probable source of cesium-137 in vegetable samples is the uptake of previously deposited cesium-137, which has leached into the soil. This cesium activity is attributed to fallout from past atmospheric weapons testing and to the nuclear accident at Chernobyl.
22
Fermi 2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report During 2004, eleven (11) vegetable samples were collected and analyzed for iodine-131 and other gamma emitting radionuclides. No iodine-131 was detected in vegetable samples during 2004. The only gamma emitting radionuclide detected was naturally occurring potassium-40.
Terrestrial monitoring results for 2004 of milk, groundwater and leafy garden vegetable samples, showed only naturally occurring radioactivity and radioactivity associated with fallout from past atmospheric nuclear weapons testing. The radioactivity levels detected were consistent with levels measured prior to the operation of Fermi 2 and no radioactivity attributable to activities at Fermi 2 was detected in any terrestrial samples.
In conclusion, the terrestrial monitoring data show no adverse long-term trends in the terrestrial environment.
Aquatic Monitoring Lake Erie, on which Fermi 2 borders, is used as a source for drinking water, as well as for recreational activities such as fishing, swimming, sunbathing, and boating. For this reason, Lake Erie and its tributaries are routinely monitored for radioactivity.
The aquatic monitoring portion of the REMP consists of sampling raw municipal drinking water, surface water, lake sediments, and fish for the presence of radioactivity.
The following sections discuss the type and frequency of aquatic sampling, analyses performed, and a comparison of 2004 data to previous operational and preoperational data.
Drinking Water Sampling Detroit Edison monitors drinking water at one control location and one indicator location using automatic samplers. The automatic samplers collect samples, known as aliquots, at time intervals that are very short (hourly) relative to the sample collection period (monthly) in order to assure that a representative sample is obtained. Indicator water samples are obtained at the Monroe water intake located approximately 1.1 miles south of the plant. Detroit municipal water is used for the control samples and is obtained at the Allen Park water intake located approximately 18.6 miles north of the plant. Drinking water samples are collected on a monthly basis and analyzed for gross beta, strontium-89/90, and gamma emitting radionuclides. The monthly samples for each location are combined on a quarterly basis and analyzed for tritium activity.
23
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report In late 1980, as shown in Figure 5, an atmospheric nuclear weapon test was conducted by the People's Republic of China. As a result of this test, the average gross beta for 1981 was 9.80E+0 pCi/liter for water samples. Figure 5 also shows that, except for the Chinese weapons testing, the historic drinking water sample data are below the lower limit of detection (4.00E+O pCi/liter) required by US Environmental Protection Agency (USEPA) National Interim Primary Drinking Water regulations. Even during the Chinese weapons testing, the drinking water samples did not exceed the USEPA maximum allowable criteria of 5.OOE+l pCi/liter gross beta. In 1980 and 1983, cesium-137 was detected in drinking water samples at levels ranging from 5.40E+0 pCi/liter to 1.90E+1 pCi/liter. Tritium was also detected during the preoperational program and had an average of 3.25E+2 pCi/liter. The presence of cesium-137 and detectable levels of tritium in these water samples is due to fallout from past atmospheric nuclear weapons testing and naturally occurring tritium.
From 1985 to 2003, the average annual gross beta activity for indicator samples was 3.37E+0 pCi/liter and 2.72E+O pCi/liter for control samples. The analysis for strontium-89/90 began in 1988, and strontium-90 has been detected in both indicator and control samples. The average strontium-90 activity for indicator samples was 7.25E-I pCi/liter and 7.56E-I pCi/liter for control samples during this time period. Tritium was also detected in both indicator and control drinking water samples during this time period.
The average tritium activity for indicator samples was 2.52E+2 pCi/liter and 2.60E+2 pCifliter for control samples. The presence of strontium-90 and detectable levels of tritium in these water samples is due to fallout from past atmospheric nuclear weapons testing and naturally occurring tritium.
In 2004, twenty-four (24) drinking water samples were collected and analyzed for gross beta, gamma emitting radionuclides, strontium-89/90, and tritium. The average gross beta for indicator samples was 4.01E+0 and 3.55E+0 pCi/liter for control samples. No gamma emitting radionuclides or strontium-89/90 activity was detected in drinking water samples during 2004. Eight (8) quarterly composite drinking water samples were prepared and analyzed for tritium. No tritium activity was detected in drinking water samples during 2004.
24
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Historical Gross Beta Activity 12.0 -
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This shows that Fermi 2 has had no measurable radiological impact on local drinking water.
Surface Water Sampling Detroit Edison monitors surface water at two locations using automatic samplers. As with drinking water, surface water samples are collected at time intervals that are very short (hourly) relative to the sample collection period (monthly) in order to assure obtaining a representative sample. Indicator surface water samples are obtained at the Fermi 2 General Service Water building, located approximately 0.3 miles south southeast from Fermi 2. The control surface water samples are obtained from Trenton Channel Power Plant's cooling water intake on the Detroit River, which is approximately 11.7 miles north northeast of Fermi 2. Surface water samples are collected on a monthly basis and analyzed for strontium-89/90 and gamma emitting radionuclides. The monthly samples for each location are combined on a quarterly basis to form a quarterly composite sample and are analyzed for tritium.
25
Fermi2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Surface water sampling began in 1979, and the samples were analyzed for gamma emitting radionuclides and tritium. During this preoperational program, no gamma emitting radionuclides, except for naturally occurring potassium-40, were detected.
Tritium was detected in both indicator and control samples during this time period and had an average concentration of 3.15E+2 pCi/liter. This tritium activity represents the background concentration due to naturally occurring tritium and tritium produced during past atmospheric nuclear weapons testing.
From 1985 to 2003, as part of the operational program, surface water samples were analyzed for gamma emitting radionuclides and tritium. The analysis for strontium-89/90 did not begin until 1988, and strontium-90 was detected in both indicator and control samples. The average strontium-90 concentration for this time period was 1.13E+0 pCi/liter. In 1990, two indicator samples showed detectable activity for cesium-137 at an average concentration of 1.20E+l pCi/liter. The presence of cesium-137 and strontium-90 in these water samples is due to fallout from past atmospheric nuclear weapons testing. Tritium was detected in both indicator and control surface water samples during this time period at a concentration of 2.31 E+2 pCi/liter. This tritium activity is consistent with background levels measured during the preoperational program.
In 2004, twenty-four (24) surface water samples were collected and analyzed for gamma emitting radionuclides and strontium-89/90. From these samples, six (6) quarterly composite samples were prepared and analyzed for tritium. During 2004, no gamma emitting radionuclides, strontium-89/90, or tritium were detected.
Sediment Sampling Sediments often act as a sink (temporary or permanent) for radionuclides, but they may also become a source, as when they are resuspended during periods of increased turbulence or are dredged and deposited elsewhere. Sediment, in the vicinity of the liquid discharge point, represents the most likely site for accumulation of radionuclides in the aquatic environment, and with long-lived radionuclides, a gradual increase in radioactivity concentration would be expected over time if discharges occur. Sediment, therefore, provides a long-term indication of change that may appear in other sample media (i.e., water and fish samples).
26
Fermi 2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report Lake Erie shoreline and bottom sediments from five locations are collected on a semiannual basis (Spring and Fall) and are analyzed for gamma emitting radionuclides and strontium-89/90. There is one control location and four indicator locations. The control sample is collected near the Trenton Channel Power Plant's cooling water intake.
The indicator samples are collected at Estral Beach, near the Fermi 2 liquid discharge area, the shoreline at the end of Pointe Aux Peaux, and Indian Trails Community Beach.
During the preoperational program, there was not a control location, and indicator samples were analyzed for gamma emitting radionuclides. During the preoperational program, except for naturally occurring radionuclides, only cesium-137 was detected in sediment samples. For this time period, the average cesium-137 concentration was 3.27E+2 pCilkilogram. The presence of cesium-137 in these sediment samples is due to fallout from past atmospheric nuclear weapons testing.
From 1985 to 2003, cesium-137, strontium-90, and naturally occurring radionuclides were detected in sediment samples. The average cesium-137 concentration was 1.37E+2 pCi/kilogram for all samples. The analysis for strontium-89/90 began in 1988, and strontium-90 has been routinely detected at similar concentrations in both indicator and control samples. The average strontium-90 activity for indicator samples was 1.80E+2 pCi/kilogram and 1.98E+2 pCi/kilogram for control samples. The presence of cesium-137 and strontium-90 in these sediment samples is due to fallout from past atmospheric nuclear weapons testing.
In 1990 and 1991, the Spring samples taken at the Fermi 2 liquid discharge line (Location S-2) showed activity for plant related radionuclides (manganese-54, cobalt-58, cobalt-60, and zinc-65) and was determined to be a result of liquid effluent from Fermi 2. The sample results were well below any regulatory reporting limits and were consistent with the activity released from the plant in liquid effluents anid the dose impact was negligible.
In 2004, ten (10) sediment samples were collected and analyzed for gamma emitting radionuclides and strontium 89/90. Cesium-137 was detected in two control samples with an average concentration of 6.48E+l pCi/kilogram and two indicator samples with an average concentration of 9.20E+l pCi/kilogram. The presence of cesium-137 in sediment samples is due to fallout from past atmospheric nuclear weapons testing.
Naturally occurring radionuclides of potassium and beryllium were also detected in sediment samples for this sampling period.
27
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Historical Cesium-137 Activity in Sediment Samples 7.0E+02 6.OE+02 E 5.oE+02 -
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Average Activity --- Calculated Trend Figure 6 - Historical Cesium-137 Activity in Sediment Samples; As the calculated trend shows, the concentration of cesium-137 in Lake Erie sediments is decreasing with time. This supports the fact that cesium-137 in Lake Erie sediments is due to fallout from past atmospheric nuclear weapons testing and not the operation of Fermi 2.
Figure 6 shows the historical concentration of cesium-137 in sediment samples from 1978 to 2004. Using the data from these years, and the statistical method of least squares, an exponential curve can be calculated that represents the cesium-137 concentration in sediment. This curve has a negative slope which indicates the overall concentration of cesium-137 in the environment is decreasing with time. This supports the fact that the inventory of cesium-137 in the environment is due to fallout from past atmospheric nuclear weapons testing and not from the operation of Fermi 2.
Fish Sampling Samples of fish are collected from Lake Erie at three locations on a semiannual basis.
There are two control locations and one indicator location. The two control locations are offshore of Celeron Island and in Brest Bay. The indicator location is approximately 1200 feet offshore of the Fermi 2 liquid effluent discharge. Edible portions of the fish are analyzed for gamma emitting radionuclides and strontium-89/90.
During the preoperational program, fish samples were analyzed for gamma emitting radionuclides. Only cesium-137 and naturally occurring potassium-40 were detected during this time period. The average concentration of cesium-137 for indicator samples was 3.53E+1 pCi/kilogram and 4.20E+1 pCi/kilogram for control samples. The presence of cesium-137 in these fish samples is due to fallout from past atmospheric nuclear weapons testing.
28
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report From 1985 to 2003, cesium-137 and naturally occurring potassium-40 were detected in fish samples. The average cesium-137 concentration for indicator samples was 3.82E+1 pCi/kilogram and 3.92E+1 pCi/kilogram for control samples. The analysis for strontium-89/90 began in 1990, and strontium-90 has been routinely detected at similar concentrations in both indicator and control samples. The average strontium-90 concentration for indicator samples was 3.84E+1 pCi/kilogram and 3.15E+1 pCi/kilogram for control samples. The presence of cesium-1 37 and strontium-90 in these fish samples is due to fallout from past atmospheric nuclear weapons testing.
In 2004, twenty-three (23) fish samples were collected and analyzed for gamma emitting radionuclides and strontium-89/90. Only naturally occurring potassium-40 was detected in fish samples for 2004.
Aquatic monitoring results for 2004 of water, sediment, and fish showed only naturally occurring radioactivity and radioactivity associated with fallout from past atmospheric nuclear weapons testing and were consistent with levels measured prior to the operation of Fermi 2. In conclusion, no radioactivity attributable to activities at Fermi 2 was detected in any aquatic samples during 2004 and no adverse long-term trends are shown in the aquatic monitoring data.
29
Fermi2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report Land Use Census The Land Use Census is conducted in accordance with the Fermi 2 Offsite Dose Calculation Manual (ODCM), control 3.12.2, and satisfies the requirements of Section IV.B.3 of Appendix I to 10 CFR Part 50. This census identifies changes in the use of unrestricted areas to permit modifications to monitoring programs for evaluating doses to individuals from principal pathways of exposure. The pathways of concern are listed below:
- Inhalation Pathway - Internal exposure as a result of breathing radionuclides carried in the air.
- Ground Exposure Pathway - External exposure from radionuclides deposited on the ground.
- Plume Exposure Pathway - External exposure directly from a plume or cloud of radioactive material.
- Vegetation Pathway - Internal exposure as a result of eating vegetables which have absorbed deposited radioactive material or which have absorbed radionuclides through the soil.
- Milk Pathway - Internal exposure as a result of drinking milk which may contain radioactive material as a result of dairy animals grazing on a pasture contaminated by radionuclides.
The Land Use Census is conducted during the growing season and is used to identify, within a radius of 5 miles, the location of the nearest residences, milk animals, meat animals, and gardens (greater than 50 square meters and containing broad leaf vegetation) in each of 16 meteorological sectors surrounding Fermi 2. -Gardens greater than 50 square meters are the minimum size required to produce the quantity (26 kg/year) of leafy vegetables assumed in NRC Regulatory Guide 1.109 for consumption by a child. To determine this minimum garden size, the following assumptions were made: (1) 20% of the garden is used for growing broad leaf vegetation (i.e., lettuce and cabbage); and (2) a vegetation yield of 2 kg/square meter.
30
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report 2004 Land Use Census Results The Land Use Census is conducted in accordance with ODCM control 3.12.2 and satisfies the requirements of Section IV.B3.3 of Appendix I to 10 CFR Part 50. This census identifies changes in the use of unrestricted areas to permit modifications to monitoring programs for evaluating doses to individuals from principal pathways of exposure. The annual Land Use Census is conducted during the growing season and is used to identify, within a radius of 5 miles, the location of the closest residences, milk animals, meat animals, and gardens in each of the 16 meteorological sectors surrounding Fermi 2.
The 2004 Land Use Census was performed during the month of August. The 2004 census data were obtained with the use of a hand-held Global Positioning System (GPS).
These data were compared to the 2003 data to determine any significant changes in the use of the land. The results of the census are tabulated in Tables 9 - 12 of this report.
No significant changes in the land use between 2003 and 2004 were found that would require changing the location of the "maximum exposed individual". There were no changes in the category of closest residences. However, there were slight changes in three meteorological sectors in the category of closest gardens. See Table 10 for these changes. The "maximum exposed individual" is located in the West-North-West sector and no longer participates in the REMP program. However, the location still maintains a potential for a garden. In the category of closest milk locations, one new goat location was identified in the north northwest sector. All milk locations identified are not used for human consumption. There were no changes in the category of closest meat locations in 2004. As with past surveys, this census identified new residential housing construction that shows a continuing trend of converting agricultural land to other uses in the area surrounding Fermi 2.
As stated above, there were no significant changes in the 2004 land use that would require changing the location of the "maximum exposed individual". For that reason, the location of "maximum exposed individual" remains the same and is described as follows:
Azimuth Distance Age Maximum Pathway Sector (degrees)
(meters)
Group Organ Ingestion WNW 303.5 1103 Child Thyroid (vegetation) 31
Fermi 2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report 2004 LAND USE CENSUS Closest Residences Table 9 I Year l
Sector l
2003 2004 NE NE 2003 2004 2003 2004 2003 2004 2003 2004 2003 (a) 2004 2003 2004 2003 2004 2003 2004 2003 2004 2003 2004 NNE NNE N
N NNW NNW NW NW WNW WNW W
Ws.
S ESE-SSE Azimuth (degrees) l 34.7 34.7 11.2 11.2 7.7 7.7 332.8 332.8 309.9 309.9 303.5 303.5 258.3 258.3 238.2 238.2 230.3 230.3 200.4 200.4 170.0 170.0 Distance (meters) 1773 1773 1646 1646 1776 1776 1743 1743 1700 1700 1103 1103 1861 1861 2547 2547 2025 2025 1826 1826 1640 1640 Change I
(meters)
Lake Erie N/A (a) = Location of "maximum exposed individual" 32
Fermi 2-2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report 2004 LAND USE CENSUS Closest Gardens Table 10 l
l l
Distance Change Year I
Sector I Azimuth (degrees) I (meters)
I (meters) 2003 2004 NE NE 2003 2004 NNE NNE 2003 2004 N
N 2003 2004 NNW NNW 2003 2004 NW NW 39.7 39.7 30.6 31.3 0.54 0.54 333.2 326.6 323.4 319 300.2 300.2 267.0 267.0 250.7 250.7 233.9 233.9 195.9 195.9 3200 3200 2894 3085 2633 2633 4107 2260 4436 3774 2936 2936 2748 2748 3845 3845 7062 7062 2414 2414
'0
+191 0
-1847
-662 0
0 0
0 0
2003 2004 WNW WNW 2003 2004 W
W 2003 2004 WSW WSW 2003 2004 SW SW 2003 2004 SSW SSW 2003 2004 S
S None None N/A ESE-SSE Lake Erie N/A 33
Fermi2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report 2004 LAND USE CENSUS Milk Locations Table 11 l
I Distance Type/Change I Year I
Sector I Azimuth (degrees) I (meters)
I (meters)
I 2003 2004 NE NE None None N/A 2003 2004 NNE NNE None None N/A 2003 2004 N
N 2003 2004 NNW NNW 1.1 1.1 None 329.3 310.5 310.5 301.0 301.0 2899 2899 4870 5874 5874 3672 3672 Goat 0
Goat N/A Cow/Goat 0
Goat 0
2003 2004 NW NW 2003 2004 WNW WNW 2003 2004 W
W None None N/A 2003 2004 WSW WSW None None N/A 2003 2004 SW SW None None N/A 2003 2004 SSW SSW' None None N/A 2003 2004 S
S None None N/A ESE-SSE Lake Erie N/A 34
Fermi 2-2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report 2004 LAND USE CENSUS Closest Meat Locations Table 12 Ya llDistance Type/Change Year Sector Azimuth (degrees)
(meters)
(meters) 2003 2004 NE NE None None N/A 2003 2004 2003 2004 NNE NNE N
N NNW NNW NW NW None None N/A None None N/A 2003 2004 2003 2004 338.4 338.4 310.5 310.5 285.6 285.6 7079 7079 5874 5874 2602 2602 Sheep 0
Sheep 0
Beef 0
2003 2004 2003 2004 2003 2004 2003 2004 W
W WSW WSW SW SW S
S ESE - SSE None None 248.8 248.8 4734 4734 Beef 0
N/A None None N/A 2003 2004 None None N/A 2003 2004 None None N/A N/A Lake Erie 35
Appendix A Sampling Locations
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Direct Radiation Sample Locations Table A-1 Meteorological Distance Station Sector/Azimuth from Reactor Collection Number (Degrees)
(Approx.)
Description Frequency Type TI NE/380 1.3 mi.
Estral Beach, Pole on Q
I Lakeshore 23 Poles S of Lakeview. (Special Area)
T2 NNE/220 1.2 mi.
Pole at termination of Q
I Brancheau St.
(Special Area)
T3 N190 1.1 mi.
Pole, NW corner of Swan Q
I Boat Club fence. (Special Area)
T4 NNW/337 0 0.6 mi.
Site boundary and Toll Rd.
Q I
on Site fence by API #2.
T5 NW/3130 0.6 mi.
Site boundary and Toll Rd.
Q I
on Site fence by API #3.
T6 WNW/2940 0.6 mi.
On Site fence at south end Q
I
-of N. Bullet Rd.
T7 W/2700 14.0 mi.
Pole, at Michigan Gas Q
C substation on N. Custer Rd., 0.66 miles west of Doty Rd.
T8 NW/3050 1.9 mi.
Pole on Post Rd. near NE Q
I corner of Dixie Hwy. and Post Rd.
T9 NNW/3340 1.5mi.
Pole, NWcornerof Q
I Trombley and Swan View Rd.
T10 N/6° 2.1 mi.
Pole, S side of Massarant-Q I
2 poles W of Chinavare.
I= Indicator C= Control 0 = On-site Q = Quarterly A-l
Fermi2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Direct Radiation Sample Locations (Table A-i continued)
Meteorological Distance Station Sector/Azimuth from Reactor Collection Number (Degrees)
(Approx.)
Description Frequency Type TII NNE/230 6.2 mi.
Pole, NE corner of Q
I Milliman and Jefferson.
T12 NNE/290 6.3 mi.
Pointe Mouille Game Area Q
I Field Office, Pole near tree, N area of parking lot T13 N/3560 4.1 mi.
Labo and Dixie Hwy. Pole Q
I on SW corner with light.
T14 NNW/3370 4.4 mi.
Labo and Brandon Pole on Q
T15 NW/3150 3.9 mi.
Pole, behind building at Q
I the corner of Swan Creek and Mill St.
T16 WNW/2830 4.9 mi.
Pole, SE comer of War and Q
I Post Rd.
T17 W/2710 4.9 mi.
Pole, NE corner of Nadeau Q
I and Laprad near mobile home park. -
T18 WSWt2470 4.8 mi.
Pole, NE corner of Mentel Q
I and Hurd Rd.
T19 SW/2360 5.2 mi.
Fermi siren pole on Q
I Waterworks Rd. NE corner of intersection - Sterling State Park Rd. Entrance Drive/Waterworks.
T20 WSW/257° 2.7 mi.
Pole, S side of Williams Q
I Rd, 8 poles W of Dixie Hwy. (Special Area)
T21 WSW/2390 2.7 mi.
Pole, N side of Pearl at Q
I Parkview Woodland Beach. (Special Area)
I = Indicator C = Control 0 = On-site Q = Quarterly A-2.
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Direct Radiation Sample Locations (Table A4i continued)
Meteorological Distance Station Sector/Azimuth from Reactor Collection Number (Degrees)
(Approx.)
Description Frequency Type T22 S/1720 1.2 mi.
Pole, N side of Pointe Aux Q
I Peaux 2 poles W of Long -
Site Boundary.
T23 SSW/1950 1.1 mi.
Pole, S side of Pointe Aux Q
I Peaux I pole W of Huron next to Vent Pipe - Site Boundary.
T24 SW/2250 1.2 mi.
Fermi Gate along Pointe Q
I Aux Peaux Rd. on fence wire W of gate Site Boundary.
T25 WSW/252 0 1.4 mi.
Pole, Toll Rd. - 12 poles S Q
I of Fermi Drive.
T26 WSW/2590 1.1 mi.
Pole, Toll Rd. -6 poles S Q
I of Fermi Drive.
T27 SW/2250 6.8 mi.
Pole, NE corner of Q
I McMillan and East Front St. (Special Area)
T28 SW/2290 10.7 mi.
Pole, SE corner of Mortar Q
C Creek and LaPlaisance.
T29 WSW/2370 10.3 mi.
Pole, E side of S Dixie, I Q
C pole S of Albain.
T30 WSW/2470 7.8 mi.
Pole, St. Mary's Park Q
I corner of Elm and Monroe St., S side of parking lot next to river. (Special Area)
T31 WSW/2550 9.6mi.
IstpoleWofentrance Q
C drive Milton "Pat" Munson Recreational Reserve on North Custer Rd.
I = Indicator C = Control 0 = On-site Q = Quarterly A-3
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Direct Radiation Sample Locations (Table A-l continued)
Meteorological Distance Station Sector/Azimuth from Reactor Collection Number (Degrees)
(Approx.)
Description Frequency Type T32 WNW/2950 10.3 mi.
Pole, corner of Stony Creek Q
I and Finzel Rd.
T33 NW/317° 9.2 mi.
Pole, W side of Grafton Q
I Rd. 1 pole N of Ash and Grafton intersection.
T34 NNW/338° 9.7 mi.
Pole, W side of Port Creek, Q
I I pole S of Will-Carleton Rd.
T35 N/3590 6.9 mi.
Pole, S Side of S Huron Q
I River Dr. across from Race St. (Special Area)
T36 N/3580 9.1 mi.
Pole, NE corner of Q
I Gibraltar and Cahill Rd.
T37 NNE/21° 9.8 mi.
Pole, S comer of Adams Q
I and Gibraltar across from Humbug Marina.
T38 WNWl2940 1.7 mi.
Residence - 6594 N. Dixie Q
I Hwy.
T39 S/176° 0.3 mi.
SE corner of Protected Q
0 Area Fence (PAF).
T40 S/1700 0.3 mi.
Q 0
T41 SSE/161° 0.2 mi.
Midwaybetween OBA and Q
0 Shield Wall on PAF.
T42 SSE/1490 0.2 mi.
Midway along Shield Wall Q
0 on PAF.
T43 SE/1310 0.1 mi.
Midway between Shield Q
0 Wall and Aux Boilers on PAR.
T44 ESE1109° 0.1 mi.
Opposite OSSF door on Q
0 PAR.
I= Indicator C= Control 0 = On-site Q = Quarterly A-4
Fermi 2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report Direct Radiation Sample Locations (Table A-I continued)
Meteorological Distance Station Sector/Azimuth from Reactor Collection Number (Degrees)
(Approx.)
Description Frequency Type T45 E/860 0.1 mi.
NE Comer of PAF.
Q 0
T46 ENE/670 0.2 mi.
NE side of barge slip on Q
0 fence.
T47 S/1850 0.1 mi.
South of Turbine Bldg.
Q 0
rollup door on PAF.
T48 SW/2350 0.2 mi.
30 ft. from comer of AAP Q
0 on PAF.
T49 WSW/2510 1.1 mi.
Comer of Site Boundary Q
I fence north of NOC along Critical Path Rd.
T50 W/2700 0.9 mi.
Site Boundary fence near Q
I main gate by the south Bullet Street sign.
T51 N/30 0.4 mi.
Site Boundary fence north Q
0 of north Cooling Tower.
T52 NNE/200 0.4 mi.
Site Boundary fence at the Q
0 comer of Arson and Tower.
T53 NE/550 0.2 mi.
Site Boundary fence east of Q
0 South Cooling Tower.
T54 S/189° 0.3 mi.
Pole next to Fermi 2 Q
0 Visitors Center.
T55 WSW/2510 3.3 mi.
Pole, north side of Nadeau Q
I Rd. across from Sodt Elementary School Marquee.
T56 WSW/2560 2.9 mi.
Pole, entrance to Jefferson Q
I Middle School on Stony Creek Rd.
I = Indicator C = Control 0 = On-site Q = Quarterly A-5
Fermi2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Direct Radiation Sample Locations (Table A-i continued)
Meteorological Distance Station Sector/Azimuth from Reactor Collection Number (Degrees)
(Approx.)
Description Frequency Type T57 Wt260" 2.7 mi.
Pole, north side of Q
I Williams Rd. across from Jefferson High School entrance.
T58 WSW/2490 4.9 mi.
Pole west of Hurd Q
I Elementary School Marquee.
T59 NW/325° 2.6 mi.
Pole north of St. Charles Q
I Church entrance on Dixie Hwy.
T60 NNW/341° 2.5mi.
lstpolenorthofNorth Q
I Elementary School entrance on Dixie Hwy.
T61 W1268° 10.1 mi.
Pole, SW corner of Stewart Q
I and Raisinville Rd.
T62 SW1232° 9.7 mi.
Pole, NE corner of Albain Q
I and Hull Rd.
T63 WSW/245° 9.6 mi.
Pole, NE corner of Dunbar Q
I and Telegraph Rd.
T64 WNW/286° 0.2 mi.
West of switchgear yard on Q
0 PAF.
T65 NW/322° 0.1 mi.
PAF switchgear yard area Q
0 NW of RHR complex.
T66 NE/50° 0.1 mi.
Behind Bldg. 42 on PAF.
Q 0
T67 NNW/338° 0.2 mi.
Site Boundary fence West Q
0 of South Cooling Tower.
I = Indicator C = Control 0 = On-site Q = Quarterly A-6
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Air Particulate and Air Iodine Sample Locations Table A-2 Meteorological Distance Station Sector/Azimuth from Reactor Collection Number (Degrees)
(Approx.)
Description Frequency Type API-I NE/390 1.4 mi.
Estral Beach Pole on W
I Lakeshore, 18 Poles S of Lakeview (Nearest Community with highest XIQ).
API-2 NNW/3370 0.6 mi.
Site Boundary and Toll W
I Road, on Site Fence by T-4.
API-3 NW/3130 0.6 mi.
Site Boundary and Toll W
I Road, on Site Fence by T-5.
API.4 W/2700 14.0 mi.
Pole, at Michigan Gas W
C substation on N. Custer Rd., 0.66 miles west of Doty Rd.
API-S S/1880 1.2 mi:
Pole, N corner of Pointe W
I Aux Peaux and Dewey Rd.
I = Indicator C = Control W = Weekly Milk Sample Locations Table A-3 Meteorological Distance Station Sector/Azimuth from Reactor Collection Number (Degrees)
(Approx.)
Description Frequency Type M-2 M-8 NW/3190
'WNW/289 0 5.4 mi.
9.9 mi.
Reaume Farm - 2705 E Labo.
Calder Dairy - 9334 Finzel Rd.
M-SM M-SM I
C I = Indicator C = Control M = Monthly SM = Semimonthly A-7
Fermi 2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report Garden Sample Locations Table A-4 Meteorological Distance Station Sector/Azimuth from Reactor Collection Number (Degrees)
(Approx.)
Description Frequency Type FP-1 NNE/21 3.8 mi.
9501 Turnpike Highway.
M I
FP-9 W/2610 10.9 mi.
4074 North Custer Road.
M C
I = Indicator C = Control M = Monthly (when available)
Drinking Water Sample Locations Table A-5 Meteorological Distance Station Sector/Azimuth from Reactor Collection Number (Degrees)
(Approx.)
Description Frequency Type DW-1 S/1740 1.1 mi.
Monroe Water Station N M
Side of Pointe Aux Peaux 1/2 Block W of Long Rd.
DW-2 N/80 18.5 mi.
Detroit Water Station M
C 14700 Moran Rd, Allen Park.
I = Indicator C = Control
.M = Monthly A-8
Fermi 2 - 2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report Surface Water Sample Locations Table A-6 Meteorological Distance Station Sector/Azimuth from Reactor Collection Number (Degrees)
(Approx.)
Description Frequency Type SW-2 NNE/2 0° 11.7 mi.
DECo's Trenton Channel M
C Power Plant Intake Structure (Screenhouse #1).
SW-3 SSE/16 00 0.2 mi.
DECO's Fermi 2 General M
I Service Water Intake Structure.
I = Indicator C = Control M = Monthly Groundwater Sample Locations Table A-7 Meteorological Distance Station Sector/Azimuth from Reactor Collection Number (Degrees)
(Approx.)
Description Frequency Type GW-l S/1750 0.4 mi.
Approx. IOOftWof Lake Q
I Erie, EF-1 Parking lot near gas fired peakers.
GW-2 SSW/28 0 1.0 mi.
4 ft S of Pointe Aux Peaux Q
I (PAP) Rd. Fence 427 ft W of where PAP crosses over Stoney Point's Western Dike.
GW-3 SW/2260 1.0 mi.
143 ft W of PAP Rd. Gate, Q
I 62 ft N of PAP Rd. Fence.
GW-4 WNW/2990 0.6 mi.
42 ft S of Langton Rd,8 ft Q
C E of Toll Rd. Fence.
I = Indicator C = Control Q = Quarterly A-9
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Sediment Sample Locations Table A-8 Meteorological Distance Station Sector/Azimuth from Reactor Collection Number (Degrees)
(Approx.)
Description Frequency Type S-1 SSE/I 650 0.9 mi.
Pointe Aux Peaux, SA I
Shoreline to 500 ft offshore sighting directly to Land Base Water Tower.
S-2 E/810 0.2 mi.
Fermi 2 Discharge, approx.
SA I
200 ft offshore.
S-3 NE1390 1.1 mi.
Estral Beach, approx. 200 SA I
ft offshore, off North shoreline where Swan Creek and Lake Erie meet.
S-4 WSW/2410 3.0 mi.
Indian Trails Community SA I
Beach.
S-5 NNE/200 11.7 mi.
DECo's Trenton Channel SA C
Power Plant intake area.
I = Indicator C = Control SA = Semiannually Fish Sample Locations Table A-9 Meteorological Distance Station Sector/Azimuth from Reactor Collection Number (Degrees)
(Approx.)
Description Frequency Type F-i NNE/310 9.5 mi.
Near Celeron Island.
SA C
F-2 E/860 0.4 mi.
Fermi 2 Discharge (approx.
SA I
1200 ft offshore).
F-3 SW/227° 3.5 mi.
Brest Bay.
SA C
I = Indicator C = Control SA = Semiannually A-10
MAP -
1 SAMPLING LOCATIONS BY STATION NUMBER WITHIN 1 MILE N
LEGEND C T-DIRECT RADIATION O API-AIR PARTICULATES/AIR IODINE A S-SEDIMENTS A DW/SW-DRINKING WATER/SURFACE WATER A GW-GROUND WATER DM-MILK E FP-FOOD PRODUCTS
- F-FISH 0
0.5 SCALE IN MILES
MAP - 2 SAMPLING LOCATIONS BY STATION NUMBER (1 To 5 MILES)
N LEGEND o T-DIRECT RADIATION O API-AIR PARTICULATES/AIR IODINE A S-SEDIMENTS A DW/SW-DRINKING WATER/SURFACE WATER Ei GW-GROUND WATER o M-MILK ED FP-FOOD PRODUCTS
- F-FISH 0
I SCALE IN MILES
MAP -
3 SAMPLING LOCATIONS BY STATION NUMBER (GREATER THAN 5 MILES)
N LEGEND N
V I-DIRECT RADIATION O API-AIR PARTICULATES OR AIR IODINE A S-SEDIMENTS A DW/SW-DRINKING WATER/SURFACE WATER E GW-GROUND WATER o M-MILK F FP-FOOD PRODUCTS
- F-FISH 5
0 5
10 SCALE IN MILES
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Appendix B Environmental Data Summary
Fermi 2 - 2004 Annual Radioactive fflutent Release and Radiological Environmental Operating Report Table B-I Radiological Environmental Monitoring Program Summary Name of Facility: Enrico Fermi Unit 2 Location of Facility: 30 miles southeas Docket No.: 50-341 t of Detroit, Michigan (Frenchtown Township)
Reporting Period: January-December 2004 to Location w.."-ith Highest
' SaipleTye Type and Annual Mean" :
'ontrol'
-Nu xrof (UUIts)
- Nmber of Locatons
on Locations -
9Ai'lysis LL
-Me" and Range Locaiion -
and Range' Meana dRaie e:'
' Rest a
Direct Radiation Gamma (TLD) 1.0 14.6 (177/177)
T-49, (Indicator) 19.0 (4/4) 14.3 (16/16)
None mR/srd qtr 193 9.5 to 21.3 14.8 to 21.3 11.6 to 17.0 Airborne Gross Beta 255 I.OOE-2 2.48E-2 (204/204)
API-2 (Indicator) 2.71E-2 (51/51) 2.53E-2 (51/51)
None Particulates 8.0013-3 to 6.31 E-2 8.OOE-3 to 6.3 IE-2 1.03E-3 to 8.47E-2 pCi/cl. m.
Gamma Spec. 20 Be-7 N/A 9.67E-2 (14/16)
API-2 (Indicator) 1.14E-1 (4/4) 1.13E-1 (3/4)
None 6.5013-2 to 1.72E-1 7.50E-2 to 1.72E-I 8.70E-2 to 1.31 E-I K-40 N/A
<MDA
<MDA None Mn-54 N/A
<MDA
<MDA None Co-58 N/A
<MDA
<MDA None Fe-59 N/A
<MDA
<MDA None Co-60 N/A
<MDA
<MDA None 7n-65 N/A
<MDA
<MDA None Zr-95 N/A
<MDA
<MDA None Ru-103 N/A
<MDA
<MDA None Ru-106 N/A
<MDA
<MDA, None Cs-134 5.OOE-2
<MDA
<MDA None Cs-137 6.00E-2
'MDA
<MDA None Ba-140 N/A
<MDA
<MDA None La-140 N/A.
<MDA
<MDA None Cc-141 N/A
<MDA
<MDA None Ce-144 N/A
<MDA
<MDA None Airborne Iodine 1-131 255 7.0013-2
<MDA
<MDA None pCi/cu. m.
B-I
Fermni 2 - 2004 Annual Radioactive E-ffluent Release and Radiological Environmental Operating Report Reporting Period: January - December 2004 Table B-I Radiological Environmental Monitoring Program Summary (cont.)
Name of Facility: Enrico Fermi Unit 2 Docket No.: 50-341 Location of Facility: 30 miles southeast of Detroit, Michigan (Frenchtown Township)
,,ti.
LctonWithHighet ypSa e
Tpe and C ontrol
,i - ndea or ;.'
Ainn aIMeat ',
C nt 1
Ninhbefb (Units) "
, - Numberof L
I Locations on,
,te,
' ina'iss LL)
Mean and "nge L'catlo Mea a d Range kesults' Milk 1-131 36 1.OOE+0
<MDA
<MDA None pCi/O Sr-89 36 N/A
<MDA
<MDA None Sr-90 N/A 1.89E+0 (6/18)
M-8 (Control) 2.57E+0 (2/18) 2.57E+O (2/18)
None 1.46E+0 to 2.63E+0 2.31 E+O to 2.82E+0 2.31 E+O to 2.82E+O Gamma Spec. 36 Be-7 N/A
<MDA
<MDA None K-40 N/A 1.42E+3 (18/18)
M-2 (Indicator) 1.42E+3 (18/18) 1.40E+3 (18/18)
None 1.26E+3 to 1.56E+3 1.26E+3 to 1.56E+3 1.30E+3 to 1.57E+3 Mn-54 N/A
<MDA
<MDA None Co-58 N/A
<MDA
<MDA None Fe-59 N/A
<MDA
<MDA None Co-60 N/A
<MDA
<MDA None 7n-65 N/A
<MDA
<MDA None Zr-95 N/A
<MDA
<MDA None Ru-103 N/A
<MDA
<MDA None Ru-106 N/A'
<MDA
<MDA None Cs-134 1.50E+1
<MDA
<MDA None Cs-137 1.80E+I
<MDA
<MDA None Ba-140 1.50E+1
<MDA
<MDA None La-140 I.50E+l
<MDA
<MDA None Ce-141 N/A
<MDA
<MDA None Ce-144 N/A
<MDA
<MDA None Vegetation 1-131 11 6.00E+I
<MDA
<MDA None pCi/kg wvet Gamma Spec. 11 Be-7 N/A
<MDA
<MDA None K-40 N/A 3.93E+3 (6/6)
FP-9 (Control) 4.57E+3 (5/5) 4.57E+3 (5/5)
None 2.76E+3 to 5.40E+3 I 2.79E+3 to 6.74E+3 2.79E+3 to 6.74E+3 I B-2
F ermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Reporting Period: January - December 2004 Table B-I Radiological Environmental Monitoring Program Summary (cont.)
Name of Facility: Enrico Fermi Unit 2 Docket No.: 50-341 Location of Facility: 30 miles southeast of Detroit, Michigan (Frenchtown Township)
.Sa m le t pe I dica or -
.~:.ocation w ith H igh est ;
' 'S ie:.t:Ytor In2 i o
Men I
'ntl s'
(rt);'.-;Numbei of
,i ns'
,o
,,s,,,,
- _; N^ton-i'ut ri,-;,,,{
- i:-
'Aalysis.-
LL-
':ean andRange atorR Mge n
dajd
- - kest Vegetation Mn-54 N/A
<MDA
<MDA None (cont.)
Co-58 N/A
<MDA
<MDA None pCikg wvet Fe-59 N/A
<MDA
<MDA None Co-60 N/A
<MDA
<MDA None Zn-65 N/A
<MDA
<MDA None Zr-95 N/A
<MDA
<MDA None Ru-103 N/A
<MDA
<MDA None Ru-106 N/A
<MDA
<MDA None Cs-134 6.00E+I
<MDA
<MDA None Cs-137 8.OOE+Il
<MDA
<MDA None Ba-140 N/A
<MDA
<MDA None La-140 N/A
<MDA
<MDA N6ne Ce-141 N/A
<MDA
<MDA None Ce-144 N/A
<MDA
<MDA None Drinking Water Gross Beta 24 4.OOE+0 4.01E+0 (6/12)
DW-I (Indicator) 4.01E+0 (6/12) 3.55E+0 (5/12)
None pCVI.
3.18E+0 to 4.90E+0 3.18E+0 to 4.90E+0 2.06E+0 to 4.20E+O Sr-89 24 N/A
<MDA
<MDA None Sr-90 N/A
<MDA eMDA None Gamma Spec. 24 Be-7 N/A
<MDA eMDA None K-40 N/A
<MDA
<MDA None Cr-51 N/A
<MDA
<MDA None Mn-54 1.50E+I
<MDA
<MDA None Co-58 1.50E+l
<MDA
<MDA None Fe-59 3.00E+I
<MDA
<MDA None Co:60 1.50E+ 1
<MDA
<MDA None Zn-65 3.00E+I
<MDA
<MDA None Zr-95 I.50E+l
<MDA
<MDA None B-3
Fermni 2 - 2004 Annual Radioactive E-ffluent Release and Radiological Environmental Operating Report Table B-l Radiological Environmental Monitoring Program Summary (cont.)
Name of Facility: Enrico Fermi Unit 2 Location of Facility: 30 miles southeas Docket No.: 50-341 t or Detroit, Michigan (Frenchtown Township)
Reporting Period: January - December 2004
,.;- -~
Location wit Highest ^-
,Sampie Type
.,Type and '
',Idicator" Anni a Mean Co'itro i'umer 'f (Units)
'Number of Locations Locatio N
'f ' Nii-otin t
--- :M i
a
Aahd Range '
Lodation Mean and kig an and nge "
Drinking Water Ru-103 N/A
<MDA
<MDA None (cont.) pCi/l Ru-106 N/A
<MDA
<MDA None Cs-134 I.50E+I
<MDA
<MDA None Cs-137 1.80E+Il
<MDA
<MDA None Ba-140 I.50E+I
<MDA
<MDA None La-140 1.50E+I
<MDA
<MDA None Ce-141 N/A
<MDA
<MDA None Ce-144 N/A
<MDA
<MDA None 11-3 8
2.OOE+3
<MDA
<MDA None Surface Water Sr-89 24 N/A
<MDA
<MDA None pCi/i Sr-90 N/A
<MDA
<MDA None Gamma Spec. 24 Be-7 N/A
<MDA
<MDA None K40 N/A
<MDA
<MDA None Cr-51 N/A
<MDA
<MDA None Mn-54 1.50E+I
<MDA
<MDA None Co-58 1.50E+Il
<MDA
<MDA None Fe-59 3.OOE+I
<MDA
<MDA None Co-60 I.50E+I
<MDA
<MDA None Zn-65 3.OOE+ I
<MDA
<MDA None Zr-95 I.50ES+I1
<MDA
<MDA None Ru-103.
N/A
<MDA
<MDA None Ru-106 N/A
<MDA
<MDA None Cs-134 1.50E+I
<MDA
<MDA None Cs-137 1.80E+I
<MDA
<MDA None Ba-140 1.50E+Il
<MDA
<MDA None La-140 I.50E+I
<MDA
<MDA None Ce-141 N/A
<MDA
<MDA None I
B-4
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological lEnvironmental Operating Report Reporting Period: January - December 2004 Table B-I Radiological Environmental Monitoring Program Summary (cont.)
Name of Facility: Enrico Fermi Unit 2 Docket No.: 50-341 Location of Facility: 30 miles southeast of Detroit, Michigan (Frenchtown Township)
,:SanpldType
.,.,,,.,Type and
,n icator cation, ii eu of Anaysis LD M an and Ringe.
Locatio' Mea and Range Mea and Range '
,esuit Surface Water Ce-144 N/A
<MDA
<MDA None (cont.) pCi/l H-3 8
2.00E1+3
<MDA
<MDA None Groundwater Gamma Spec. 16 pCZQ Be-7 N/A
<MDA
<MDA None K-40 N/A
<MDA
<MDA None Cr-SI N/A
<MDA
<MDA None Mn-54 1.50E+I
<MDA
<MDA None Co-58
,.SOE+I
<MDA
<MDA None Fe-59 3.OOE+I
<MDA
<MDA None Co-60 1.50E+I
<MDA
<MDA None Zn-65 3.00E+1
<MDA
<MDA None Zr-95 I.SOE+5 I
<MDA
<MDA None Ru-103 N/A
<MDA
<MDA None Ru-106 N/A
<MDA
<MDA None Cs-134 I.SOE+5 I
<MDA
<MDA None Cs-137 1.80E+1
<MDA
<MDA None Ba-140 I.50E+I
<MDA
<MDA None La-140 1.SOE+1I
<MDA
<MDA None Ce-141 N/A
<MDA
<MDA None Ce-144 N/A
<MDA
<MDA None H-3 16 2.00E+3
<MDA
<MDA None Sediment Sr-89 10 N/A
<MDA
<MDA pCi/kg dry Sr-90 N/A
<MDA
<MDA None Gamma Spec. 10 Be-7 N/A
<MDA S-S (Control) 5.90E+2 (1/2) 5.90E+2 (1/2)
None K-40 N/A I.OIE+4 (8/8)
S-I (Indicator) 1.16E13+4 (2/2) 1.02E1+4 (2/2) 7.42E1+3 to 1.39E+4 1.06E+4 to 1.25E+4 9.85E+3 to l.OSE+4 None B-S
Table B-I Radiological Environmental Monitoring Program Summary (cont.)
Name of Facility: Enrico Fermi Unit 2 Docket No.: 50-341 Location of Facility: 30 miles southeast of Detroit, Michigan (Frenchtown Township)
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Reporting Period: January - December 2004
- IndcaorLiocationi With Highesr,-
'Sample Type Type and Aninual Mean-ont1; Number of'
("nits).'
Number of
'Loca nsaions
.A.
Non-rout'ne Ana i.'
n s-- -
'Me n'nd R n'e :' '
Loc'tion MeI d afd Range
'-Mean d
e'ii '
- .;.. esui 2<.
Sediment (cont.)
Mn-54 N/A
<MDA
<MDA None pCi/kg dry Co-58 N/A
<MDA
<MDA None Fe-59 N/A
<MDA
<MDA None Co-60 N/A
<MDA
<MDA None Zn-65 N/A
<MDA
<MDA None Zr-95 N/A
<MDA
<MDA None Ru-103 N/A
<MDA
<MDA None Ru-106 N/A
<MDA
<MDA None Cs-134 1.50E+2
<MDA
<MDA None Cs-137 1.80E+2 6.09E+1 (2/8)
S-3 (Indicator) 7.00E+1 (1/2)
'6.48E+1 (2/2)
None 5.17E+1 to 7.00E+1 5.058+1 to 7.908+1 Ba-140 N/A
<MDA
<MDA None La-140 N/A
<MDA
<MDA None Ce-141 N/A
<MDA
<MDA None Ce-144 N/A
<MDA
<MDA None Fish Sr-89 23 N/A
<MDA
<MDA None pCi/g wvet Sr-90 N/A
<MDA
<MDA None Gamma Spec. 23 Be-7 N/A MdDA
<MDA None K-40 N/A 2.78E+3 (11/11)
F-3 (Control) 2.85E+3 (7n) 2.828+3 (12/12)
None 2.24E+3 to 3.76E+3 1.938+3 to 3.69E+3 1.938+3 to 3.69E+3 Mn-54 1.30E+2
<MDA
<MDA None Co-58 1.30E+2
<MDA
<MDA None Fe-59 2.60E+2
<MDA
<MDA None Co-60 1.308+2
<MDA
<MDA None Zn-65 2.60E+2
<MDA
<MDA None B-6
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Reporting Period: January - December 2004 Table B-I Radiological Environmental Monitoring Program Summary (cont.)
NameofFacility: Enrico Fermi Unit 2 Docket No.: 50-341 Location of Facility: 30 miles southeast of Detroit, Michigan (Frenchtown Township)
'-Loca, ction With Highest' v;d
'I icator:
-Adn'ta iMean '
et, C'ontrol:m
'(Units)
Numberof Locatons t !
i No.--t;.
Anysi L-'Ud
' Mean a e
Lo'an
'Mcan and an n
e mesits-'
Fish (cont.)
Zr-95 N/A
<MDA
<MDA None -
pCi/kg ivet Ru-103 N/A
<MDA
<MDA None Ru-106 N/A
<MDA
<MDA None Cs-134 1.30E+2
<MDA
<MDA None Cs-137 I.50E+2
<MDA
<MDA None Ba-140 N/A
<MDA
<MDA None La-140 N/A
<MDA
<MDA None Ce-141 N/A
<MDA
<MDA None Ce-144 N/A
<MDA
<MDA None Direct Radiation mean and range values are based on off-site TLDs LLD = Fermi 2 ODCM LLD: nominal lower limit of detection based on 4.66 sigma error for background sample.
<MDA = Less than the lab's minimum detectable activity which is less than the LLD.
Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses (F).
Locations are specified by Fermi 2 code and are described in Appendix A Sampling Locations.
Non-routine results are those which are reportable according to Fermi 2 ODCM control 3.12.1.
Note: Other nuclides were considered in analysis results, but only those identifiable were reported in addition to ODCM listed nuclides.
B-7
Appendix C Environmental Data Tables
e s-no Fermi 2-2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2
TLD ANALYSIS (mR/Std Qtr)
STATION FIRST SECOND THIR 1 FOURTH.
NUMBER
- QUARTER QUARTER '
QUARTER j
QUARTER
_QATR.
QURTR-T-1 12.22 13.14 13.94 15.21 T-2 12.52 12.19 15.14 15.50 T-3 9.47 11.38 12.52 12.93 T-5 12.07 13.29 15.83 16.22 T-5 12.42 13.71 16.36 16.73 T-6 12.76 13.21 15.74 16.39 T-7 11.57 12.33 14.34 15.10 T-8 123.71 14.21 17.03 17.35 T-9 12.24 14.09 16.59 15.56 T-10 12.89 14.00 16.31 16.44 T-1 I (a) 12.94 14.47 15.21 T-12 11.01 11.85 14.34 14.95 T-13 13.46 15.03 16.72 17.63 T-14 14.42 14.71 17.15 17.50 T-15 11.44 12.28 13.45 14.94 T-16 15.32 16.42 19.70 19.79 T-17 10.42 15.61 14.50 15.87 T-18 11.77 13.00 15.03 18.79 T-19 13.89 15.05 17.27 18.00 T-20 14.16 16.25 18.31 20.05 T-21 13.61 (a) 14.48 14.97 T-22 12.07 12.98 14.95 16.54 T-23 12.21 12.80 14.74 15.28 T-24 10.40 11.35 13.84 14.26 T-25 14.88 15.97 17.99 18.38 T-26 14.59 16.68 18.34 18.58 T-27 10.10 11.16 12.86 12.71 T-28 12.66 13.13 15.68 15.49 T-29 12.85 13.01 16.09 16.17 T-30 13.10 14.12 15.98 (a)
T-31 12.99 14.16 16.95 15.52 T-32 12.47 13.72 16.65 16.09 T-33 11.14 11.51 13.45 13.58 T-34 11.23 11.79 13.97 14.37 T-35 11.91 13.16 14.30 14.90 T-36 12.53 13.71 15.76 15.21 T-37 12.77 13.84 15.75 15.58 T-38 13.69 14.32 16.59 17.01 T-39 59.03 62.52 51.75 44.71 T-40 50.69 49.98 40.83 37.22 T-41 94.18 89.17 88.49 66.81 T-42 90.67 88.50 74.06 66.06 T-43 101.99 99.76 85.97 73.93 T-44 88.21 86.38 75.24 63.24 T-45 55.06 56.55 47.64 41.22 T-46 38.15 41.05 37.72 31.80 T-47 94.36 83.32 69.78 69.07 C-1
Ferni2 - 2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 TLD ANALYSIS (CONT.)
(mR/Std Qtr)
I STATION FIRST :
-:SECOND
- THIRD FOURTH NUMBER ! JQUARTER QUARTER` " QUARTER 'L>:
QUARTER--
T-48 41.91 44.65 40.74 34.98 T-49 14.81 18.92 21.16 21.26 T-50 12.67 15.40 15.95 16.12 T-51 9.31 11.24 11.99 12.30 T-52 12.84 14.16 15.23 15.85 T-53 23.47 25.60 25.54 22.55 T-54 14.31 17.52 17.69 16.58 T-55 12.48 14.08 15.28 16.32 T-56 11.41 13.48 15.24 15.89 T-57 14.56 16.47 19.49 17.82 T-58 11.10.
12.40 13.44 14.54 T-59 11.20 12.17 14.16 14.33 T-60 12.79 14.41 16.52 15.87 T-61 13.40 15.29 16.50 16.66 T-62 12.54 15.42 16.41 16.66 T-63 11.11 12.87 13.53 14.52 T-64 20.51 23.07 21.56 21.34 T-65 23.36 26.58 24.36 23.09 T-66 130.88 143.07 113.87 104.78 T-67 15.42 18.00 18.01 17.82 (a) TLD missing, see Appendix D i Program Execution.
C-2
Fermi2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR PARTICULATE GROSS BETA (pCi/cubic meter)
API-I FRST QUARTER 1/6/2004 3.05E-02 +1 2.50E-03 1/13/2004 3.77E-02 +1-2.50E-03 1/20/2004 1.93E-02 +1-2.30E-03 1/27/2004 1.42E-02 +1-2.30E-03 2/3/2004 3.37E-02 +1-2.50E-03 2/10/2004 4.02E-02 +1-2.60E-03 2/17/2004 4.01E-02 +1-2.70E-03 2/2412004 2.83E-02 +1-2.40E-03 32/2004 3.18E-02 +/- 2.40E-03 3/9/2004 2.24E-02 +1-2.30E-03 3/16/2004 1.79E-02 +1-2.30E-03 3/24/2004 1.58E-02 +1-2.IOE-03 3/30/2004 2.02E-02 +/- 2.60E-03 API-1 SECOND QUARTER
^.'Date Aciitv 4/6/2004 1.62E-02 +/- 12.40E-03 4/13/2004 1.54E-02 +/- 2.20E-03 4/20/2004 2.05E-02 +/- 2.30E-03 4/27/2004 1.40E-02 +/- 2.1 OE-03 5/4/2004 1.78E-02 +1-2.20E-03 5/11/2004 2.24E-02 +1-2.20E-03 5/18/2004 2.39E-02 +1-2.30E-03 5/25/2004 1.48E-02 +1-2.20E-03 6/1/2004 1.62E-02 +/- 2.20E-03 6/8/2004 2.19E-02 +1-2.40E-03 6/15/2004 2.38E-02 2.50E-03 6/22/2004 1.97E-02 +1-2.50E-03 6/29/2004 1.41 E-02 +/- 2.40E-03 C-3
Fermi 2-2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR PARTICULATE GROSS BETA (pCi/cubic meter)
API-i THIRD QUARTER l'.Date-'
iv-Acit
7/6/2004 2.15E-02 +t 2.20E-03 7/13/2004 1.77E-02 +/
2.50E-03 7/20/2004 2.OOE-02 +/ 2.30E-03 7/27/2004 2.06E-02 +/
2.30E-03 8/3/2004 3.08E-02 +/ 2.50E-03 8/10/2004 2.51 E-02 +/ 2.30E-03 8/17/2004 1.36E-02 +/ 2.1OE-03 8/23/2004 2.31 E-02 +/
2.60E-03 8/31/2004 (a) 9/7/2004 3.38E-02 +/ 3.30E-03 9/14/2004 2.47E-02 +1 2.30E-03 9/21/2004 2.60E-02 +1 2.30E-03 9/28/2004 3.21E-02 +1 2.50E-03 API-I FOURTH QUARTER iDate-
. ACtivit 10/5/2004 1.77E-02 +/-12.10E-03 10/12/2004 2.38E-02 +/
2.50E-03 10/19/2004 1.59E-02 +/ 2.20E-03 10/26/2004 1.33E-02 +/- 2.20E-03 1 1/2/2004 2.03E-02 +/
2.50E-03 11/9/2004 2.25E-02 +/
2.30E-03 11/16/2004 2.99E-02 +/ 2.60E-03 11/23/2004 3.06E-02 +/ 2.70E-03 11/30/2004 1.81E-02 +/
2.50E-03 12n7/2004 2.86E-02 +/
2.70E-03 12/14/2004 1.811E-02 +/
2.50E-03 12/21/2004 2.50E-02 +/ 2.40E-03 12/28/2004 3.40E-02 +/
2.60E-03 (a) Sample not collected; see Appendix D, Program Execution.
C-4
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR PARTICULATE GROSS BETA (pCi/cubic meter)
API-2 FIRST QUARTER I Date'-",I, 1A tVI Y.,_
1/6/2004 3.10E-02 +1-2.40E-03 1/13/2004 3.39E-02 +1. 2.50E-03 1/20/2004 1.24E-02 +1-2.10E-03 1/27/2004 1.90E-02 +1-2.40E-03 2/3/2004 2.1 5E-02 +1-2.40E-03 2/10/2004 3.62E-02 +1-3.90E-03 2/17/2004 3.06E-02 +1-3.1 OE-03 2/24/2004 1.94E-02 +1-2.3 0E-03 3/2oo4 2.94E-02 +1-2.40E-03 3/9/2004 2.07E-02 +1-2.80E-03 3/16/2004 1.35E-02 +1-2.20E-03 3/24/2004 9.70E-03 +1-2.OOE-03 3/30/2004 1.26E-02 +/- 2.40E-03 API-2 SECOND QUARTER Date- [
1Cttii-4/6/20041 8.40E-03 +/- 2.20E-03 4/13/2004 2.05E-02 +/- 2.30E-03 4/20/2004 1.30E-02 +/- 2.20E-03 4/27/2004 8.00E-03 +/- 2.00E-03 5/4/2004 1.33E-02 +/- 2.10E-03 5/11/2004 2.8OE-02 +/- 2.30E-03 5/18/2004 2.63E-02 +/- 2.30E-03 5/25/2004 1.96E-02 +/- 2.20E-03 6/1/2004 1.47E-02 +/- 2.20E-03 6/8/2004 1.83E-02 +/- 2.30E-03 6/15/2004 2.58E-02
+
2.50E-03 6/22/2004 2.79E-02 +/- 3.40E-03 6/29/2004 2.06E-02 +/- 2.50E-03 C-S
Fermi 2-2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR PARTICULATE GROSS BETA (pCi/cubic meter)
API-2 THIRD QUARTER V ~Date~ ;-- 1. R >W Activity§
]-
7/6/2004 2.78E-02 +t-2.30E-03 7/13/2004 2.23E-02 +t-2.50E-03 7/20/2004 2.46E-02 +t-2.40E-03 7/27/2004 2.66E-02 +t-2.40E-03 8/3/2004 5.09E-02 +t-2.80E-03 8/10/2004 3.83E-02 +t-2.60E-03 8/17/2004 2.20E-02 +t-2.30E-03 8/23/2004 4.82E-02 +t-2.90E-03 8/31/2004 3.90E-02 +t-2.50E-03 9n72004 6.31E-02 +t-3.OOE-03 9/14/2004 5.15E-02 +t-2.80E-03 9/21/2004 4.67E-02 +t-2.70E-03 9/28/2004 2.38E-02 +t-2.30E-03 API-2 FOURTH QUARTER
-Date'
-lTi
.Actiitr
-7 10/5/2004 4.09E-02 +/- 2.60E-03 10/12/2004 4.80E-02 +/- 2.90E-03 10/19/2004 3.05E-02 +t-2.90E-03 10/26/2004 3.53E-02 +t-3.60E-03 1 t/22004 (a) l 1/9/2004 2.45E-02 +t-2.30E-03 11/16/2004 3.1 OE-02 +t-2.60E-03 11/23/2004 3.30E-02 +t-2.70E-03 11/30/2004 1.76E-02 +t-2.50E-03 12n/2004 2.77E-02 +t-2.70E-03 12t14/2004 2.46E-02 +t-2.60E-03 12121/2004 2.33E-02 +t-2.40E-03 12128/2004 2.82E-02 _
2.40E-03 (a) Sample not collected; see Appendix D, Program Execution.
C-6
Fermi 2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR PARTICULATE GROSS BETA (pCi/cubic meter)
API-3 FIRST QUARTER t.
1AcDt 1/6/2004 3.02E-02 +1-2.40E-03 1/13/2004 3.57E-02 +1-2.50E-03 1/20/2004 2.60E-02 +1-2.40E-03 1/27/2004 2.31 E-02 +1-2.50E-03 2/3/2004 3.94E-02 +1-2.60E-03 2/10/2004 4.55E-02 +1-2.70E-03 2/17/2004 4.42E-02 +1-2.80E-03 2/24/2004 3.61E-02 +1-2.60E-03 32/2004 2.12E-02 +1-2.20E-03 3/9/2004 2.33E-02 +1-2.40E-03 3/16/2004 2.74E-02 +1-2.50E-03 3/24/2004 2.01E-02 _
2.20E-03 3/30/2004 2.44E-02 +/- 2.60E-03 API-3 SECOND QUARTER Dat
]8-
-Daiit 4/6/2004 2.09E-02 +/- 2.40E-03 4/13/2004 1.07E-02 +/- 2.1 OE-03 4/20/2004 2.63E-02 +1-2.40E-03 4/27/2004 1.90E-02 _
2.20E-03 5/4/2004 1.90E-02
+/- 2.20E-03 5/11/2004 2.73E-02 +1-2.30E-03 5/18/2004 1.80E-02 +1-2.20E-03 5/25/2004 1.49E-02 +1-2.10E-03 6/1/2004 1.40E-02 +1-2.20E-03 6/8/2004 2.47E-02 +1-2.40E-03 6/15/2004 2.02E-02 +1-2.50E-03 6/22/2004 2.50E-02 +1-3.10E-03 6/29/2004 1.53E-02 2.40E-03 C-7
Fermni2 -2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR PARTICULATE GROSS BETA (pCi/cubic meter)
API13 THRD QUARTER lT" K '::Date:
'Activity-7/6/20041 2.42E-02 +/- 2.30E-03 7/13/2004 1.32E-02 +1-2.40E-03 712012004 2.19E-02 +1-2.30E-03 7/27/2004 1.83E-02 +1-2.20E-03 8/312004 3.05E-02 +1-2.50E-03 8/1012004 2.38E-02 +1-2.30E-03 8/1712004 1.76E-02 +1-2.20E-03 812312004 2.98E-02 +1-2.60E-03 8/3112004 2.22E-02 +1-2.20E-03 9n//2004 2.65E-02 +1-2.40E-03 9/1412004 2.45E-02 +1-2.30E-03 9s2112004 2.62E-02 2.40E-03 912812004 3.18E-02 +1-2.soE-03 API-3 FOURTH QUARTER
- -Date-;1
- Activitv 10/S/2004 2.38E-02 +/- 2.20E-03 10/1212004 2.76E-02 +1-2.60E-03 10/19s2004 2.13E-02 +1-2.30E-03 10/2612004 1.3 1 E-02 +/- 2.20E-03 11/12n004 2.68E-02 +1-2.60E-03 11/9s2004 2.07E-02 +/- 2.20E-03 11/1612004 2.89E-02 +/- 2.60E-03 11n2312004 3.01E-02 +/- 2.70E-03 11/3012004 2.14E-02 +- 2.60E-03 12/712004 3.25E-02 +/- 2.80E-03 12/1412004 1.90E-02 +/ 2.50E-03 1212112004 2.39E-02 +/- 2.40E-03 12/2812004 2.92E-02 +/- 2.50E-03 C-8
Fermi 2-2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR PARTICULATE GROSS BETA (pCilcubic meter)
API-4 FIRST QUARTER Date.-
lvActivit l6120041 3.25E-02 +/- 2.50E-03 1/13/2004 3.36E-02 +1-2.40E-03 1/20n2004 (a) 1/2712004 1.71 E-02 +1-2.40E-03 2/3/2004 3.15E-02 +1-2.50E-03 2/1012OD4 5.03E-02 +1-2.80E-03 2/1712004 4.65E-02 +1-2.80E-03 2/24n2004 3.74E-02 +1-2.60E-03 312004 3.28E-02 +1-2.40E-03 3/912004 2.40E-02 +1-2.40E-03 3/1612004 2.79E-02 +1-2.50E-03 3/2412004 2.59E-02 2.30E-03 3/30/2004 1.93E-02 +- 2.50E-03 API-4 SECOND QUARTER
- Date -l I Acti--ty ^ '- :
4/612004 2.OOE-02 +1-2.40E-03 4/1312004 1.87E-02 +1-2.20E-03 412012004 2.71E-02 +1-2.40E-03 412712004 1.83E-02 +1-2.20E-03 5/412004 2.42E-02 +1-2.30E-03 5/11/2004 2.59E-02 +- 2.30E-03 5/1812004 2.12E-02 +1-2.20E-03 512512004 1.29E-02 +/- 2.10E-03 6/l12004 1.20E-02 +1-2.20E-03 6/812004 2.1 SE-02 +1-2.30E-03 6/1512004 2.19E-02 +/- 2.50E-03 612212004 1.70E-02 _
2.50E-03 612912004 1.23E-02 +/- 2.40E-03 L
(a) Sample not collected; see Appendix D, Program Execution.
C-9
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR PARTICULATE GROSS BETA (pCi/cubic meter)
AP14 THIRD QUARTER l Date
- .i P Activity
]-^
7/6/2004 2.33E-02 +1-2.30E-03 7/13/2004 1.73E-02 +1-2.50E-03 7/20/2004 2.03E-02 +1-2.30E-03 7/27/2004 1.88E-02 +1-2.20E-03 8/3/2004 2.59E-02 +1-2.40E-03 8/10/2004 2.12E-02 +- 2.30E-03 8/17/2004 1.22E-02 +1-2.1 OE-03 8/23/2004 2.61E-02 +
2-.60E-03 8/31/2004 2.32E-02 +1-2.30E-03 n/20oo44 2.66E-02 +/- 2.40E-03 9/14/2004 2.56E-02 +1-2.30E-03 9/21/2004 2.61E-02 _
2.30E-03 9/28/2004 8.47E-02 +/- 3.20E-03 API-4 FOURTH QUARTER
- .Date J lK-<-::-.Activitv' 10/5/2004 1.89E-02 +1-2.10E-03 10/12/2004 2.58E-02 +1-2.50E-03 10/19/2004 1.98E-02 +1-2.30E-03 10/26/2004 1.03E-02 +1-2.20E-03
- Ioo004 2.44E-02 +/- 2.50E-03 11/9/2004 2.16E-02 +1-2.30E-03 11/16/2004 2.53E-.02 2.50E-03 11/23/2004 2.96E-02 +- 2.70E-03 11/30/2004 1.70E-02 +1-2.50E-03 12nn/204 2.95E-0
+2 - 2.70E-03 12/14/2004 2.57E-02 +1-2.60E-03 12/21/2004 2.47E-02 +1-2.40E-03 12/28/2004 3.64E-02 +/- 2.60E-03 C-10
Fermi2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2
- AIR PARTICULATE GROSS BETA (pCilcubic meter)
API-S FIRST QUARTER
. Datel '
- '.Ativity 1/6/2004 3.12E-02 +1-2.40E-03 1/13/2004 3.12E-02 +1-2.40E-03 1120/2004 1.99E-02 +1-2.30E-03 1/27/2004 1.941-02 +1-2.40E-03 2/3/2004 3.58E-02 +1-2.60E-03 2/10/2004 3.83E-02 +1-2.602-03 2/17/2004 3.93E-02 +1-2.70E-03 2/24/2004 3.29E-02 +1-2.50E-03 3//oo4 2.72E-02 +1-2.30E-03 3/9/2004 4.49E-02 +1-4.60E-03 3/16/2004 1.75E-02 +1-2.40E-03 3/24/2004 1.40E-02 +1-2.10E-03 3/30/2004 1.692-02 +1-2.501E-03 API-5 SECOND QUARTER
'Date'. -: :
Activiti' 4/6/2004 1.43E-02 +1-2.30E-03 4/13/2004 1.50E-02 +1-2.20E-03 4/20/2004 2.57E-02 +/- 2.40E-03 4/27/2004 1.61E-02 +/- 2.101E-03 5/4/2004 2.19E-02 +/- 2.30E-03 5/11/2004 3.333E-02 +1-2.40E-03 5/18s2004
- 2. 12 E-02 +/- 2.20E-03 5/25/2004 1.862-02 +/- 2.30E-03 6/1/2004 1.39E-02 +/- 2.20E-03 6/8/2004 2.27E-02 +/- 2.40E-03 6/15/2004 2.31E-02 +/- 2.502-03 6/22/2004 2.32E-02 +/- 2.60E-03 6/29/2004 1.28E-02 +/- 2.30E-03 C-ll
Fermi 2 - 2004 Annual
. Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR PARTICULATE GROSS BETA (pCi/cubic meter)
API-5 THIRD QUARTER
'.-I Dite Activitj' 7/612004 2.45E-02 +/- 2.30E-03 7/13/2004 1.57E-02 +J 2.40E-03 7/20/2004 2.166E-02 +/
2.300E-03 7/27/2004 2.35E-02 +/ 2.30E-03 8/3/2004 3.08E-02 +/ 2.50E-03 8/10/2004 1.99E-02 +1-2.20E-03 8/17/2004 1.47E-02 +/ 2.1 OE-03 8/24/2004 (a) 8/31/2004 2.40E-02 +/ 2.30E-03 9/712004 2.711E-02 +/ 2.40E-03 9/14/2004 2.49E-02 +/
2.30E-03 9/21/2004 2.71E-02 +/
2.30E-03 9/28/2004 3.51 E-02 +1 2.60E-03 API5 FOURTH QUARTER 10/5Da2e 240-Ac1i0vt 1
10/512004 2.40E-02l +/- l2.20E-03 10/12/2004 2.78E-02 +/
2.60E-03 10/19/2004 1.60E-02 +/ 2.20E-03 10/26/2004 1.29E-02 +/
2.20E-03 1112/2004 2.27E-02 +/
2.50E-03 11/9/2004 2.05E-02 +/ 2.20E-03 11/16/2004 2.86E-02 +/ 2.60E-03 11/23/2004 3.25E-02 +J 2.70E-03 11/30/2004 1.91E-02 +/
2.50E-03 12/7/2004 2.74E-02 +/
2.80E-03 12/14/2004 (a)
=
12/21/2004 2.86E-02 +- 2.50E-03 12/28/2004 4.37E-02 +/
2.80E-03 (a) Sample not collected; see Appendix D. Program Execution.
C-12
Fermi 2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR IODINE-131 (pCi/cubic meter)
API-1 FIRST QUARTER
--Datew.
4l. AdtintyP-l 1/612004
< 5.soE-02 1/13/2004
< 5.70E-02 1/20/2004
< 3.50E-02 1/27/2004
< 4.50E-02 2/3/2004
< 4.10E-02 2/10/2004
< 4.40E-02 2/17/2004
< 4.00E-02 2/24/2004
< 4.40E-02 3/2/2004
< 4.70E-02 3/9/2004
< 3.50E-02 3/1 6/2004
< 3.soE-02 3124/2004
< 3.soE-02 3/3020041,
< 3.20E-02 API-i SECOND QUARTER I "~.
.1 1 -~ A rtiAtvuv-4/6/2004
<12.soE-02 4/13/2004
< 3.40E-02 4/20/2004
< 5.OOE-02 4127/2004
< 3.30E-02 5/4/2004
< 3.90E-02 5/1112004
< 3.90E-02 5/18s2004
< 4.soE-02 5/2512004
< 4.soE-02 6/1/2004
< 4.50E-02 6/8/2004
< 4.20E-02 6/15/2004
< 4.50E-02 6/22/2004
<14.OOE-02 6129/2004
< 4.20E-02 C-13
Fermi2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR IODINE - 131 (pCi/cubic meter)
API-1 THIRD QUARTER Date.
Adi 7/6/2004
< 3.80E-02 7/13/2004
< 4.30E-02 7120/2004
< 5.50E-02 7/27/2004
< 3.70E-02 8/3/2004
< 3.90E-02 8/10/2004
< 4.30E-02 8/17/2004
< 5.30E-02 8/23/2004
< 4.70E-02 8/31/2004 (a) 9/7/2004
< 4.20E-02 9/14/2004
< 3.10E-02 9/21/20041
<4.OOE-02 9/28/2004
< 3.60E-02 API-1 FOURTH QUARTER
- 2Date>04
< 3Actii0 10/51/2004
< 3.20E-02 10/12/2004
< 3.00E-02 10/19/2004
<3.70E-02 10/26/2004
<I 3.00E-02 11/2/2004
< 4.IOE-02 11/9/2004
< 3.60E-02 11/16/2004
< 3.40E-02 11/23/2004
< 3.50E-02 11/30/2004
< 4.80E-02 12t7/2004
< 5.30E-02 12/14/2004
< 3.70E-02 12/21/2004
< 4.30E-02 12i28/2004
< 4.70E-02 (a) Sample not collected; see Appendix D, Program Execution.
Fermi 2 - 2004 Annual
-Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR IODINE-131 (pCi/cubic meter)
API-2 FIRST QUARTER Date :;'j :;: 'Activitg 1/6/2004
< 5.50E-02 1/13/2004
< 5.60E-02 1/20/2004
< 3.50E-02 1/27/2004
< 4.8OE-02 2/312004
< 4.30E-02 2/10/2004
< 3.20E-02 2/17/2004
< 5.50E-02 2/24/2004
< 4.30E-02 3/2/2004
< 4.OOE-02 3/9/2004
< 4.90E-02 3/16/2004
< 3.90E-02 3/24/2004
< 3.30E-02 3/30/2004
< 4.60E-02 API-2 SECOND QUARTER
.Date -;
Activi 4/6/2004
< 3.OOE-02 4/13/2004
< 3.30E-02 4/20/2004
< 4.60E-02 4/27/2004
< 3.OOE-02 5/4/2004
< 4.20E-02 5/11/2004
< 3.90E-02 5/18/2004
< 4.soE-02 5/25/2004
< 4.30E-02 6/1/2004
< 3.40E-02 6/8/2004
< 3.90E-02 6/15/2004
<13.30E-02 6/22/2004
<14.60E-02 6/29/2004
<14.30E-02 C-15
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR IODINE - 131 (pCi/cubic meter)
API-2 THIRD QUARTER Date '1 ActiitY-7/6/2004
< 3.20E-02 7/13/2004
< 3.30E-02 7/20/2004
< 4.50E-02 7/27/2004
< 4.30E-02 8/3/2004
< 3.20E-02 8/1012004
< 4.00E-02 8/1712004
< 5.1OE-02 8/23/2004
< 4.30E-02 8/31/2004
< 4.30E-02 9/7/2004
< 4.20E-02 9/14/20041 4.1 OE-02 9/2112004
< 14.1OE-02 9128120041
< 3.50E-02 API-2 FOURTH QUARTER C.>-Date 7--l:
-Ativi>
10/5/2004
< 2.80E-02 10/1212004
<14.20E-02 10/19/2004
< 4.40E-02 10126/2004
< 4.30E-02 11/2/2004 (a) 11/9/2004
< 3.50E-02 11/16/2004
< 3.60E-02 11/23/2004
< 4.50E-02 11/3012004
< 5.20E-02 12/7/2004
< 4.20E-02 12/14t2004
< 4.10E-02 12/21/2004
< 4.80E-02 12/28/2004
< 5.20E-02 (a) Sample not collected; see Appendix D, Program Execution.
C-1 6
Fermi 2 - 2004 Annual
- Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR IODINE - 131 (pCilcubic meter)
API-3 FIRST QUARTER Date -
Adilit3&
1/6/2004
< 5.60E-02 1/13/2004
< 4.80E-02 1/20/2004
< 3.20E-02 1/27/2004
< 3.00E-02 2/312004
< 4.80E-02 2/10/2004
< 4.40E-02 2/17/2004
< 4.20E-02 2/24/2004
< 4.40E-02 3/2/2004
< 5.1OE-02 319/2004
< 3.90E-02 3/16/2004
< 3.30E-02 3/24/2004
< 4.30E-02 3/30/2004
< 4.1 OE-02 API-3 SECOND QUARTER 2-Date 1 [
3Ativt-4/6/2004
< 3.30E-02 4/13/2004
< 3.60E-02 4/20/2004
< 3.70E-02 4/27/2004
< 2.40E-02 5/4/2004
< 4.1 OE-02 5/11/2004 c 3.60E-02 5/18/2004
< 3.OOE-02 5/25/2004
< 4.OOE-02 6/1/2004
< 4.40E-02 6/8/2004
< 4. 1OE-02 6/15/2004
< 4.60E-02 6/22/2004
< 4.30E-02 6/29/2004
< 4.80E-02 C-17
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR IODINE - 131 (pCi/cubic meter)
API-3 THIRD QUARTER Date" -1 IActiitv.-
7/6/2004
< 4.40E-02 7/13/2004
< 4.1OE-02 7/20/2004
< 6.40E-02 7/27/2004
< 4.OOE-02 8/3/2004
< 3.70E-02 8/10/2004
< 4.50E-02 8/17/2004
< 4.70E-02 8/23/20041
< 4.10E-02 8/31/2004
< 3.90E-02 9/72004
< 4.40E-02 9/14/2004
< 2.80E-02 9/21/2004
< 3.80E-02 9/28/2004
< 4.OOE-02 API-3 FOURTH QUARTER
- 5Date [2004 Act1ty<
1 10/5/2004
< 3.80E-02 10/12/2004
< 3.20E-02 10/19/2004
< 4.30E-02 10/26/2004
< 3.90E-02 11/2/2004
< 3.40E-02 11/9/2004
< 3.80E-02 11/16/2004
< 3.80E-02 11/23/2004
< 4.10E-02 11/30/2004
< 4.OOE-02 12n/2004
< 4.70E-02 12/14/2004
< 3.50E-02 12/21/2004
< 4.60E-02 12/28/2004
<14.30E-02 C-1 8
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR IODINE - 131 (pCi/cubic meter)
API-4 FIRST QUARTER
.-';Date ' '" -;.Activity:.-
1/6/2004
< 5.80E-02 1/13/2004
< 4.40E-02 1/20/2004 (a) 1/27/2004
< 4.50E-02 213/2004
< 3.10E-02 2/10/2004
< 4.20E-02 2/17/2004
< 2.70E-02 2/24/2004
< 4.60E-02 3/2004
< 3.50E-02 3/912004
< 3.90E-02 3/16/2004
< 3.90E-02 3/24/2004
< 3.80E-02 3/30/2004
< 3.80E-02 API-4 SECOND QUARTER
--Date.
Actintyi-'
4/6/2004
< 3.60E-02 4/13/2004
<3.20E-02 4/20/2004
< 4.50E-02 4/27/2004
<2.40E-02 5/4/2004
< 3.40E-02 5/11/2004
< 4.20E-02 5/18/2004
< 4.OOE-02 5/25/2004
< 3.90E-02 6/l/2004
< 5.1OE-02 6/8/2004
< 4.OOE-02 6/15/2004
< 3.90E-02 6/22/2004
< 3.90E-02 6/29/2004
< 5.OOE-02 (a) Sample not collected; see Appendix D, Program Execution.
C-19
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR IODINE - 131 (pCilcubic meter)
API-4 THIRD QUARTER 7620Date
< 3.8A00ty 7/6/2004
< 3.80E-02 7/1312004
< 4.50E-02 7/20/2004
< 4.10E-02 7/27/2004
< 3.1OE-02 8/3/2004
< 4.OOE-02 8/10/2004
< 3.80E-02 8/17/20041
< 4.10E-02 8/23/2004
< 3.70E-02 8/31/20041
< 4.20E-02 9/7/2004
< 3.50E-02 9/14/2004
< 3.40E-02 9/21/2004
< 3.90E-02 9/28/2004
< 4.IOE-02 API-4 FOURTH QUARTER 10/5/2004
< 2.50E-02 10/12/2004
< 3.40E-02 10/19/2004
< 3.80E-02 10/26/2004
< 4.20E-02 11/2/2004
< 2.80E-02 11/9/2004
< 3.50E-02 11/16/2004
< 3.40E-02 11/23/2004
< 5.10E-02 11/30/2004
< 5.40E-02 i 2/7/2004
< 4.80E-02 12/14/2004
<13.80E-02 12/21/2004
< 4.50E-02 12/28/2004
<14.90E-02 C-20
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR IODINE - 131 (pCi/cubic meter)
API-5 FIRST QUARTER
- Date. -
Actiit 16120041
< 6.OOE-02 1/13/2004
< 4.soE-02 1120/2004
< 3.10E-02 1/27/2004
< 4.60E-02 2/3/2004
< 4.80E-02 2/10/20041
< 4.10E-02 2/17/2004
< 4.20E-02 2/2412004
< 4.00E-02 3/2/2004
< 4.40E-02 3/9/2004
< 3.00E-02 3/16/2004
< 4.30E-02 3n24/2004
< 2.90E-02 3/30/2004
< 4.soE-02 API-5 SECOND QUARTER
-CActivity 4/6/2004
< 2.90E-02 4/13/2004
< 3.OOE-02 4/20/2004
< 3.40E-02 4/27/2004
< 2.50E-02 5/4/2004
< 2.90E-02 5/11/2004
< 3.50E-02 5/18/2004
< 3.90E-02 5/25/2004
< 4.10E-02 6/1/2004
< 4.OOE-02 6/8/2004
< 4.40E-02 6/15/2004
< 4.10E-02 6/22/2004
< 3.90E-02 6/29/2004
< 4.60E-02 C-21
Fermi 2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR IODINE - 131 (pCi/cubic meter)
API-5 THIRD QUARTER
-Date -
Aivit 7/6/20041
< 3.50E-02 7/1312004l
<l4.70E-02 7/20/2004
< 6.30E-02 7/27/2004
< 4.40E-02 8/3/2004
< 3.70E-02 8/10/2004
< 4.00E-02 8/17/2004
< 4.60E-02 8/24/2004 (a) 8/31/2004
< 4.50E-02 9/7/2004
< 4.OOE-02 9/14/2004
< 4.1OE-02 9/21/2004
< 4.10E-02 9/28/2004
< 3.20E-02 API-5 FOURTH QUARTER
.;-Date:;. -.Actiit' 10/5/2004
< 3.40E-02 10/12/2004
< 3.00E-02 10/19/2004
< 3.50E-02 10/26/2004
< 3.60E-02 11/2/2004
< 3.40E-02 11/9/2004
< 3.80E-02 11/16/2004
< 3.70E-02 11/23/2004
< 1.40E-02 11/30/2004
< 4.70E-02 12n/2004
< 4.90E-02 12/14/2004 (a) 12/21/2004
<14.80E-02 12/28/2004
< 5.20E-02 (a) Sample not collected; see Appendix D, Program Execution.
C-22
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR PARTICULATE QUARTERLY COMPOSITE ANALYSIS API-1 (indicator)
(pCi/cubic meter) lNuclide':19-I First Quarter SecondQuarter "
Be-7 8.50E-02 +1-1.90E-02 I
l.09E-011 +/- 2.OOE-02 K.40 5.30E-02 4.10E-02 Mn-54 2.20E-03 3.20E-03 =
Co-58 4.1 OE-03 3.40E-03 Fe-59 1.80E-02 I.OOE-02 _-
Co-60 3.30E-03 7.70E-04 Zn-65 7.20E-03 7.40E-03 =
Zr-95 8.40E-03 7.50E-03 Ru-103 I.OOE-02 6.OOE-03 Ru-106 2.70E-02 =
< 2.20E-02 =
Cs-134 3.10E-03 2.1OE-03 Cs-137 2.70E-03 =
1.90E-03 =
Ba-140 1.80E-01 4.70E-02 La-140 2.10E-01 5.50E-02 Ce-141 1.60E-02 9.20E-03 Ce-144 1.50E-021 1.40E-02 =
API-1 (indicator)
(pCi/cubic meter)
[NUClIde -
-.d.- Third Quarier (a)
Ž t'-_Foixrtib Quarter Be-7 1.1 E-O0
+1-2.50E-02 7.60E-02 +1-2.OOE-02 K-40 2.1 OE-02 4.30E-02 Mn-54 2.80E-03 1.60E-03 Co-58 3.90E-03 5.40E-03 Fe-59 3.30E-02 2.20E-02 Co-60 2.80E-03 2.20E-03 =__
Zn-65 7.40E-03 =
8.30E-03 =
Zr-95 1.20E-02 _<
1.1OE-02 Ru-103 1.30E-02 6.60E-03 Ru-106 1.70E-02 3.OOE-02 Cs-134
<_ 2.40E-03 =
3.30E-03 =
Cs-137 2.OOE-03 =
2.30E-03
=
Ba-140 7.10E-O1
< I.IOE-OI La-140 8.20E-01 1.30E-O1 _-
Ce-141 1.20E-021 1.30E-02 Ce-144 5.30E-03 =
1.30E-02 =
(a) See Appendix D, Program Execution.
C-23
Fermi 2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR PARTICULATE QUARTERLY COMPOSITE ANALYSIS API12 (indicator)
(pCi/cubic meter) lNuclide 1 --
' First'Quarter;-
7 Second Quarter Be-7 I
7.50E-021 +/- 2.OOE-02 I
1.09E-01 +/- 12.10E-02 K-40
_<l 6.70E-021 l_
3.10E-02 Mn-54 3.30E-03 2.90E-03 =
Co-58 5.70E-03 4.90E-03 Fe-59 1.70E-02 =
1.20E-02 =
<1 4.30E-03 =
2.30E-03 Zn-65 9.OOE-03 7.OOE-03 =
Zr-95 8.OOE-031 5.50E-03 Ru-103 6.30E-03 5.30E-03 Ru-106 3.70E-02 3.OOE-02 _
Cs-134 2.40E-03
=<_
_ 2.80E-03 __
Cs-137 2.90E-03 2.50E3-03=
Ba-140 1.40E-01 l 5.60E-02 La-140 1.60E-01 6.50E-02 Ce-141 1.50E-021 I.OOE-02 Ce-144 1.50E-021 1.20E-02 =
API-2 (indicator)
(pCi/cubic meter)
INucfide.. [I
--Third Quarter-:
I
---FousihQuarter (a)m--
Be-7 1.72E-01 I +/- 2.90E-02 1 I.OIE-OI +/- 2.70E-02 K-40 3.70E-02[
4.90E-02 Mn-54 4.30E-031 3.60E-03 Co-58 6.30E-03 3.OOE-03 Fe-59 2.30E-02 1.80E-02 Co-60 4.90E-03 =<
5..OE-03 Zn-65 5.20E-03 1.1 OE-02 Zr-95 1.OOE-02 1.1 OE-02 Ru-103 8.90E-03 9.60E-03 Ru-1 06 2.90E-02 2.20E-02 Cs-134 3.80E-03 3.80E-03
=
Cs-137 5.30E-03 3.OOE-03 Ba-140 8.50E-02 8.30E-02 La-140 9.80E-02 9.60E-02 =
Ce-141 1.40E-02 I.50E-02 Ce-144 1.50E-02 =<_
1.60E-02 =
(a) See Appendix D, Program Execution.
C-24
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR PARTICULATE QUARTERLY COMPOSITE ANALYSIS API-3 (indicator)
(pCi/cubic meter) li-rst Quarer
-Second Quarter ':
Be-7 l_
6.50E-021+/- 2.IOE-02 1.OlE-O1 +1-j2.20E-02 K-40 5.70E-02=
3.OOE-02 Mn-54 3.70E-03 2.30E-03 Co-58 5.70E-03 3.90E-03 Fe-S9 1.80E-02 1.50E-02 Co-60 2.80E-03 =
3.30E-03 Zn-65 4.40E-03 6.20E-03 Zr-95 9.20E-03 7.60E-03 Ru-103 8.30E-03_
7.40E-03 Ru-106 3.20E-02
=
2.60E-02 Cs-134 2.30E-03
=
3.40E-03
=
Cs-137 2.30E-03 1.90E-03 Ba-140 1.50E-OI 1.40E-02 La-140 1.70E-01 1.60E-02 Ce-141 1.50E-021 9.00E-03 Ce-144 1.40E-02 I
1.20E-02
=
API-3 (indicator)
(pCi/cubic meter) lNuclide;--
3/4r 'Third Quane'.it'r l-I' '.Fourth Ouaner -
Be-7 8.OOE-02 +1 2.40E-02 7.60E-02 K-40 5.50E-02 3.30E-02 Mn-54 3.90E-03 2.OOE-03 Co-58 4.40E-03 3.90E-03 Fe-59 1.80E-02
=__
1.50E-02 Co-60 5.20E-03
=
3.70E-03 =
Zn-65 1.1OE-02 9.80E-031 Zr-95 1.40E-02 8.60E-03 _-
Ru-103 9.60E-03 9.60E-03 Ru-106 3.60E-02 =<_
2.60E-02 Cs-134 4.80E-03 2.70E-03
=
Cs-137 6.60E-03 2.80E-03 Ba-140 6.70E-02 9.50E-02 La-140 7.70E-02_
I.IOE-O1 Ce-141 9.30E-03 1.30E-02
=
_=
Ce-144 I.IOE-02 1.30E-02 =
C-25
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR PARTICULATE QUARTERLY COMPOSITE ANALYSIS API-4 (control)
(pCi/cubic meter),
lNuclide FirstQuarter(a) j Second Quarter-,' 8 - -
Be-7 8.70E-02 +1-2.30E-02
_I 1.31E-01 +/- 2.30E-02 K-40 6.OOE-02 3.60E-02 Mn-54
< 3.20E-03 3.OOE-03 Co-58 3.60E-03
_=<
_ 4.80E-03 =
Fe-59 1.80E-02 =
1.20E-02 =
Co-60 2.80E-03 3.70E-031 Zn-65 4.40E-031 6.80E-03 _
Zr-95 7.50E-03 7.50E-03 Ru-103 9.20E-03 =
5.60E-03 =
Ru-106 2.70E-02 2.00E-02 Cs-134 2.90E-03 2.60E-03 Cs-137 2.90E-03 I <
3.30E-03 =
Ba-140 1.30E-01 =_
<_ 3.80E-02 =
La-140 1.50E-01 =
4.30E-02 =
Ce-141 1.40E-02 9.80E-03 Ce-144
<_ 1.30E-021 1.20E-02 _
API-4 (control)
(pCi/cubic meter) lNuclide~.,
§ J:
Third Quarter,. -:
l ^-^
- Fourih Quanterl Be-7 1.21E-OI +1-1.30E-02 7.OOE-02 I
K-40 2.10E-02 =
3.60E-02 I
< _1.70E-03
_ 3.50E-03 =
Co-58 2.50E-03 5.10E-03 =
Fe-59 7.80E-03
< _2.00E-02 _
Co-60 1.40E-03 3.30E-03 Zn-65
<1 4.50E-03 1.lOE-02 Zr-95 4.80E-03 =<_
7.90E-03 Ru-103 3.90E-03 =
6.60E-03
=
Ru-106 1.70E-02 _
3.00E-02 _
Cs-134 1.40E-03 2.90E-03 Cs-137 1.30E-03 3.1OE-03 _
Ba-140 4.80E-02 =
7.60E-02 =
La-140 5.50E-021 8.70E-02 I
Ce-141 6.30E-031 1.20E-02 I
Ce-144
< 7.10E-03=
1.30E-02 I
(a) See Appendix D, Program Execution.
C-26
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 AIR PARTICULATE QUARTERLY COMPOSITE ANALYSIS API-5 (Indicator)
(pCilcubic meter)
-Nuclide 4
- Frst Quarter Second Quarter Be-7 7.40E-021 -
2.30E-02 7.90E-02 +1 1.90E-02 K-40 6.70E-02 3.30E-02 Mn-54
< *2.80E-03 2.30E-03 Co-58 6.20E-03 4.50E-03 Fe-59 2.40E-02 8.20E-03 ___
Co-60 8.OOE-04 =
3.30E-03 =
Zn-65 6.70E-03 6.1OE-03 Zr-95 1.IOE-02 =
7.50E-03 Ru-103 9.10E-03 5.60E-03 Ru-106 2.80E-02 =
< 2.40E-02 Cs-134 3.20E-03 3.OOE-03 Cs-137 2.60E-03 2.60E-031 Ba-140 1.30E-01
=
< 5.50E-02 =
La-140
.50E-O1
_=
6.30E-02 _=
=
Ce-141 1.40E-02 =
8.80E-03 =
Ce-144 1.50E-02 1.40E-02 _
API-5 (Indicator)
(pCi/cubic meter) lNuclide l
'Third Quarter (a) f-i.
iFourtb Quarter (a)'
Be-7 1.17E-01 +/- 2.90E-02 8.30E-02 _
K-40 5.30E-02 3.90E-02 Mn-54 4.30E-03 =
< 4.40E-03 =
Co-58
< 8.60E-03 =
5.10E-03 =
Fe-59 2.30E-02 =
1.90E-02 =
Co-60 4.10E-031
<1 3.60E-03 Zn-65 1.20E-02 1.1OE-02 I
Zr-9S 1.60E-02 8.60E-03 Ru-103 1.OOE-02 __
=
7.20E-03 _=
Ru-106 3.60E-021 3.40E-02 =
Cs-134.
3.80E-03
< 2.90E-03 Cs-137 5.50E-03
< 3.40E-03 _-
Ba-140 1.20E-01
< - 1.20E-O1 La-140 1.40E-01
=
< 1.40E-O1
____=
Ce-141 1.20E-02 =
1.40E-02 =
Ce-144
<. 1.40E-02 1.60E-02 (a) See Appendix D, Program Execution.
C-27
Fermi 2-2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 MILK ANALYSIS M-2 (Indicator)
(pCi/liter)
Nuclide.
- I
--S-:29-JAN 19-FEB I
25-MAR --
- _____ l 1-131 7.00E-OII 9.10E-01 I
9.90E-01 O
Sr-89
< 4.1 OE+OO
< 8.20E+00 =_
I 9.30E+00 =
< 1.90E+00 1.70E+00 1.70E+00 Be-7
< 6.50E+01 3.20E+01
< 5.20E+01
=
K-40 1.45E+03 +/- 8.90E+01 1.41E+03 +/ 4.1 OE+O I 1.44E+03 +/ 7.OOE+O I Mn-54
< 9.10E+00
< 3.60E+00
< 7.00E+0O Co-58
< 8.20E+00
< 4.10E+00 6.30E+00 =
Fe-59
< 2.80E1+01
< 1.20E+01 =
___=_
< 2.OOE+01 Co-60 1.1 OE+O I
< 3.80E+00 8.80E+00
=
Zn-65
< 2.40E+01
< 9.20E+00 1.80E+01 Zr-95 1.40E+01 6.5 0E+oo 1.30E+01 Ru-103
< 9.30E+00
< 4.1OE+00
< 6.90E+00 Ru-106
< 7.70E+01 3.50E+01 I 6.60E+01
=
Cs-134
< 9.1OE+00
< 4.OOE+00
< 6.10OE+00 Cs-137
< 7.90E+00 3.60E+00 6.80E+00 Ba-140 1.20E+01 6.50E+00 1.30E+01
=
La-140
< 1.40E+01
< 7.50E+00 1.50E+01 _
Ce-141
< 1.20E+01=
_< 8.40E+00 =
< 8.90E+00
=
Ce-144
< 3.80E+01 I < 1.90E+01
< 3.10E+01 _
I Nuclide l
'13-MAY _;_:-_:_ I 27-MAY ________]
I-131 8.60E-0Il 6.10E-01l I_
l <1 8.90E-01I Sr-89
< 7.90E+00
< 8.902+00
< 7.002+001 __
=
1.67E+00 +/- 4.80E-01 2.63E+00 +/ 5.30E-01 1.40E+001 Be-7
< 6.00E+01
< 4.50E+01
< 5.20E+01 K-40 1.42E+03 +/- 7.80E+01 1.44E+03 +/ 5.80E+01 1.312E+03 +/- 6.60E+01 Mn-54
< 7.00E+00
<1 5.80E+00
< 6.70E+00O Co-8=
< 8.70E+00
< 5.40S+00
<_E+O__
6.40E+00
=
Fe-59
< 2.60E+01 l 1.60E+01
< 2.40E+01 Co-60
< 8.50E+00
< 5.40E+00
< 7.40E+00_
Zn-65
< 2.70E+01
< 2.20E+01
=
<1 3.002+01 I
Zr-9S
< 1.40E+01.
< 9.80E+00
<I 1.10E+01 Ru-103
< 9.10E+00
< 6.40E+00
<1 7.002+00_
Ru-106
< 6.90E+01
< 4.90E+01
<1 6.20E+01 Cs-134
< 7.70E+00
< 5.50E+00
<I 6.60E+00 Cs-137
< 6.80E+00
< 5.60E+00 7.10E+00 Ba-140
< 1.00E+01
< 1.10E+01 1.30E+01 La-140 1.20E+01
<1 1.30E+01
< 1.502E+01 __
Ce-141
< 1.30E+01 8.90E+00 =
< 8.60E+00l Ce-144
< 3.90E+01
< 2.80E+01
_II I
< 3.20E+01 C-28
Fermi 2-2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 MILK ANALYSIS M-2 (Indicator)
. (pCi/liter)
Nuclide'. j -"
10--U J
l
'24-
______[
8-1UL>
-77sf 1-131 9.40E-01 l 9.80E-01 I
9.50E-01 I
Sr-89
< 8.70E+00
< 8.60E+0O (a)
Sr-90 1.70E+00
< 1.80E+00 (a)
Be-7 3.50E+01
< 4.10E+01
< 4.50E+01 K-40 1.48E+03 +1 5.00E+01 1.42E+03 +/- 4.90E+01 1.45E+03 +/- 5.70E+O I Mn-54
< 4.70E+00
< 4.20E+00
< 5.70E+OO Co-58
< 4.60E+00
< 4.80E+001
< 5.50E+00 Fe-59 1.60E+01
< 1.40E+01 1.70E+I01 Co-60 5.80E+0o
=
< 5.50E+00
< 6.20E+O0
=
Zn-65
< 1. IOE+O I
< 1.10E+0]
< 2.1OE+O I Zr-95
< 7.80E+00
< 8.90E+OO
< 1.OOE+0 I Ru-103
< 4.50E+00 =
< 5.10E+00
=
< 5.90E+OC
=
Ru-106
< 4.30E+01
< 4.OOE+01
< 4.70E+01 Cs-134
< 4.40E+00 =
< 4.90E+00
< 5.80E+O0
=__
< 4.40E+00
<1 4.20E+00
< 5.40E+00 Ba-140
< 9.50E+00
< 4.80E+0Q
< 8.30E+00 La-140 I.IOE+OI
< 5.50E+00
< 9.50E+00 Ce-141
< 7.0E+00
< 7.90E+00;
< 1.IOE+OI I Ce-<4 2.30E+01
_=
< 2.30E+O4 I
< 2.80E+OI =
Nuclide-lP- ;.
22-J
-l.-.
12-AUG. I 26-AUG 7771 I-131 7.40E-01 I <
4.70E-01 8.OOE-01 Sr-89
< _.60E+00
< 6.20E+O0 I
5.30E+00 Sr-90 1.46E+00 +J-4.60E-01 1.70E+OC I 1.72E+00 +/- 4.40E-01 Be-7
< 5.80E+01 6.10E+01 6.40E+01 I
K-40 1.37E+03 +/- 7.1OE+OI 1.26E+03 +/- 7.OOE+01 1.40E+03 +/- 7.30E+01 Mn-54
< 6.90E+00 c< 7.60E+00
< 6.90E+00 I
Co-58 6.70E+O0 8.OOE+OC
< 7.30E+00 =
Fe-59 2.30E+O1
< 2.30E+01 2.20E+O1
=
< 8.40E+00 7.80E+OC
< 9.OOE+00 Zn-65
< 2.OOE+01 1.90E+01
< 2.20E+01 Zr-95 1.40E+01 1.20E+01 1.20E+I0I Ru-103
< 8.80E+00
< 8.40E+00
< 7.90E+00 Ru-106
< 6.40E+01
< 6.80E+01
< 6.20E+0_
Cs-134
< 7.30E+00 7.60E+OC
< 7.50E+00 Cs-137
< 5.70E+0O
< 6.70E+00
< 6.60E+00 Ba-140 1.30E+I01 1.OOE+01 1.30E+01 La-140
< 1.50E+01 c
1.20E+01 1.40E+O1 Ce-141 1.IOE+O1 7
< 1.,OE+O1 1.20E+O I l Ce-144 3.50E+01 l
< 3.50E+01
_I__
3.50E+01 I I
(a) See Appendix D, Program Execution.
C-29
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 MILK ANALYSIS M-2 (Indicator)
(pCi/liter)
,Nuclide:
l '.';- SE-' -':l'.-'-:23SEP.>
-'l--'
- .4OT
,-:W; 1-131 9.60E-01I 7.80E-01 9.60E-OI Sr-89
_< 3.90E+00 =<
6.40E+00 =<
7.60E+OO Sr-9o
< I1.SOE+OO
< 1.40E+00 2.07E+00 +/- 4.40E-OI Be-7
< 3.40E+01
=<
6.40E+01
=<
5.70E+OI1 K-40 1.40E1+03 +/- 4.60E+01 1.40E+03 +/7.00E+01 1.56E+03 +/- 7.40E+O I1 Mn-54
<1 4.40E+00
< 7.20E+00 7.OOE+OO Co-58
_< 4.00E+001_
< 6.90E+00 _<
8.80E+OOl Fe-S9 1.40E3+01
=<
1.60E+01 l<
- 2. 1 OE+O Il Co-60
< 5.70E+00 =<
7.60E+oo0
< 6.90E+00:=
Zn-65 1.1 OE+O I
< 1.80E+01
< 3.50E+O I Zr-9S
< 7.10OE+OO 1.40E+01 1.20E+O0I Ru-103
< 4.30E+00 =
8.10E+00 =<
8.20E+OO0 Ru-106
< 3.90E+OI
< S.8E+O1 =
< 6.70E+OI01; Cs-134
< 3.70E+OC0
< 7.20E+00 =<
8.OOE+OO0 Cs-137
< 4.10E+OC0_
< 6.30E1+00
< 7.50E+OO Ba-140
< 7.60E+00^
1.30E1+01
< 1.30E+OI La-140
< 8.70E+001
< 1.SOE+OI
< 1.SOE+0I Ce-144
< 2.00E+01 I
< 3.50E+011 I <1 3.90E+O I I=
Nuld-.l> 'i'},- OCT -:77:. 7-> '~n8-O',-:--
.' 6-DEC -.
1-131
<1 9.70E-01 I 5.20E-01 I
<1 8.40E-01 Sr-89
<1 8.50E+00 _
<l 9.OOE+00,
<l 4.60E+0 Sr-90
=
1.80E+00 +/- 5.20E-01 E.9OE+00 =<
1.20E+00:
Be-7
< 4.70E+01
< 4.50E+01
< 4.80E+01l K-40 1.43E3+03 +/- 5.60E+01 1.47E+03 +/6.40E+01 1.49E+031 +/6.20E+OI01 Mn-54
< 5.70E+00
< 6.40E+00
< 5.80E+00; I
Co-58
<5.70E+00 =<
6.20E+00 =<
6.60E+0 Fe-S9 1.60E+01
=<
2.20E+OI I1.90E+01l Co-60
< 6.40E+00
< 7.90E+00
< 6.50E+OOl0 Zn-65
< 1.30E+01
< 1.40E+01 1.40E+0 Zr-9S
< 9.70E+OO
< I.OOE+OI
<l 1.lOE+OI01 Ru-103< <
6.30E+OO=0
< S.SOE+OO0'
<l 6.40E+OO00 Ru-106
< 4.80E+01
=<
5.60E+OI1
<l S.OOE+OIl1 Cs-134
< 6.10E+OO
< S.90E+00
<1 6.50E+00l Cs-137
< 4.80E+00
< 5.40E+00
<. 4.80E+00 Ba-140
< 7.60E+OO I.OOE+OI I.OOE+OI La-140
< 8.80E+001
< 1.20E+01
=<l 1.20E+OIl Ce-141
< 8.40E+00;
<1 7.70E+00-
< 8.90E+OOll0 Ce-144
< 2.60E+01 l<1 2.80E+01 I<l 3.00E+O Il li C-30
Fermi2 -2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 MILK ANALYSIS M-8 (Control)
(pCilfiter)
Nuclide g'l : `
.-+29-JN
` l.-;J-]B;
---25-AR-' --l I-13i 4.50E-01 I=
6.10E3-011=
<1 9.10E3-OI I
Sr-89 I<
3.60E+001 I < 7.90E+00 8.80E3+OO Sr-90
< 1.70E3+OO
< I1.SOE+OO 1.60E+OO Be-7
< 6.20E3+01
< 2.90E3+01
< 6.50E3+OI K-40C 1.38E+03 +/- 7.3013+01
=
1.43E3+03 +/- 4.1 OE3+O I
=
1.4413+03 +/- 7.9OE+0I Mn-54
< 6.50E3+00 =<
4.00E3+00 =
< 7.20E3+OO=0 C-8
< 7.40E3+00 _<
3.80E3+00 _<
8.10OE+OO0 Fe-S9
< 2. 1 OE3+O I I.OOE3+0I
< 2.OOE3+0I Co-60
< 7.40E+00
< 4.50E3+00, 8.60E+OO Zn-65
< 1.80E3+01
=<
9.50E+00 =<
l1.90E+OI1 Zr-9S
< 1.30E3+01 6.50E3+00
< 1.30E+OI Ru-1 03
< 7.60E3+00
< 4.10OE+OO
< 6.9OE3+OO Ru-106
< 5.80E3+01
=<
3.30E3+01 =<
6.50E3+OI1 Cs-134 8.10OE+OO0 4.10OE+OO0
< _.70E+OO0i
=
< 7.00E3+00 =<
3.20E+00 =<
7.90E3+OO0 Ba-140 1.OOE3+OI
< 5.70E3+00 1.30E3+OI La-140 1.20E+01
< 6.60E3+OO I1.SOE+OI
!Ce-141
< 1.1 OE+O1 I
< 9.00E3+001 9.0EO JCe-144 I<
3.40E3+01 I
< 2.00E+01 I
<1 2.70E3+OI1 Nuclide 'l SSP
- ,1
!-'l'._';9
-3AK-s *--
- 27-MAY;:
I-131 7.70E3-01I 7.80E-01 I
<1 8.80E-Oli I
Sr-89
< 6.90E3+001=
8.20E3+00 l<1 5.4013+00l Sr-90 1.30E+00==
2.82E1+00 +/- l4-90E3-OI
<1.lO1E+00 Be-7
< 5.40E3+01 =<
2.60E+OI1 r<
5.8013+01rl K-40 1.57E3+03 +J-8.50E+01 I 1.32E3+03 +/- 13.7013+01 l
1.39E3+03l +/7.20E3+OI Mn-54
< 8.40E3+00
< _.40E3+00
<1 8.0013+00:
Co-58
< 7.30E+00
=<
3.30E+00 ll<1 7.30E+00; Fe-S9
< 2.70E+O I I.IOE3+OI I
<I 2.40E3+OI1 Co-60
< 7.30E+00
< 4. 10E3+OO0 r<
8.OOE+00r Zn-65
< 2.00E+01
< 8.80E+00;
<1 3.40E+OI Zr-9S 1.60E+01 5.80E+OOIi0
<I I.SOE+OI Ru-103
< 9.30E+00 3.70E3+00;
<1 9.OOE+00^
Ru-106
< 7.50E3+01
< 2.90E3+01 l ll<l 6.40E3+OIl1 Cs-134=
< _.90E+00
< 3.40E+00l
< 8.6013l00 Cs-137
< 7.80E3+00
< 3.50E3+00l
<1 7.6012+00l Ba-140 1.30E3+01 6.40Esg00
<l 1.30E3+OIl La-140 I.SOE1+OI
< 7.30E+007
<l I.SOE3+OIl Ce-141
- <1 _30E3+01
< 7.30E+00 l
<1 1.30E3+OI I
Ce-144
<1 4.30E3+0 I I_<
1.6013+01[
I I <1 4.20E+O Il I C-31
Fermi 2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 MILK ANALYSIS M-8 (Control)
(pCi/liter)
Nuclide
. 1-UN __-
l;.24-'JUNW F tx'
-JUL; l
I-131 9.10E-01 9.80E-01 8.00E-OI Sr-89 8.30E+001I
< 9.20E+00
< 9.70E+OO Sr-90 1.70E+00 1.80E+00 1.90E+OO Be-7
< 2.OOE+O1
=
5.501E+O1
< 4.40E+O0 K-40 1.40E1+03 +/- 2.30E+01
=
1.35E+03 +/- 6.90E+01
=
1.43E+03 +/ 5.60E+OI Mn-54 2.1 OE1+OO 8.OOE+OO
< 5.50E+OO Co-58
< 2.20E+00
< 8.30E+OC
=
5.60E+OO Fe-59 7.50E1+00
< 2.20E+01 I
1.60E+OI l Co-60
< 2.40E+00_=
< 9.30E+OC 6.30E+OO
=
Zn-65
< 7.40E+00
< 3.1OE+01 2.30E+O I Zr-95
< 4.OOE+00 1.20E+0 9.60E+OO Ru-103 3.80E+oo
< 9.20E13+OC 5.40E+OO Ru-106 2.OOE+01
< 5.70E+O1
=<____
5.OOE+O1
=_
Cs-134
< 2.20E+00=
< 7.OOE+OC 5.70E+OO
=
< 2.101E+00 7.10E+00 5.40E+OO Ba-140
< 5. 1OE+OO 1.30E+01 8.60E+OO La-140
< S.90E+OC 1.50E+OI1 I
9.90E+OO_
Ce-141 4.OOE+OI 1.IOE+OI 8.50E+OO Ce-144
<I 1.20E+0
< 3.40E+01 I I <
3.10E+OI Nuclide'r.
-1 l
' -__i_
22-AUG 26-AUG -_!__
I-131 I <
7.20E-01 I
<1 4.70E-01l l
<1 8.70E-01 I
Sr-89
< 9.20E+00
<l 8.60E+00 I
<1 7.201+002 I
< 1.70E+00 =
1.70E+00 7_
l <
1.IOE+00 l_7 Be-7
< 5.IOE+O I
< 5.90E+01 l_
l < 6.40E+01 l
K-40 1.30E+03 +/- 7.10E 0+01 1.37E1+03 +/- 7.20E+O1 1.32E1+03 +/- l7.60E1+O1 Mn-54 6.40E+00
< 7.40E+00 8.OOE+OO Co-58
< 6.50E+00 6.90E+00 8.70E+OOl Fe-59 1.90E+01
=
< 2.20E+01
< 2.40E+01 l
Co-60 1.OOE+O1
< 7.30E+00 9.10E+OOI l
Zn-65
< 2.00E+01
< 2.10E+01 l<
3.OOE+O l_
Zr-95 1.30E+01 1.20E+01 1.30E+O1 Ru-103 8.20E+O0 =
< 7.60E+00 9.1OE+O0 Ru-106
< 5.80E+01
< 6.20E+01 l
_l l
<1 6.40E+O1 I l Cs-134
< 7.90E+00
<1 7.50E+00 I
<1 8.80E+OOl I
< 6.10E+00
< 7.60E+00 I
<1 6.70E+OO I
Ba-140 1.20E+O1 1.IOE+O1 1.IOE+OI ___
La-140 1.40E+01
=
1.20E+01 1.30E+O1
_l Ce-141
< 1.IOE+O1 1.OOE+O1 l_
l < 1.20E+01 l_
Ce-144 3.70E+01
< 3.50E+01
< 4.10E+O1 I C-32
~Fermi 2 -2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report F'ERMI 2 MILK ANALYSIS M-8 (Control)
(pCi/liter) l Nuclide; 'l]
6'SEP:-
23-SEP.
2:'-'
4-OCT-'."-,-
I-131 9.50E-01I 7.30E-01 1.50E3+OI Sr-89
< 4.10OE+OO0
< 7.40E+00 =<
7.90E+OO0 Sr-90
< 1.60E+00
< _.60E3+00
=_<
1.50E3+00 Be-7
< 3.30E+01 =<
7.00E3+01 =<
5.50E3+OI1 K-40 1.42E+03 +14.80E3+01 1.36E3+03 +/- 8.60E3+01 1.53E3+03 +/7.00E+O0I Mn-54
<4.10OE+OO
<1 9.30E3+00
< 6.80E3+OO Co-58
< 4.60E3+00
< 8.40E+OC1
< 7.30E3+OC Fe-S59
< 1.01.S+01
< 2.40E+01 =
< g2.2013+01=
< 6.40E+00 =<
1.30E3+01
=<
7.40E3+OC0 Zn-65
<1.10E3+01
< 2.SOE3+01
< 3.OOE3+0I Zr-9S
< 7.30E3+OO I1.SOE+O0I1
< 1.30E3+0I Ru-103 5.9OE3+OO
< 1.1 OE+O0I
<1 6.20E3+OC Ru-106
< 4.OOE+01 =<
7.90E3+01 =
<1 5.90E3+O I
Cs-134
< 4.60E+OO
< I.IOE+OI
< 6.40E3+OC0 Cs-137
< 4.40E3+OO
< l.OOE+O I
< 7.70E+OO Ba-140
< 8.00E3+00 1.20E+01 1.20E3+OI La-140
< 9.2013+00;
<1 _.40E3+01 =_<
1.40E3+OI Ce-141
< 6.20E3+00 =<1 1.40E3+01 I
< 9.90E3+OO0 Ce-144 2.00E3+01 7<] 4.4-0E+01I
<1 3.60E3+OI
,Nuclide
~~~~~
1 -:'i'2A C
^
-~l' -'8-NOV
]6-DEC' :-
I-131 l<l 9.50E-01 I I <l 5.80E-OIl I
<1 8.20E-01 I
Sr-89
< 7.50E3+00 =<
8.30E3+OC
<1 6.0013+00 Sr-90 2.3 1E+00 +1-4.60E3-01 1.70E3+OC 1.20E+00 Be-7
< 4.50E3+01
< 6.70E3+01
< 4.30E3+OIi1 K-40 1.42E1+03 +1-S.SOE3+OI 1.4311+03 +1-7.50E3+01
=
1.42E+03l +/- l5.90E+O Il Mn-54
< 4.30E+00 _<1 7.60E3+OC0
< 5.60E+00l Co-58
< 5.40E3+00 =<
8.90E+OC0
< 5.3013+00l Fe-S9
< 1.60E+01
< 2.40E3+OI I.90E3+OI Co-60
< S.90E3+00
< 7.60E+00l
< 5.80E+00l Zn-65
< I.IOE+OI
< 2.50E3+0]
1.40E3+OI1 Zr-9
< 7.60E+00
=
-< _1.30E+O1
=
_< =.OOE3+OIll Ru-103 I<
5.40E+00 =
< 8.70E+00 6.00E3+OO
-l-0 Ru-106
< 4.70E+OI
< S.SOE+O1
< S.OOE3+OI Cs-134
< S.OOE3+OO
< 6.90E3+0(
< 5.6013+00:
< S.IOE+OO
< 7.40E3+0(
< 6.0013+00; Ba-140
< 9.90E3+00
< _1.30E3+01
< 9.4013+00l l
La-140 I.IOE+OI1
<1 1.50E+01
< I.IOE+OIl1l lCe-141
< I7.50E3+001
< I1.20E3+0]
< 8.20E+OO1 JCe-144 I<1 2.70E+01I
< I4.60E3+0]
<1 2.90E+01 Il C-33
Fermi2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 VEGETABLE ANALYSIS FP-1 (Indicator)
(pCi/kg wet)
Nuclide
[. '
22-JUL Broccoli 22-lUL Cabba 22-JUL Swiss Cha'rd' 1-131
< 4.20E+01 I I < 4.10E+01
<1 3.80E+O1 I
Be-7
< 3.70E+02
< 3.40E+02 1
< 3.40E+02 I
K-40 5.08E+03 +/- 5.90E+02 2.76E+03 +/- 3.1 OE+02 4.35E+03 +1-4.40E+02 Mn-54
< 7.20E+01
< 4.1OE+O1
< 3.30E+O1 Co-58
< 5.80E+01
< 3.60E+01 4.50E+O1 Fe-59
< 2.20E+02
< 9.20E+01
< 1.70E+02
=
< 5.70E+O1
< 5.50E+O1
< 6.30E+O1
=
Zn-65 1.30E+02
< 1.20E+02
< 1.20E+02 Zr-95 9.OOE+01 7.60E+01
< < 8.80E+O1
_=
Ru-103
< 4.30E+01
< 3.70E+01
< 3.30E+O1 Ru-106
< 4.30E+02 =
< 3.80E+02
< 2.30E+02 =
Cs-134
< 5.90E+O1
< 3.50E+01
< 4.20E+O1 Cs-137
< 6.20E+01
< 3.40E+O1
< 5.IOE+OI Ba-140
< 9.50E+01
< 5.80E+01
< 8.40E+O1 La-140
< 1.IOE+02
< 6.70E+O1
< 9.60E1 =
Ce-141
< 5.50E+O1
_=
< 4.60E+01
=
< 4.80E+O I =
Ce-144 2.OOE+02 1.60E+02 1.80E+02 FP-1 (Indicator)
(pCi/kg wet)
Nuclide I 19-AUG Cabbage 1
I 9-AUG Lttuce
'19-AUG Swiss Chard=
< 4.90E+O1
_I
< 2.90E+01
< 4.70E+O1 I
Be-7
< 3.20E+02
< 2.90E+02
< 4.30E+02 I
K-40 3.12E+03 +/- 3.1OE+02 2.86E+03 +/ 3.1OE+02 5.40E+03 +/- 3.70E+02 Mn-54
< 4.30E+01
=
3.80E+O1
< 4.E+1 Co-58
< 3.60E+01
< 3.70E+01
< 4.90E+O1 l
_l Fe-59
- .20E+02
< 7.20E+01 1.40E+02l Co-60
< 4.80E+01
< 3.20E+O1
< 5.90E+O1 Zn-65
< 1.60E+02 1I.OOE+02 1< 1.40E+02 I
Zr-95
< 5.90E+O1
< 5.90E+01
< 8.20E+01 Ru-103
< 4.OOE+01 3.20E+01
< 4.80E+OI1 l_l Ru-106
< 3.60E+02
< 2.50E+02
< 4.90E+02 l
Cs-134
< 4.50E+01
< 3.30E+01
< 5.30E+O1 Cs-137
< 4.50E+01
< 2.80E+01
< 4.90E+OI1 Ba-140
< 5.90E+01 4.70E+OI
< 5.70E+1 1
La-140
< 6.70E+01
< 5.40E+01
< 6.50E+01 l l
Ce-141
< 5.OOE+O1
< 3.90E+01
< 6.80E+01 l Ce-144
< 1.90E+02 1.30E+02
< 2.30E+02 l
C-34
. I
.i i
Fermi2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 VEGETABLE ANALYSIS FP-9 (Control)
(pCilkg wet)
.Nuclide 22-JUL Cabbage--j,
.'22-JULMoirse'Radish 22-JUL Swss Chard 1-131
< 4.50E+01 I < 2.30E1+01 I
< 4.40E1+OI I
Be-7 4.OOE+02 4.70E1+02 =
3.80E+02 K-40 4.29E+03 +/ _OOE+02 4.21E+03 +/- 5.30E+02 6.74E+03 +/- 5.90E+02 Mn-54
< 4.80E+01
=<_
5.60E+01 =
< 3.50E+0O Co-58
< 5.20E+01 6.OOE+01
< 3.60E+01 Fe-59
< 1.30E+02
< 2.30E+02
< 1.90E+02 Co-60
< 9.OOE+01
< 7.30E+0I
< 7.OOE+O I Zn-65
< 1.30E+02 =
1.20E+02
< 1.60E+02 Zr-95
< 9.30E+01
< 9.30E+01
< 8.20E+O1 _
Ru-103
< 5.OOE+O1
< 5.70E+01
< 4.60E+01 Ru-106
< 6.30E+02
< 4.70E+02
< 3.70E+02 =
Cs-134
< 3.90E+01
< 3.80E+01
< 5.30E+O1 I_=_=__
< 4.40E+01
=
< 6.60E+01
< 4.50E+OI =
Ba-140
< 6.20E+O 1.IOE-+02
< 8.90E+O1 La-140
< 7.20E+01
< 1.30E+02
< 1.OOE+02 Ce-141
< 7.30E+01
< 6.70E+01
< 4.90E+0I Ce-144
< 2.50E+02 =1-
< 2.20E+02 1.80E+02 =
FP-9 (Control)
(pCi/kg wet)
Nuclide?
-' 19-AUG 'Lettuce" 1
19-AUG Red Cabbage:
1-131
< 3.70E+OI_
<.l 3.10E+O1 Be-7
< 3.00E+02 2.60E+02 =
K-40 2.79E+03 +/ 2.40E+02 4.84E+03 +/- 3.OOE+02 Mn-54
< 3.90E+01
< 3.30E+OI1 Co-58
< 3.70E+0 3.OOE+01 Fe-59
< 9.10E+01 1
d 8.50E+01 Co-60
< 4.20E1+0I
=
<I 4.50E+OI
=
Zn-65
< 1.40E1+02 1.20E+02 Zr-95
< 6.60E+01
< 5.30E+OI Ru-103
< 4.OOE+01
< 2.90E+OI Ru-106
< 3.20E+02
< 3.20E+02 _
Cs-134
< 4.001E+01 3.30E+O1
=
< 3.70E+OI 3.40E+O l-Ba-140
< 4.70El+01
< 4.001E+O I La-140
<l 5.40E+01
< 4.60E+01 Ce-141
<_ 4.80E1+01
=
4.10E+O1 Ce-144
<l 1.70E+02 1.60E+02 =
C-35
Iermi 2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 DRINKING WATER ANALYSIS DW-I (Indicator)
(pCiliter)
Nuclide? {.'
30-3AN
- 4:
I
- FEB. -_____
- -__30-__
GR-B
< 2.90E+00
< 3.1 OE+OO
< < 3.20E+00 Sr-89
< 7.40E+00
< 5.80E+00,
< 7.1OE+00 Sr-90
< 1.70E+00 1.60E+00 1.60E+0OO Be-7
< 4.90E+0 5;0E+01
< 4.00E+01 K-40
< 8.OOE+01
< 9.60E+01
< 7.20E+01 Mn-54
< 4.902+00
< 5.20E+00
< 4.30E+00 Co-58
< 5.1l1OE+00
< 6.70E+00
< 4.40E+00 Fe-59
< 1.30E+01
< 1.70E+01
< 1.500E+01 Co-60
< 6.30E+00 =
< 7.1OE+00
< 4.60E+00 I
Zn-65
< 2.30E+01 1.30E+01
< 9.90E+00 Zr-95
< 9.60E+00
< 1.00E+01
< 8.80E+00 Ru-103
< 6.10E+00
< 6.1OE+00
< 5.80E+00 Ru-106 4.30E+01
< 5.90E+01
< 4.50E+01_
Cs-134
< 6.40E+00=
< 7.10E+00
< 5.30E+00O Cs-137
< 5.50E+00
< 6.50E+00
< 4.70E+00 Ba-140
< i.lOE+01 1.20E+01 1.20E+01 La-140 1.30E+01 1.40E+01
< 1.40E+O I_=
Ce-141
< 9.20E+00 =
8.10E+00 =
< 6.902+00 Ce-144 j < 2.90E+01 I
_I__
2.90E+01 2.20E+O I <
Nuclide j
.27-AR i § '
25-MY 29-JUN._______
GR-B I
4.90E+001 +/- 1.20E+00 I 4.002+00 +11.10E+00 I 3.18E+00+/ 19.80E-01 Sr-89
< 6.20E+00 =
< 8.20E+00=
< 8.302+00 I
< 1.60E+00 1.70E+00 1.80E+001 I
Be-7
< 3.80E+01
< 4.80E+01
< 2.902+01 l I
< 6.40E+01
< 8.80E+01
< 6.302+01 Mn-54
< 4.30E+00
< 5.60E+00
< 3.50E+00 Co-58
< 4.50E+00l
< 6.20E+00
< 4.30E+00 Fe-59 1.50E+01 l 1.90E+01
< 1.30E+01 Co-60
< 5.OOE+00
< - 6.40E+00
< 4.102E+00 Zn-65
< 1.10E+01 l 1.70E+01 =
< 9.602+00 Zr-95
< 7.40E+00
< 9.802+00
< 7.20E+00 _
Ru-103
< 5.10E+00
< 6.80E+00
< 3.70E+00 Ru-106
< 4.50E+01l
< 5.30E+01l
< 3.50E+01_
Cs-134
< 4.40E+00
< 6.60E+00
< 4.70E+00 Cs-137
< 4.60E+00
< 6.30E+00
< 3.80E+003 I
Ba-140
< 1.12OE+
01
< 9.10E+00
< 7.30E+00 La-140
< 1.30E+01 l
< 1.10+011
< 8.30E+00 Ce-141
< 7.30E+00
< 1.10E+01
< 5.202+00 Ce-144
< 2.50E+01 l
< 3.40E+01
< 1.60E+01 l C-36
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 DRINKING WATER ANALYSIS DW-1 (Indicator)
(pCiAiter)
'Nuclide: 1
-27.JUL
[
- 31-iAUG'--i'.
l
- 'i 28-SEP GR-B
< 3.OOE+00 l 4.80E+OO +/- L.I1OE+OO 3.30E+00 +/- 9.70E-OI Sr-89
< 8.70E+00
< 8.9OE+00 I
<1 2.70E+OO Sr-90 1.80E+00l 1.70E+00
<1_ 1.70E+OO =
Be-7
< 4.50E+01
< _6.10E+01 3.90E+O1 K-40 c 7.60E+01
< 8.90E+01 6.70E+O1
=
< 5.10E+00
< 5.30E+00 4.90E+OO Co-58
< 5.20E+00
< 6.30E+00
< 4.60E+OO Fe-59 1.60E+01 I=
< 2.OOE+01 1.20E+O1
=
< 4.70E+OC0
< 5.80E+00
< 5.40E+OO Zn-65 1.30E+01
< 2.50E+O1
<=_ 1. I.OE+OI I Zr-95
< 1.1OE+O1 1.10E+01
< 8.50E+OO Ru-103
< 6.10E+W0
< 6.70E+00 4.90E+OO I
Ru-106
< 5.40E+01
< 5.70E+01 4.30E+O1 Cs-134
< 5.lOE+OC
<1 5.70E+OO
< 5.IOE+OO =
< 5.20E+00
< 6.80E+00 4.70E+OO Ba-140 1.20E+01 1.20E+01
< 6.30E+OO_
La-140 1.40E+01
< 1.30E+01 7.20E+OOl Ce-141
< 8.40E+00
< 9.80E+00 7.50E+OO_
Ce-144
< 3.10E+01 =
< 3.30E+O1 I
< 2.50E+O1I l Nuclide
,28-OCT l
30-NOV-
.28-DEC' GR-B I
3.90E+OO +/- l.OOE+OO I < 3.30E+00l lI
<1 3.10E+OOl Sr-89
< 9.OOE+00=_
< 5.30E+00
<1 5.70E+OO=
Sr-90 1.80E+00
< 1.60E+00
< 1.40E+00 Be-7
< 4.20E+01
< 3.80E+01
< 4.OOE+01 K-40
< 7.10E+01
< 7.60E+01 7.30E+O1 Mn-54
< 5.80E+oo
< 5.1OE+OO
< 5.30E+OO Co-58
< 4.10E+00
< 4.30E+OO
< 5.50E+O
=_
Fe-59 1.50E+O1
< 1.50E+OI 1.40E+O1 Co-60
< 5.40E+00
< 4.80E+00
< 5.20E+O0 Zn-65
< 9.80E+OO I.OOE+O1
< 1.50E+O1 Zr-95
< 9.70E+00
< 7.80E+00 8.OOE+OO =
Ru-103
< 5.OOE+OO =
4.70E+OO
< 6.20E+O
=_
Ru-106 4.OOE+01
< 4.20E+01
< 4.60E+O
=
Cs-134
< 4.90E+00
< 5.20E+00 l 5.20E+O0 Cs-137
< 4.60E+00
< 4.80E+OO
< 5.1OE+OO Ba-140 I.OOE+OI
< 8.80E+00
< 8.90E+00 La-140 1.20E+O1
<1
.OOE+O1 I
<_ I.0E+01 Ce-141
< 4.20E+00
<1 6.50E+00It
< 9.40E+OO I
Ce-144 1.80E+01
< 1.90E+O1 I_
I <1 2.50E+
l
_I C-37
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 DRINKING WATER ANALYSIS DW-2 (Control)
(pCi/liter)
- Nuclide 4 30-wAN -
l FEB 30-MAR-1 GR-B
< 3.OOE+OO
=I_
3.57E+OO +/- 9.60E-01
< 2.90E+OO _
Sr-89
< 7.50E+00
< 6.10E+00I
< 7.30E+OO I
Sr-90 1.70E+00 1.70E+00 1.70E+OO Be-7
< 4.50E+01
=
< 3.90E+01
=
< 4.50E+O _
K-40 8.60E+01
< 4.60E+01
< 6.90E+O I Mn-54
< 5.70E+00
< 4.1OE+OO=
< 4.30E+OO Co-58
< 6.60E+00
< 3.70E+OO
< 5.OOE+OO Fe-59 1.60E+01 1.30E+0l 1.30E+O I Co-60
< 6.40E+00
< 5.30E+00
< 4.50E+OO Zn-65
< 2.20E+01
< c 9.00E+OO
=
1.1OE+OI
=
Zr-95 1.IOE+O1
< 7.40E+00
< 8.30E+OO
=
Ru-103 7.1OE+OO
< 4.70E+00
< 6.1OE+OO Ru-106
< 5.30E+01
< 4.1 OE+O I
< 4.60E+O I Cs-134
< 6.60E+00
< 4.40E+00
< 4.90E+OO Cs-137
< 5.20E+00
< 4.40E+00
< 3.90E+OO
=
Ba-140
< 1.IOE+O1I
< 5.60E+OO 1.OOE+OI La-140 1.30E+01
< 6.50E+OO
< 1.IOE+OI1 Ce-141 9.OOE+00 =
< 6.30E+00 =
< 7.60E+OO Ce-144
< 3.10E+01 I
< 2.40E+01
=
< 2.30E+OjI Il I
Nuclide APR
- 1.
25-MAY 29-1UN:-
GR-B
< 3.1OE+OO 4.20E+OO +/- 1.1 OE+OO 3.OOE+OO Sr-89
< 6.70E+00
< 8.10E+00
< 7.10E+OO __
Sr-90 1.80E+00 =
1.70E+00 1.60E+OO Be-7
< 5.40E+01
< 4.1OE+OI
< 5.OOE+OI K-40
< 9.50E+01
< 7.70E+01
< 7.50E+O1 l Mn-54
< 5. l OE+OO
< S.50E+OO 6.OOE+00_
I____
<. O Ei O,
Co-58
< 7.40E+00
< 4.60E+00_
< S
_.__+0 Fe-59
< 1.50E+OI=
1.40E1+01 1.60E+01 l Co-60
< 5.70E+00
< 6.40E+00
< 5.50E+00 Zn-65
< 1.20E+01
< 1.IOE+01 1.60E+I01 Zr-95
< 1.IOE+01
< 8.40E+00 1.20E+I0 l Ru-103
< 6.70E+00
< 5.20E+00
< 8.30E+00_
Ru-106
< 4.90E+01
< 4.20E+01
< 5.90E+01 l Cs-134
< 5.40E+00 =
< 5.302+00
< 6.30E+00l Cs-137
< 5.90E+00 4.902+00
< 5.80E+00 l Ba-140 1.20E+01
< 8.70E+00
- 1. IOE+O I La-140 1.40E+01
< 1.00E+01
< 1.30E+01 Ce-141
< 9.60E+00
=0_
< 6.1OE+001 I <1 7.20E+00 Ce-144 3.10E+01 =
< 2.30E+01 lI_
I < 3.00E+01 l C-38
Fermi 2-2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 DRINKING WATER ANALYSIS DW-2 (Control)
(pCi/liter)
Nuclide 27-lUL, _
31-AUG
]
28-SEP GR-B
< 2.90E+00 4.00E+00, +/- 1.OOE+O0 2.06E+00 +I-9.90E-O I Sr-89
< 8.20E+00
< 8.70E+00
< 2.60E+00 Sr-90 1.70E+00 1.60E+00 =
1.70E+OO =
Be-7
< 3.70E+01 3.60E+01
< 4.00E+OI1 K-40
< 7.50E+O1 I
< S.lIOE+0I
=
< 7.1 OE+OI I Mn-54
< 4.50E+00
< 2.70E+00
< 4.70E+0O Co-58
< 5.OOE+0O
< 3.70E+OO
< 5.OOE+O0 Fe-59
< 1.50E+3O I
< 9.40E+00 1.20E+O I Co-60
< 6.1 OE+OO =
< 3.30E+00
< 4.80E+OO =
Zn-65
< I.90E+01 =
1.1OE+01
< 1.20E+0 I
_=
Zr-95
< 8.OOE+00
<1 7.20E+00
< 7.60E_+OO Ru-103
< 5.OOE+OO_
< 4.70E+00
< 5.20E+O0O_
Ru-106
< 4.20E+01
< 3.10E+01
< 4.10E+OI Cs-134
< 5.20E+00 =
< 3.80E+00 =
< 4.80E+O0
=
< 5.OOE+00
< 3.40E+00
< 4.60E+O0 Ba-140 1.1OE+01 8.40E+00
< 7.30E+OO La-140 1.30E+01
< 9.70E+00
< 8.40E+00, Ce-141
< 7.30E+00
=
< 7.40E+00
=
___=
8.90E+00 0_
Ce-144
<1 2.30E+01 I
< 2.50E+01
=
< 2.50E+
Nuclide 28-OI 30-NOV 28-DEC-GR-B I < 2.70E+001 IO < 2.90E+00j IlI l
3.90E+00 +/- 1.IOE+
l00 Sr-89
< 5.70E+00
< 4.20E+OC
=
< 6.80E+O0 =
Sr-90 1.lOE+OO 1.40E+O0C 1.80E+O0 _
Be-7
< 3.70E+01
< 3.80E1+01
< 3.30E+0I K-40
< 5.60E+01 7.50E+O1
< 5.50E+0.__.._-
< 4.30E+00
< 4.30E+OC 4.OOE+0C _
Co-58
< 4.80E+00 =
< 4.60E+OC =
4.30E+O0
=__
Fe-59 1.60E+01 =
1.40E+01 =
< 2.60E+I01 Co-60
< 6.20E+00
< 6.00E+00
< 3.70E+OOl Zn-65 9.00E+OO 1.I1OE+0 I
< 1.40E+O l_
Zr-95.
< 7.80E+00
< 7.40E+00
< 7.10E+13 Ru-103
< 5.30E+OO
< 4.90E+00
< 4.80E+0O Ru-106
< 4.30E+01 =
< 4.50E+01
< 3.80E+0 l Cs-134
< 4.70E+00
< 4.00E+O0
< 4.40E+OO Cs-137
< 5.30E+00
< 4.70E1+00
< 3.80E+O0 Ba-140 9.80E+00
< 8.40E+00 9.30E+O0I La-140 1.IOE+OI1
< 9.70E+O0l 1.I1OE+0O I Ce-141 1.OOE+O1
< 6.70E+00 7.10E+OO_
Ce-144
< 2.10E+01 l1 I
2.20E1+011 2.30E+O I I C-39
Fermi2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 SURFACE WATER ANALYSIS SW-2 (Control)
(pCi/liter)
Nuclide.
l - -. i - S 30-J--AN;:
-_ ; ;l
.- 24-FEB.
5 30-R -
Sr-89
< 7.80E+00
< 5.70E+00 Ij
< 7.80E+OO _
Sr-90 1.80E+00 1.60E+O0_
< 1.70E+O0 Be-7
< 3.60E+01
- < 4.40E+01
< 3.40E+OI K-40
< 8.20E+01 9.OOE+01
< 7.90E+O l Mn-54
< 4.30E+O0
=0_
< 5.30E+00
< 4.40E+O0 Co-58 4.30E+00 =
< 5.60E+00
< 4.30E+00O Fe-59 1.30E+01 1.60E+01 I
1.20E+O I Co-60
< 5.1OE+OO
< 6.50E1+00
< 4.80E+00 Zn-65
< 9.70E+00 1.20E+OI 1.1 OE+O I Zr-95
< 7.70E+00
=
< 1.OOE+0O I
_=-
< 8.1OE+00
=
Ru-103
< 4.60E+00
< 5.30E+00
< 4.30E+OO Ru-106
< 4.00E+01
< 4.50E+01
< 3.70E+OI Cs-134 4.80E+00 =
< 5.70E+00 =
< 4.40E+OO =
< 4.60E+oo
< 5.20E+00 l
< 4.OOE+OO
=00 Ba-140 9.90E+00
=
< 9.10E+00 =
- 8. IOE+00
=
La-140
< 1.IOE+O I I.OOE+OI
< 9.40E+O0O Ce-141
< 6.1OE+00
< 7.50E+00
<1 5.30E+O0 Ce-144
<j 2.20E+O I I I < 2.50E+01
< 2.OOE+O I Nuclide.--. l'-
.`-; 27-APR, '- -
25-MAY-29-JUN --
Sr-89 I
6.30E+00
< 7.20E+00 I
<1 6.20E+00 l
Sr-90 1.60E+0O l.50E+O0 1.40E+OO Be-7
< 4.10E+01
< 3.70E+01
=
l < 6.70E+OIl l1 K-40
< 7.80E+01 =
< 6.80E+01 =
< 8.40E+Olj r__
< 5.lOE+OO
< 4.80E+00
-0_
< 7.20E+O0 l
Co-58
< 5.40E+00
< 4.20E+00 6.90E+O0 Fe-59 I.70E+01 1.40E+01
< 2.10E+Ol Co-60
< 5.30E3+OO
< 5.50E+0 I <I 8.10E+OOI Zn-65
< 2.00E+OI
=
I.90E+01 1.901E3+OI1 Zr-95
< 8.00E+00
< 7.40E+00
=
1.40E+01 Ru-103
< 5.50E+OO_
< 4.60E1+00 8.40E+00 Ru-106
< 4.20E+0l1
< 3.80E1+01
< < 7.20E+01 Cs-134
< 4.70E+00
< 4.30E+00 I <
8.101_+00 Cs-137
< 4.80E+00
< 5.501E+OO
=
_ <[ 8.1O0E+O Ba-140 I.IOE+01
< 6.90E+OOl 1.OOE+0Ol l_
l La-140
< 1.30E+01 l
< 7.90E+00 1.20E+0Ol _
Ce-141
< 7.80E+00l I_
I < 6.40E+00 I <1 l.OOE+0Ol Ce-144
< 2.50E+01 II
< 2.40E+OI I
<1 3.90E+Ol l l
C-40
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 SURFACE WA.TER ANALYSIS SW'-2 (Control)
(pCi/liter)
Nuclide:
l ': -'.-27-UL 0
- - ' :<- AUG
',-l'-
i-SEP
"~,
Sr-89 I<
9.30E3+OOj0
<1 9.60E3+00 I<1 2.20E3+OO I
Sr-90 1.90E3+00 1.70E3+OO0 1.SOE3+OO Be-7 8.00E3+01
< 4.80E+01
< 5.40E3+0I K-40
< 8.00E3+01
=<
8.70E3+01 =<
7.70E3+Ol Mn-54
< 7.1 OE+OO
< 5.20E3+00
< 5.40E3+OO Co-58
< 9.00E3+OO
< S5.SOE+OO
< 6.20E3+OO Fe-59 2.50E3+01
< 2.00E3+01 1.30E3+OI1 Co-60
=
8.70E3+OO=0 5.90E3+00 _<
6.50E3+O00 Zn-65
< 2.90E+01 =<
1.40E+01l 1.40E3+OI Zr-9S 1.20E3+01
< 8.40E+00
< 9.70E3+OO Ru-103
< 8.80E+00
< 6.30E+00 6.50E3+OO Ru-1 06 6.90E+01
< 4.50E+01l
<1 5.40E3+O I
Cs-134
< 7.80E3+00
=
< 6.00E2+00
< 5.90E+OO Cs-137
< 7.80E3+00 =<
6.20E1+00 =<
6.00E+OO0 Ba-140 1.30E3+01
< 1.30E3+01
-< 9.00E+OO, La-140 1.40E3+0I
< I1.SOE3+0I I.OOE+O I JCe-141 I
E.30E3+01
=<1 8.30E3+00 8.60E3+O00
=
Nulde'-l O..8CT,'.
-¢-3-O
- - DEC4 Sr-89 I <l 7.50E3+00l I <l 4.50E3+OO I
<1 6.2013+0 I
Sr-90 1<t 1.6013+00 1'
1.50E+00l 1
1.6013+00:
Be-7
< 5.30E3+01
< 5.40E3+01 =
< 3.60E+OI1 K-40
< 9.40E3+01
< 9.40E+01l
< 6.50E+0 Mn-54
< 6.50E3+001
< 6.80E+00 =<
3.5013+00 Co-58 6.3013+00t
< 6.50E+00 _<
4.5013+00=
F-59 1.3013+01= _
=
I 0 1.90E+I_
I. IOE1+O I=
Co60
< 7.1 013+00
< 7.30E+00 =
< 5.60E3+00=7 Zn-65 1.20E+01 l<
1.70E3+01
< 9.50E+0 Zr-95 I.OOE+01I
< I.IOE+OI 8.2013+0 Ru-103 6.30E3+003 8.60E3+00
< -4.7013+0 Ru-106
< 5.3013+01l==
7.10E3+01 =
=<
3.4013+01=
X Cs-134
< 6.20E3+00 6.80E+001=
< 3.80E3+oo I
Cs-137 5.40E3+003
< 6.40E+00
< 4.70E+OO Ba-140 1.2013+01 1.20E3+01
< 9.80E+0 La-140 1.40E+01I 1.40E3+OI I.IOE3+OI Ce-141=
9.3013+0031
=
X
< 9.7g01+00 _10
<1 6.90E+00=
Ce-144 I.0+1
<- 3.20E3+017I
<1 2.10E3+OIl
.C41
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 SURFACE WATER ANALYSIS SW-3 (Indicator)
(pCi/liter)
Nuclide
30-JAN 25FEB'>WJ 30-MAR ______]
Sr-89
< 7.60E+o0 6.OOE+O0 c 6.70E+OO Sr-90
< 1.70E+O0 1.70E+O0 1.30E+OO Be-7
< 3.70E+O1 7.30E+O1
<1 4.50E+O1 K-40
< 8.80E+01
- 1. IOE+02
< c 7.90E+0I Mn-54
< 4.50E+OO
< 8.70E+O0
< 5.30E+OO Co-58
< 5.30E+00
< 8.30E+OO 5.90E+OO Fe-59 l.50E+O1
< 2.50E+O1 1.70E+O I Co-60
< 4.80E+00
< 9.40E+O0
< 6.50E+O0 Zn-65 1.1OE+O1
_=
< 1.70E+01
=
< 1.40E+O I_=
Zr-95
< 8.60E+00
< 1.30E+01
< 9.50E+O0 Ru-103
< 5.20E+00
< 7.80E+00
< 6.60E+O0 Ru-106
< 3.80E+O1
< 6.50E+01
< 5.OOE+OI Cs-134
< 5.OOE+00 =
8.OOE+O0
< c 5.90E+O0 =
< 4.80E+o0o 8.70E+O0 I
< 6.30E+OO Ba-140 I.OOE+01 1.20E+O1I
< 1.20E+O1 La-140 I.IOE+O1
=<
_1.40E+OI =<'_
c 1.40E+OI =
Ce-141
< 8.00E-+OO I.IOE+01 I
< 9.20E+-0O Ce-144 1.90E+01 =
< 3.90E+01
=
< 3.20E+O1
=
Nuclide' l-27-APR '
I' 25-MAY.-
-2;9-JUN 1
Sr-89 I < 6.40E+001 I <
8.50E+O00 j
<1 7.30E+00_
Sr-90 I <
.70E+001
< I.80E+c0 1.60E+o0 Be-7
< 4. 1OE+OI
< 3.40E+O1 5.40E+O1 _
< 6.90E+OI
< 7.30E+01
< 8.00E+01 Mn-54
< 5.OOE+00
< 4.40E+00
< 6.40E+00 Co-58
< 5.OOE+OO
< 4.30E+O0 6.60E+OO Fe-59
< c
.30E+O1 1.40E+O1 I.50E+O1
__l Co-60
< 4.90E+00
< 5.60E+oo
< 6.20E+OO Zn-65
< 2.20E+01 1.20E+01
< 2.20E+01 Zr-95
< 7.30E+OO
< 7.90E+O0 I.IOE+O I Ru-103
< 5.40E+00
< 4.60E+-00
< 6.50E+00 Ru-106
_< 4.40E+01
< 3.70E+01
< 6.OOE+01 Cs-134
< 5.50E+OO
< 4.80E+00
< 6.50E+00 Cs-137
< 4.70E+00
< 4.90E+00
< 7.20E+0 Ba-140
< 8.90E+00
< 7.OOE+OO 1.1OE+O La-140 I.OOE+OI1
< 8.10E+00_
1.30E+01 Ce-141
< 8.30E+O I_
< 5.90E+00
< 9.70E+OO0 Ce-144
< 2.40E+01l
< 2.10E+01l
< 3.50E+01l C-42
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 SURFACE W"ATER ANALYSIS SW-3 (Indicator)
(pCifliter)
Nuclide-27-JJ 31-AUG'.
28-SEP Sr-89
< 8.40E+00
< 9.60E+OO I
< 2.40E+OO Sr-90 1.80E+OO 1.80E+00
< 1.60E+OO Be-7
< 6.1OE+01
< 5.40E+01
< 4.70E+O1 _
< 9.40E+01
< 9.20E+01
< 8.40E+O I Mn-54
< 6.30E+OO
< 5.IOE+OC=
< 5.50E+OO Co-58
< 8.60E+00 6.40E+OC
< 5.80E+OCI Fe-S9 1.90E+O1
< 2.OOE+01
< 1.40E+O l Co-60 7.20E+00
< 6.50E+OC
< 4.80E+OO Zn-65
< 2.80E+01
< 2.00E+01 1.30E+O1 Zr-95
< 1.IOE+O1
=
< 1.IOE+O1
< 9.30E+OO Ru-103
< 8.60E+00
< 7.1OE+OC
< 5.90E+OO Ru-106
< 6.OOE+01
< 5.80E+O1
< 5.50E+O1 Cs-134
< 7.1 OE+OO
< 6.60E+W0 6.1OE+OO Cs-137
< 6.1OE+OO
=
5.70+0E
< 4.70E3+OO _
Ba-140
< 1.30E+01
=
< 1.30E+01
< 7.90E+OO =
La-140 1.50E+O1 I < 1.50E+01
< 9.10E+OO Ce-141
< 9.30E+00 I_ <1 9.90E+OC
< 7.80E+OO _
Ce-144
< 4.1OE+O1
< 3.40E+01
< 3.1OE+O I Nuclide'
- OC]>
K 30-NOV<
V 28-DECr Sr-89
< 8.1OE3+OO
< 5.50E+00 I
<1 6.20E+OO lI Sr-90 1.60E+00
< 1.70E+00 1.60E+OO Be-7 4.40E+O1
< 5.OOE+O1 3.30E+01 K-40 8.OOE+OI
< 8.90E1+01 6.00E+O l_
< 5.40E+00
< 6.10E+00 4.OOE+OO Co-58
< 5.70E+00
< 6.50E+00 4.50E+OO Fe-59
< 1.60E+01
<_ 1.80E+O1 I.OOE+O1 l l_
< 5.30E+00
< 7.80E+00 3.90E+OO I
Zn-65 I.IOE+OI =
< 2.OOE+OI
< 1.OOE+O1 l
_l l
Zr-95 I.OOE+O1
< 1.30E+01
__< 7.20E+OO l__
Ru-103 6.OOE+00
< 7.30E+00 l < 4.90E+OO Ru-106
< 5.OOE+O1
< 5.90E+01 =
3.50E+O1 l l
Cs-134
< 5.90E+00
< 6.60E+00=1
< 3.90E+OO l
< 4.70E+00
< 6.OOE+OO =
< 4.10E+OOl Ba-140 1.30E+O1
< I.IOE+O1 l < 9.1OE+OOl l
La-140 1.50E+01 1.30E+O1 1.OOE+O1 Ce-141 1.20E+O1 I_ 1.IOE+O1 I <1 5.40E+oo Ce-144
< 2.40E+O1 =II I < 3.20E+O1 =II I < 2.10E+O1 l C-43
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 DRINKING AND SURFACE WATER QUARTERLY COMPOSITE SAMPLES Tritium (pCi/liter)
IlStation J F
1
.'stQuarter-.
-,:-Second.Quarler s-1I DW-1 1.30E+03 T
I < 1.70E+03 T
I DW-2
<1 1.30E+03 1.70E+03 SW-2 I <
1 I1.OOE+03 1.70E+03 SW-3 I
<1 I 3
=__
<1 1.70E+03
=
Station '`'-j
-Third Quarter -.:-:-
i Fourh urer I
I I
IL I _
DW-1
<l 1.1OE+03 _
1.OOE+03 DW-2 1.20E+03 =<
I.OOE+03 =
SW-2 I.20E+03 I.OOE+03
__=
SW-3
< 1.20E+03 I
I 1.OOE+03 I
C-44
Fermi2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 GROUNDWATER ANALYSIS GW-1 (Indicator)
(pCi/liter) l-Nuclide:l' nFirstQuarter
-'-.Second Quarter Be-7
< 4.40E+ 0I I I <1 4.10E+OI I
< 5.40E+01
< 7.20E+1OIl Mn-54
< 4.40E+00-
< 5.30E+OO, Co-58
< 4.70E+0, 5.30E+00X _
Fe-59 1.30E+O IlI_
I < 1.70E+01 Co-60
< 3.90E+00_
< 4.OOE+00 Zn-65
< 1.20E+01
< 9.70E+O0 Zr-95
< 9.10E+00
< 1.OOE+O1 Ru-103
< 5.30E+O0
=__
< 5.50E+00 =
Ru-106
< 4.40E+01
< 3.90E+O1 Cs-134
< 4.60E+0o
< 4.70E+00 Cs-137
< 5.50E+00
< S.OOE+00i Ba-140 1.10E+1 _
< 1.3 i
La-140 1.30E+01 1
1.50E+01_
Ce-141
< 7.90E+00
< 8.40E+O Ce-144
< 2.80E+01
< 2.40E+OIl H-3 1.1OE+03 1.20E+031 I
Nuclide t
Third Quarter!
'IL' Fourth Quarter Be-7
< 4.90E+01 I
< 4.30E+01 K-40
< 7.OOE+01
< 5.90E+O 1 Mn-54
< 4.70E+00 =
< 5.30E+OC Co-58
< 5.20E+00
< 6.30E+00 Fe-59 1.70E+01
< 1.90E+0
=
< 7.1OE+OO
< 6.20E+00 Zn-65
< I.50E+01 1.30E+O1t Zr-95
< 1.OOE+0I 9.00E+O0 Ru-103
< 7.OOE+00
< 6.30E+00_
Ru-106
< 4.90E+01l
< 5.20E+01]I Cs-134
< 6.50E+00
< 6.20E+OO Cs-137
< 6.40E+00
< 6.10E+00 Ba-140
< 9.90E+00
< 1.20E+0I 1 La-140 1.IOE+O I
< 1.40E+OI Ce-141
< 9.10E+00
< 9.00E+-00, Ce-144
< 3.40E+01
< 2.90E+O1 =
< 1.1OE+03 I <
1.30E+031 C-45
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 GROUNDWATER ANALYSIS GW-2 (Indicator)
(pCi/liter)
INuclide>'l;---'
First Quarter :;
- ;'SecondQuarter Be-7
< 4.50E+O1
< 4.40E+O I K-40 8.20E+01 =
< 7.30E+OI
=
< 6.40E+00
< 4.80E+O0 Co-58
< 6.70E+00 =
< 4.90E+O0
=
Fe-59 1.70E+0]
1.80E+01 Co-60
< 7.50E+00
< 6.1OE+0O Zn-65 1.20E+01
< 1.30E+O1 Zr-95 IOE+O1
=I _
< 9.90E+O0 Ru-103
< 5.40E+00 =
< 5.70E+O0
=
Ru-106
<_ 5.20E+01
< 5.20E+OI _
Cs-134
< 5.90E+00
< 5.80E+00 Cs-137
< 5.10E+00 _
< 5.80E+Ot Ba-140
< 1.30E+01
=
< I.OOE+O1 =
La-140
< 1.40E+01 _
1.20E+O1 _
Ce-141
< 8.40E+00
< 8.60E+O0_
Ce-144
< 2.90E+0 I
< 3.OOE+O1 =
H-3 1.1 OE+03
<lI 1.20E+0
=
Nuclide *-
' Thid Qu' lQuarter Be-7
<j 5.80E+O1 I < 6.20E+O1 _
<l 9.20E+01
< 9.80E+OI Mn-54
<l 5.50E+O
<1 6.40E+00 Co-58
< 6 0 8.10E+OC
=-
Fe-59 2.30E+01
< 2.40E+0I
=
<l 5.30E+00
< 1.OOE+01 Zn-65
<1 1.30E+O1
=
< l.90E+O1 =
Zr-95
<1 1.30E+01 1.50E+01 Ru-103
<1 6.40E+O0
=
< 8.SOE+00 =
Ru-106
<1 4.50E+01
< 6.70E+0I Cs-134
<1 7.40E+00
< 6.50E+OO I
<I 5.10E+OC
< 5.90E+00 Ba-140 1.lOE+O1 l < I.IOE+OI La-140 1.30E+01 =
l <l 1.30E+01 =
Ce-141
< 9.80E+00 -
_l
< 1.1IOE+O1 Ce-144
<l 2.80E+01 l
<1 3.80E+O1 H-3
< 1.IOE+03l I
<1 1.30E+03 =
C-46
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 GROUNDWATER ANALYSIS GW-3 (Indicator)
(pCi/liter)
-i INuclide:
4
>1 First QuarterirI:
i
.diX --. Second Quarter Be-7
< 3.80E+0O1
< 4.40E+O1I K-40
< 9.20E+01
< 7.50E+O1 Mn-54
<l 4.90E+00 =
< 4.80E+
OC Co-58
<' 6.10E+00
< 4.40E+0O
=
Fe-59
< 1.50E+O I
< 1.80E+O I Co-60
< 6.30E+00 =
< 6.10E+00 =
Zn-65 1.30E+O1 1.20E+01 =
Zr-95
< 8.40E+00 =
< 8.30E+O0
=
Ru-103 6.OOE+00
< 5.80E+00 Ru-106
< 5.20E+01
< 4.10E+01 Cs-134
< 6.70E+00
< 4.40E+00 Cs-137
< 6.10E+00
<__ 4.50E+O(
=
Ba-140
<- 1.30E+01
< 1.20E+O1 La-140
< 1.50E+01
=
1.40E+01O Ce-141
< 8.50E+O0
< 5.50E+00 Ce-144
< 3.40E+01j
< 2.40E+OI H-3
<I 1.1OE+03 I
<1 1.20E+3 =E Nuclide 'Il T
irdQuarur FourthQuarter Be-7
< 5.30E+O1
-< 5.20E+0 I K-40 9.OOE+01 =
8.30E+O1 l
<J 6.70E+00 _
=
<l 5.90E+00 Co-58
<l 7.30E+O0
<l 6.OOE+00_
Fe-59
<4 1.60E+01_
< 1.70E+l l
<l 7.30E+00 _
<_ 6.70E+00 Zn-65 1.60E+OI I.O1E+OI Zr-95
<r 1.10
_E+01_
1.20E+OI L T___
Ru-103
<j 6.90E+00 T < 6.60E+O0 1
1 Ru-106
<j 4.60E+01 l < 5.30E+O1l Cs-134
< 7.20E+00 _
6.30E+OO l
<1 7.1OE+00 _
< 5.60E+0O i _
Ba-140
< 7.50E+00
< 1.30E+01 La-140
< 8.60E+OO 1.50E+O1 Ce-141 1.OOE+O1 l l < 9.10E+00 l
Ce-144
< 3.30E+01 l
'l 2.90E+01 l
_l H-3
< 1.IOE+03
<_ 1.30E+03 l
C-47
Fermi2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 GROUNDWATER ANALYSIS GW-4 (Control)
(pCi/liter) l Nuclide.l
- iT
- First Quarter l> -Second Quarter Be-7 I <
4.10E+011 _I1
<1 4.80E+Ol I
< 7.OOE+01 I <1 7.40E+O i I=
< 5.10E+00
< 5.30E+O(
Co-58
< 6.1OE+OO_
< 6.20E+OC0 Fe-59
< 1.40E+01 1.40E+O ]
< 6.20E+00
< 5.40E+OC _
Zn-65
< 1.30E+01 1.20E+O i=
Zr-95 1.1OE+O I 1.OOE+O1 Ru-103
< 5.OOE+00
< 6.1OE+i-OO Ru-106
< 4.40E+O1
< 3.80E+O I Cs-134
< 6.30E+00
< _ 5.50E+00 =
< 5.20E+00 =
< 4.70E+OO Ba-140
< 9.40E+00 1.30E+OI l La-140 I.IOE+OI 1.50E+0 Ce-141
< 7.60E+00
< 8.90E+O00 Ce-144
.60E+OO _
< 2.70E+Oj _
< I1.1 OE+031
< 1.20E+03 I
Nuclide,1;:-;
-Third Quarter 4,
- -Tourth Quarter-
Be-7
< 4.10E+01l l
l <I 2.61+
I K-40
< 8.70E+O1
< 4.801_
II Mn-54
< 5.1OE+OO =0 3.OOE+OC =
Co-58
< 5.1OE+OO
< 3.40E+OC Fe-59
< 2.20E+01
< 9.60E+OC Co-60
<I 6.80E1+00
< 2.60E+OC Zn-65
<1 1.50E+Ol
< 7.50E+OC0 =
Zr-95
<1 8.80E+00 =
< 5.60E+OCI Ru-103
<l 5.90E+00O
< 3.30E+OC Ru-106
< 4.40E+01
< 2.50E+OI Cs-134
< 6.60E+00
< 3.20E+O(
Cs-137 4.90E+WO 3.20E+OO Ba-140 1.20E+01
< 7.30E+O0 0 La-140
< 1.40E+01
< 8.40E+O0 Ce-141 8.11OE+OO =
< 4.60E+O00=
Ce-144
<I 3.20E+01
<1 1.701_+0_
<l I.IOE+03 =
< 1.30E+03l C-48
Fermi2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 SEDIMENT ANALYSIS S-I (Indicator)
(pCi/kg dry) lINuclide-.
4-M¶.AY I-25-OCT -
Sr-89
< 2.30E+02
<[ 2.40E+02 I
< 1.30E+02
<1 1.90E+02 Be-7 3.30E+02
< 2.00E+02 =
K-40 1.25E1+04 +1-3.30E+02 1.06E+04 +J-2.70E+02 Mn-54
< 2.70E+01
< 2.10E+01 Co-58
< 3.30E+01
< 2.40E+01 Fe-59 9.10E+01
=
6.20E+01
=
=
Co-60 2.40E+01
=
< 2.20E+O1
=
Zn-65 1.40E+02
< 8.80E+0I Zr-95
< 8.20E+01
< 4.20E+03 _-
Ru-103
< 5.30E+01 _
< 2.60E+O I Ru-106 2.50E+02
=
1.80E+02 =
Cs-134 8.90E+OI
=
< 7.50E+01
=
Cs-137 2.30E+01 _<
2.OOE+01 Ba-140
< 7.70E+02 1_ 2.90E+02 La-140
<j 4.30E+02
<_ 1.30E+02 Ce-141
< 8.80E+01
< 4.70E+OI J
Ce-144 1.60E+02
< 1.20E+02 I
S-2 (Indicator)
(pCi/kg dry)
Nuclide j l :
-MAY -: :5--OCT Sr-89
< 2.90E+02 I < 2.60E+02_
< 2.50E+02 1.1OE+02 Be-7
< 3.40E+02
< 2.40E+02 K-40 8.98E+03 +1-3.1 OE+02
=
9.01E+03 +1-2.80E+02 Mn-54
< 3.OOE+0l __
< 2.40E+01 Co-58
< 6.40E+01
< 2.50E+01 Fe-S9
< 1.IOE+02
< 7.20E+01 Co-60
< 2.70E+0I
< 2.50E+01 Zn-65
< 1.40E+02 1.1 OE+02 Zr-95 1.OOE+03
< 8.60E+OI Ru-103
< 5.60E+01
< 2.40E+0 I Ru-106
< 2.70E+02 _<
1.50E+02 Cs-134
< 2.80E+01
=
1.70E+01 Cs-137
< 3.1OE+0 j
=
=
5.17E+01 +1-8.90E+00 Ba-140 9.50E+02 _<
3.OOE+02 La-140 4.OOE+02 _
1.50E+02 Ce-141 1.OOE+02
< 4.90E+O I Ce-144 2.OOE+02 =
< 1.1OE+02 I
C-49
Fermi2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 SEDIMENT ANALYSIS S-3 (Indicator)
(pCi/kg dry)
-Nuclide j
-MAY 25-OCT Sr-89 I<
2.70E+02 I_<
2.40E+021 Sr-90
< 2.70E+02
< 2.20E+02 Be-7
<l 1.80E+02 =
< 6.90E+02 K-40 7.42E+03 +/- 2.1 OE+02 1.39E+04 +/- 3.90E+02 Mn-54
< 1.50E+01
< 2.60E+O1 _
Co58
< 2.OOE+01
< 3.60E+O1 Fe-59
< 6.40E+0I1
< 9.40E+01 Co-60
< I.50
_E+O1
< 2.80E+O
=
Zn-65
< 7.OOE+01 =
1.40E+02 =
Zr-95
< 4.40E+01
< 5.80E+02 Ru-103
< 2.50E+01 =
< 3.70E+01 Ru-1 06 1.20E+02
< 2.30E+02 Cs-134
< 5.40E+01 =
< 5.30E+OI =
< 1.20E+01 _
7.OOE+01 +/- 1.20E+O1 Ba-140
< 3.80E+02
< 3.80E+02 La-140 2.OOE+02
< 2.00E+02 Ce-141 =
<l 4.90E+01 =
=
< _30E+OIl_
Ce-144
<1 8.90E+O1 I
< 1.6E+2 I
S-4 (Indicator)
(pCi/kg dry)
Nuclide MAY
-K`
10-NOV
._-___l Sr-89
< 2.20E+02
< 2.70E+02 I
< 2.80E+02
< 1.60E+02 Be-7
< 2.60E+02
< 1.30E+02 K-40 9.=1E+03 +/- 2.80E+02 9.49E+03 +1 2.OOEE+02 Mn-54
< 2.50E+01
=
< 1.40E+01
_=
Co-58
< 3.30E+01
< 1.50E+O1 Fe-59
< 7.40E+01
< 3.40E+01 Co-60
< 2.70E+01
< 1.40E+O1 Zn-65 1.20E+02
< 7.IOE+01 ___
Zr-95
< 7.40E+01
< < 3.30E+03
=
Ru-103
< 3.60E+01 1.30E+01 Ru-106
< 2.10E+02 1.1OE+02 Cs-134
< 9.00E+01 5.20E+O1 Cs-137
< 2.50E+01 =
< 1.40E+OI1 Ba-140
< 3.40E+02
< 8.10E+O1 La-140
< 1.70E+02
< 4.10E+0I Ce-141
< 6.40E+-01 I
< 2.60E+OI Ce-144
< 1.80E+021
<1 9.60E+01 C-SO
Fermi 2-2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 SEDIMENT ANALYSIS S-5 (Control)
(pCi/kg dry)
Nuclide lJ-i;, - ;MAY
_1
[j l
]9-OCT Sr-89
< 3.OOE+02 I
< 2.40E+02 I
Sr-90 1.80E+02 1.90E+02 _
Be-7
< 3.00E+02 5.90E+02 +/- 1.I OE+02 K-40 9.855E+03 +/- 2.50E+02 1.05E+04 +/- 3.00E+02 Mn-54
< 1.90E+01
< 2.1OE+0I Co-58
< 2.90E+01 3.00E+O1
=
Fe-59
<. 7.30E+01
< 9.10E+01 Co-60
< 1.90E1+01
< 2.20E+O1 Zn-65
< I.OOE+02 1.IOE+02 Zr-95
< 9.30E+01 8.70E+01 Ru-103
< 3.30E+01
=
< 3.60E+01
=
Ru-106
< 1.70E+02
< 2.10E+02 Cs-134
< 7.80E+01
< 8.90E+OI1 Cs-137 5.05E1+01 +/- 8.20E+00 7.90E+O1 +/- 1.IOE+OI Ba-140
< 4.801+02 =
< 4.10E+02
_ =
La-140
< 3.20E+02 =
< 2.50E+02 =
Ce-141
< 7.20E+01
< 7.20E+01 Ce-144 1.40E+02 _
< 1.80E+02 I
C-SI
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 FISH ANALYSIS F-1 (Control)
(pCi/kg wet) lNuclideS.l '- :i 4-MAY 'RockBass-'- -[ -'--MAY-Yellow'Pcrch'.
' OCT Bass-Sr-89
< 2.50E+02
< 2.60E+02 I
< 2.60E+02 I
< 2.40E+02
< 2.50E+02
< 2.50E+02 Be-7
< 6.50E+02
< 5.OOE+02
< 5.20E+02 K-40 2.86E+03 +/- 3.OOE+02 2.65E+03 _
2.40E+02 2.92E+03 +1-2.80E+02 Mn-54
< 5.50E+OI
< 4.1OE+01
=
4.OOE+0 I =
Co-58
< 7.1OE+O1
< 5.80E+O1
< 5.50E+O1 Fe-59
< 2.40E+02
< 1.80E+02
< 2.20E+02 Co-60
< 5.20E+01
< 4.1OE+01
< 4.803E+O1 Zn-65 1.40E+02
< < 1.40E+02 =
< 1.80E+02 Zr-95
- 1. IOE+02
< 8.90E+OI
< 1.I1OE+02 Ru-103
< 8.90E1+01_
< 7.10E+01
< 7.10E+OI Ru-106
< 5.OOE+02
< 3.70E+02
< 2.80E+02 Cs-134
< 5.20E+01
< 3.80E+01
< 3.70E+O1 Cs-137
< 5.1OE+O1I
< 3.90E+01
< 3.50E+O=1 Ba-140
< 6.20E+02
< 4.80E+02 =
< 6.40E+02
=
La-140
< 7.20E+02
< 5.SOE+02
< 7.30E+02 Ce-141
< 1.60E+02
< 1.20E+02
< 1.1 OE+02 Ce-144 2.30E+02
< 1.90E+02 II
< 1.50E+02 _
Nuclide
`;-,'
18-OCT Sucker-18-OCT Walleye5-Sr-89
< 2.60E+02
< '2.50E+021 Sr-90 1.60E+02 __.
1.90E+02 Be-7 8.1 OE+02
< 5.70E+02 K-40
_ j 2.58E+03 +/- 3.00E+02 2.83E+03 +/- 2.90E+02 Mn-54
< 5.60E+01
< 4.70E+01
_=
Co-58 7.50E+01
< 6.40E+01 Fe-59 2.60E+02
< 2.50E+02 Co-60 4.OOE1+01
< 4.60E+01 Zn-65
< 2.OOE+02 _
< 1.90E+02 =
Zr-95 1.30E+02
< 9.40E+OI
=
Ru-103 1.20E+02
< 8.10E+01 Ru-106 4.80E+02
< 3.40E+021 Cs-134 5.30E+01
< 3.90E+01 Cs-137 5.20E+01 4.30E+0I =__
Ba-140
_< 8.10E+02
< 7.00E+02 =
La-140
< 9.30E+02
< 8.00E+02 Ce-141 1.80E+02 =
1.40E+02 =
Ce-144 2.30E+02 _
< 2.00E+02 =
C-52
Fermi2-2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 FISH ANALYSIS F-2 (Indicator)
(pCi/kg wet)
NuclideI l',',
- -; 13'MAY.Drum-';
.'13-MAY:Qullback
. 3-.:'13-MAY
'SilverBass.'-
l Sr-89 I < 2.30E+02 I <
2.60E1+02 I
< 2.10E+02 I
< 2.1OE+02 2.40E+02 1.90E+02 I
Be-7
< 2.70E+02
< 4.50E+02
=
< 5.50E+02 ___
K-40 2.53E+03 +/- 2.1 OE+02
=
2.83E+03 +/- 2.80E+02 2.37E+03 +/- 4.OOE+02 Mn-54
< 2.70E+01 4.1OE+O1
< 4.40E+O1 Co-58
< 2.80E+01
< 5.70E+01
< 6.30E+O1 Fe-59
< 1.1 OE+02
< 2.20E+02
< 2.1 OE+02 Co-60
< 2.50E+01
< 5.60E+01
< 6.40E+OI=
Zn-65
< 7.40E+0I 1.1 OE+02
< 1. IOE+02 Zr-95
< 4.90E+01
< 9.80E+01
< 1.20E+02 Ru-103
< 4.30E+01
< 6.70E+01
< 9.1OE+OI Ru-106
< 2.30E+02
< 3.50E+02
< 4.40E+02 Cs-134
< 3.40E+01
< 4.90E+OI
< 5.50E+O I =
< 2.1OE+O1
< 4.70E+01
< 5.80E+O1 Ba-140
< 2.20E+02
< 3.80E+02
< 5.30E+02 La-140
< 2.50E+02
< 4.30E+02
< 6.10E+02 Ce-141
< 5.60E+01
=
< 8.90E+O1
=
< 1.OOE+02 =
Ce-144
< 9.20E+01 1.80E+02
< 2.80E+02 Nuclide-
{7'l'~-:-.13-MAY Sucker','.'
'13-MAY-Wa--
,l MAY White Perch l
Sr-89 I <
2.20E+021 I__ <
2.40E4-02 I
<1 2.10E+02 I
Sr-90 2.OOE+02
< 2.20E+02 I
1.90E+02 Be-7
< 5.OOE+02
=
< 5.OOE+02
=
< 5.90E+02 =
K-40 2.86E+03 +/- 3.20E+02 2.72E+03 +/- 4.OOE+02 3.76E+03 +/- 3.30E+02 Mn-54
< 4.80E+01
< 4.60E+O1
< 5.lOE+OI _I Co-58
< 4.90E+01
< 7.20E+01
< 6.OOE+O1 Fe-59
< 1.70E+02
=
1.60E+02
< 2.OOE+02 Co-60
< 3.50E+O1
< 6.90E+01
< 5.30E+0I Zn-65
- 1. IOE+02 1.40E+02 1.40E+02 Zr-95
< 8.20E+01 1.30E+02 1.20E+02 Ru-103
< 6.90E+01
=
< 7.30E+01
< 8.60E+O1
=
Ru-106
< 3.90E+02
< 3.50E+02
< 4.50E+02 =____
Cs-134
< 4.30E+01
=<
4.OOE+01
< 5.90E+OI
=
< 3.80E+01 9
< 4.60E+01
< 4.70E+O I Ba-140
< 3.OOE+02
< 5.70E+02
< 4.OOE+02 La-140
< 3.50E+02
< < 6.60E+02 =
< 4.60E+02 =
Ce-141
< I1.1OE+02
< 9.40E+O I I I
1.40OE+02 Ce-144
< 2.30E+02 I=I
< 1.60E+02 I
< 2.40E+02 =
- C-53
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMIR 2 FISH ANALYSIS F-2 (Indicator)
(pCi/kg wet)
Nuclide'-
-I 3-MAY'Yellow.Perch'
- 1 T'25-OCTBass 25-OCT Catfish Sr-89
< I.90E+02l I < 2.40E+02 I
<1 2.40E+02 I
Sr-90 1.70E+02 l
2.OOE+02
< 2.50E+02 Be-7
< 5.30E+02
< 6.90E+02 =
< 6.80E+02 =
K-40 2.37E+03 +/- 3.50E+02 3.14E+03 +/- 3.OOE+02 2.24E+03 +/ 3.20E+02 Mn-54
< 5.30E+01
< 4.50E+O1
< 5.50E+O I Co-58
< 5.90E+01
< 6.20E+01
< 7.30E+O I Fe-59
< 2.40E+02
_< 2.60E+02
< 2.40E+02 =__
< 6.OOE+O1
< 5.OOE+O1
< 5.70E+O
=
Zn-65
< 1.60E+02
< 1.30E+02
< 2.30E+02 Zr-95 1.1 OE+02 =
< 1.20E+02 1.40E+02 =
Ru-103
< 7.90E+01
< 9.40E+O1 1.1OE+02 Ru-106
< 4.80E+02 =
< 4.40E+02
< 5.30E+02 =
Cs-134
< 3.90E+01
< 4.90E+01
< 5.70E+O1 Cs-137
< 5.OOE+O1
< 4.50E+01
< 4.70E+O1 Ba-140
< 4.20E+02
< 6.20E+02
< 8.OOE+02 La-140
< 4.80E+02
< 7.1OE+02 =
< 9.20E+02 Ce-141 1.20E+0,=2
< 1.40E+02 =
< I.50E+02 =
Ce-144
< 2.40E+02
< 2.30E+02
_I___
< 2.60E+02
'Nuclide z
'25-OCT Perch I
l'25-OCT Wallye.-
Sr-89 I <
1.70E+021
<1 2.50E+02 I
1 Sr-90 1.60E+02
< 2.50E+02 =
Be-7
< 5.50E+02
< 4.50E+02 K-40 2.79E+03 +/- 3.30E+02 2.98E+03 +1 3.OOE+02 Mn-54
< 5.40E+01 3.70E+O1
=
Co-58
< 5.50E+01 _
4.OOE+O1 _
Fe-59
< 2.50E+02
< 2.10E+02 =
< 4.00E+01 5.1OE+O1
=
Zn-65 1.1 OE+02
< 8.70E+O1 Zr-95
< 1.IOE+02
< 9.50E+O1 Ru-103
< 8.80E+01
< 6.70E+O1 Ru-106 3.OOE+02 3.10E+02 Cs-134
< 4.20E+01
< 4.10E+OI Cs-137
< 4.80E+01
< 3.80E-+OI Ba-140
< 6.OOE+02 5.30E+02 La-140
< 6.80E+02 6.1OE+02 Ce-141
< 1.20E+02 =
9.60E+OI Ce-144
< 2.OOE+02
<1 I.50E+02 C-54
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 FISH ANALYSIS F-3 (Control)
(pCi/kg wet)
Nuclide
, MAY Drum' '
12MAY Sucker 12-MAY Walleye'-.-,
Sr-89
< 2.30E+02
=
< 2.40E+02 I
< 2.1OE+02 Sr-90 I<
2.OOE+02 2.1OE+02 1.90E+02 Be-7
< 6.70E+02
< 6.OOE+02
< 5.60E+02 K-40 3.69E+03 +/- 3.20E+02 3.44E+03 +/ 3.OOE+02 2.46E+03 +/ 3.40E+02 Mn-54
< 5.80E+01
< 4.40E+01
< 4.00E+O1 Co-58
< 7.40E+01
=
5.60E+01
< 5.80E+O1
=
Fe-59
< 2.30E+02
< 2.40E+02
< 2.20E1+02 Co-60
< 5.50E+01
-< 4.70E+01
< 5.70E+OI Zn-65
< 1.60E+02 1.60E+02 1.30E+02 Zr-95
<_ I.lOE+02
=
< 1.OOE+02 1.OE I.I0+02 Ru-103
< 8.70E+01
=
8.20E+01
< 7.80E+0
=
Ru-106
< 5.60E+02
< 4.80E+02
<1 3.50E+02 Cs-134
< 5.50E+01
=
< 5.OOE+01
< 4.30E+Ol I=
< 4.80E+01
< 4.30E+01
< 4.30E+O1 =
Ba-140
< 4.50E+02 1
< 4.40E+02
< 4.60E+02 =
La-140
< 5.10E+02 5.OOE+02
< 5.30E+02 Ce-141
< 1.40E+02 1.20E+02
< 1.OOE+02 Ce-144
< 2.50E+021
< 2.40E+02
< 2.10E+02 Nuclide;l 4:- ;, MAY W-ite Bass --12-MAY.YellowPerch l
20-OCT Catfish' Sr-89
< 2.20E+02 I < 2.50E+02 I
< 2.80E+02 I
< 2.OOE+02
< 2.30E+02
< 2.20E+02 Be-7
< 6.40E+02
< 4.40E+02
< 6.80E+02 K-40 2.99E+03 +/- 4.40E+02 2.73E+03 +/- 2.40E+02 2.74E+03 +/- 2.70E+02 Mn-54
< 4.90E+01 3.80E+01
< 4.70E+OI
=
Co-58
< 5.30E+01
< 5.OOE+01
< 7.50E+OI1 Fe-59
< 2.40E+02 1.60E+02
< 2.1OE+02 Co-60
< 5.70E+01
< 4.40E+01
< 4.IOE+0 I Zn-65
< 1.60E+02
< 1.20E+02
< 2.OOE+02 Zr-95
< 1.40E+02
< 8.50E+01
< 1.60E+02
=
Ru-103
< 7.70E+01 6.40E+O1 1.1OE+02 Ru-106
< 4.60E+02 I < 3.50E+02
< 4.50E+02 I
Cs-134
< 6.40E+01
=
< 3.90E+01
< 4.80E+OI =
< 4.10E+01
< 3.70E+01
=_=___=< 4.20E1i3 =__
Ba-140
< 4.70E+02
< 3.20E+02
=
< 7.40E+02-La-140
< 5.40E+02
< 3.70E+02 8.50E+02 =
Ce-141 1.30E+02 8.30E1+01 1.50E+02.
Ce-144
< 2.OOE+021
< 1.60E+02 I____
2.IO0E+02 _I C-55
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report FERMI 2 FISH ANALYSIS F.3 (Control)
(pCi/kg wet)
Nuclide-20-OCT Drum
'1n Sr-89 I < 2.50E+021 Sr-90
< 1.90E+02 Be-7
< 7.00E+02 K-40 1.93E+03 +1-3.OOE+02 Mn-54
< 5.60E+01 Co-58
< 8.10E+01 Fe-59
< 2.50E+02 Co-60
<.6.10E+01 Zn-65 1.30E1+02 Zr-95 1.40E+02 Ru-1 03 1.20E+02 =
Ru-106
< 5.40E1+02 Cs-134
< 5.80E+01 Cs-137
< 5.10E+01 Ba-140
< 7.60E+02 =
La-140
< 8.70E+02 =
Ce-141 1.90E+021 Ce-144
< 2.70E+02 C-56
Appendix D Environmental Program Execution
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Environmental Program Execution On occasions, samples cannot be collected. This can be due to a variety of events, such as equipment malfunction, loss of electrical power, severe weather conditions, or vandalism. In 2004, missed samples were a result of missing three field TLDs and loss of electrical power or malfunction of air sampling equipment. The following sections list all missed samples, changes and corrective actions taken during 2004. These missed samples did not have a significant impact on the execution of the REMP.
Direct Radiation Monitoring All TLDs are placed in the field in inconspicuous locations to minimize the loss of TLDs due to vandalism. During 2004, two hundred sixty-eight (268) TLDs were placed in the field for the REMP program and all but three TLDs were collected and processed.
T-l Iwas found missing during the first quarter collection.
- T-21 was found missing during the second quarter collection.
- T-30 was found missing during the fourth quarter collection.
All TLDs were replaced with the next quarter's TLD.
Atmospheric Monitoring During 2004, two hundred sixty (260) air samples were placed in the field, all but five particulate filters and charcoal filters were included in this report.
- API-i filters collected on 8/31/2004 were counted but subsequently discarded due to possible cross-contamination at the laboratory. See Appendix H for investigation results. For this reason, the third quarter composite sample for this location is considered to be less than representative.
- API-2 filters collected on 11/2/2004 were not counted due to low volume caused by sampler malfunction. Sampling equipment was replaced. For this reason, the fourth quarter composite sample for this location is considered to be less than representative.
- API-4 filters collected on 1/20/2004 were not counted due to low volume caused by loss of power to the equipment. Sampling equipment power was restored. For this reason, the first quarter composite sample for this location is considered to be less than representative.
- API-5 filters collected on 8/24/2004 were not counted due to low volume caused by loss of power to the equipment. The breaker was reset and sampling equipment was restored to operation. For this reason, the third quarter composite sample for this location is considered to be less than representative.
D-1
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report
- API-5 filters collected on 12/14/2004 were not counted due to low volume caused by loss of power to the equipment. The fuse was replaced and the sampling equipment was restored to operation. For this reason, the fourth quarter composite sample for this location is considered to be less than representative.
Terrestrial Monitoring During 2004, all scheduled terrestrial monitoring samples were collected.
Milk Sampling All scheduled milk samples were collected in 2004.
§ For sample M-2 collected on 7/8/2004, strontium analysis could not be perform due to the milk curdled.
Garden Sampling All scheduled garden samples were collected in 2004.
Groundwater Sampling All scheduled groundwater samples were collected in 2004.
Aquatic Monitoring During 2004, twenty-four (24) drinking water and surface water samples were collected, and ten (10) sediment samples were collected. In addition, twenty-three (23) fish samples were collected for the Aquatic Monitoring program. There were no changes to the Aquatic Monitoring program during 2004.
Drinking Water Sampling All scheduled drinking water samples were collected in 2004.
D-2
- - -1. - --------- -.- I... 1 I.-
- --. 1-1-I.-
.. I Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Surface Water Sampling All scheduled surface water samples were collected in 2004.
Sediment Sampling All scheduled sediment samples were collected in 2004.
Fish Sampling All scheduled fish samples were collected in 2004.
D-3
Appendix E Effluent and Radwaste Data
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Regulatory Limits for Radioactive Effluents The Nuclear Regulatory Commission (NRC) limits on liquid and gaseous effluents are incorporated into the Fermi 2 Offsite Dose Calculation Manual. These limits prescribe the maximum doses and dose rates due to radioactive effluents resulting from normal operation of Fermi 2. These limits are described in the following sections.
A. Gaseous Effluents I. Dose rate due to radioactivity released in gaseous effluents to areas at and beyond the site boundary shall be limited to the following:
a) Noble gases Less than or equal to 500 mremlyear to the total body.
Less than or equal to 3000 mrem/year to the skin.
b) lodine-131, iodine-133, tritium, and for all radionuclides in particulate form with half lives greater than 8 days Less than or equal to 1500 mrem/year to any organ.
II. Air dose due to noble gases to areas at and beyond the site boundary shall be limited to the following:
a) Less than or equal to 5 mrad for gamma radiation Less than or equal to 10 mrad for beta radiation
- During any calendar quarter b) Less than or equal to 10 mrad for gamma radiation Less than or equal to 20 mrad for beta radiation
- During any calendar year III. Dose to a member of the public from iodine-131, iodine-133, tritium, and all radionuclides in particulate form with half lives greater than 8 days in gaseous effluents released to areas at and beyond the site boundary shall be limited to the following:
E-1
Fermi 2-2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report a) Less than or equal to 7.5 mrem to any organ
- During any calendar quarter b) Less than or equal to 15 mrem to any organ
- During any calendar year Note: The calculated site boundary dose rates for Fermi 2 are based on identification of individual isotopes and on use of dose factors specific to each identified isotope or a highly conservative dose factor. Average energy values are not used in these calculations, and therefore need not be reported.
B. Liquid Effluents I. The concentration of radioactive material released in liquid effluents to unrestricted areas shall be limited to ten times the concentrations specified in Title 10 of the Code of Federal Regulations (10 CFR) Part 20 (Standards for Protection Against Radiation), Appendix B, Table 2, Column 2 for radionuclides other than dissolved or entrained noble gases, as required by the Fermi 2 Offsite Dose Calculation Manual. For dissolved or entrained noble gases, the concentration shall be limited to 2E-4 (.0002) microcuries/ml total activity. This limit is based on the Xe-135 air submersion dose limit converted to an equivalent concentration in water as discussed in the International Commission on Radiological Protection (ICRP) Publication 2.
II. 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:
a) Less than or equal to 1.5 mrem to the total body Less than or equal to 5 mrem to any organ
-During any calendar quarter b) Less than or equal to 3 mrem to the total body Less than or equal to 10 mrem to any organ
- During any calendar year.
E-2
I Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report Measurements and Approximations of Total Activity in Radioactive Effluents As required by NRC Regulatory Guide 1.21, this section describes the methods used to measure the total radioactivity in effluent releases and to estimate the overall errors associated with these measurements. The effluent monitoring systems are described in Chapter 11.4 of the Fermi 2 Updated Final Safety Analysis Report (UFSAR).
A. Gaseous Effluents
- 1. Fission and Activation Gases Samples are obtained from each of the six plant radiation monitors which continuously monitor the five ventilation exhaust points. The fission and activation gases are quantified by gamma spectroscopy analysis of periodic samples.
The summary values reported are the sums of all fission and activation gases quantified at all monitored release points.
- 11. Radiolodines Samples are obtained from each of the six plant radiation monitors which continuously monitor the five ventilation exhaust points. The radioiodines are entrained on charcoal and then quantified by gamma spectroscopy analysis.
For each sample, the duration of sampling and continuous flow rate through the charcoal are used in determining the concentration of radioiodines. From the flow rate of the ventilation system, a rate of release can be determined.
The summary values reported are the sums of all radioiodines quantified at all continuously monitored release points.
E-3
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report 111. Particulates Samples are obtained from each of the six plant effluent radiation monitors which continuously monitor the five ventilation exhaust points. The particulates are collected on a filter and then quantified by gamma spectroscopy analysis.
For each sample, the duration of sampling and continuous flow rate through the filter are used in determining the concentration of particulates. From the flow rate of the ventilation system, a rate of release can be determined.
Quarterly, the filters from each ventilation release point are composited and then radiochemically separated and analyzed for strontium (Sr)-89/90 using various analytical methods.
The summary values reported are the sums of all particulates quantified at all monitored release points.
IV. Tritium Samples are obtained from each of the six plant effluent radiation monitors which continuously monitor the five ventilation exhaust points. The sample is passed through a bottle containing water and the tritium is "washed" out to the collecting water. Portions of the collecting water are analyzed for tritium using liquid scintillation counting techniques. For each sample, the duration of sample and sample flow rate is used to determine the concentration. From the flow rate of the ventilation system, a release rate can be determined.
The summary values reported are the sums of all tritium quantified at all monitored release points.
E-4
-1
--
T- . -... -,,
1 -- --
Fermi2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report V. Gross Alpha The gaseous particulate filters from the six plant effluent radiation monitors are stored for one week to allow for decay of naturally occurring alpha emitters. These filters are then analyzed for gross alpha radioactivity by gas proportional counting, and any such radioactivity found is assumed to be plant related. The quantity of alpha emitters released can then be determined from sample flow rate, sample duration, and stack flow rate.
The summary values reported are the sums of all alpha emitters quantified at all monitored release points.
B. Liquid Effluents The liquid radwaste processing system and the liquid effluent monitoring system are described in the Fermi 2 UFSAR. Fermi 2 released no radioactive liquid effluents in 2004.
C. Statistical Measurement Uncertainties The statistical uncertainty of the measurements in this section has been calculated and summarized in the following table:
Measurement Type Sample Type One Sigma Uncertainty Fission and Activation Gaseous 30%
Gases Radioiodines Gaseous 17%
Particulates Gaseous 16%
Tritium Gaseous 25%
Gross Alpha Gaseous 16%
Gaseous Releases by Individual Nuclide Values in the following tables which are preceded by the "less than" symbol represent the lower limit of detection (LLD) in units of microcuries per cubic centimeter (.LCi/cc) for individual samples, and indicate that the nuclide in question was not detected in gaseous effluent samples in the indicated quarter of 2004.
For quantities of gross alpha radioactivity and tritium in gaseous effluents, see Tables 3 and 4 on page 13 of this report.
E-5
v w 5 1.
_'... _ _.1 -.
1:
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report A. Particulate Radionuclides (Curies)
-t; Cr-51 2.62E-04
<4.3E-13
<4.3E-13 2.45E-04 Mn-54
<6.IE-14
<6.IE-14 1.19E-05 2.93E-05 Co-58 2.65E-05
<6.3E-14 1.27E-05 2.1 OE-05 Co-60 4.35E-05 5.40E-06 1.811E-05 6.25E-05 Zn-65 2.70E-05
<1.5E-13
<I.5E-13
<1.5E-13 Na-24 2.55E-04
<5.9E-14
<5.9E-14
<5.9E-14 Tc-99m 1.93E-04
<6.4E-13 6.85E-05 3.13E-05 Ba-139 1.45E-01 1.17E- 0 8.19E-02 7.03E-02 La-140 8.08E-05 4.04E-05 1.17E-04 4.30E-05 Ba-140 1.30E-05 1.95E-05 3.9 1E-05 3.89E-05 Y-91m 1.36E-02 1.19E-02 3.72E-03 4.65E-03 Sr-91 6.54E-04 3.66E-04 4.79E-04
<4.2E-12 Rb-89 I.OOE-O1
<3.7E-10 1.07E-01 9.51 E-02 Cs-138 9.59E-02 6.48E-02 9.84E-02 4.68E-02 As-76 4.24E-03 8.34E-03 3.39E-03 3.37E-03 Br-82 8.65E-06 1.82E-05
<2.5E-13 2.22E-05 Sr-89 3.07E-05 1.75E-05 4.25E-05 2.29E-05 Sr-90 2.36E-06
<7.7E-15
<7.7E-15
<7.7E-15 Cs-134
. <4.3E-14
<4.3E-14
<4.3E-14
<4.3E-14 Cs-137
<7.4E-14
<7.4E-14
<7.4E-14
<7.4E-14 Ce-141
<5.8E-14
<5.8E-14
<5.8E-14
<5.8E-14 Ce-143
<4.OE-13
<4.0E-13
<4.0E-13
<4.OE-13 Ce-144
<2.4E-13
<2.4E-13
<2.4E-13
<2.4E-13 Total 3.60E-01 2.03E-01 2.95E-01 2.21E-O1 B. Noble Gases (Curies) 0 0
6 4
<8.9E-08
<8.9E-08
<8.9E-08
<8.9E-08 Xe-135
<2.3E-08
<2.3E-08
<2.3E-08
<2.3E-08 Xe-135m
<2.2E-08
<2.2E-08
<2.2E-08
<2.2E-08 Xe-138
<1.2E-07
<1.2E-07
<1.2E-07
<1.2E-07 Total
<2.5E-07
<2.5E-07
<2.5E-07
<2.5E-07 E-6
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report C. Radioiodines (Curies) 1-131 8.23E-04 1.29E-03 1.06E-03 1.1 8E-03 I-132 7.29E-03 1.61E-02 9.47E-03 3.70E-03 I-133 6.59E-03 1.05E-02 7.64E-03 3.46E-03 1-134 1.29E-02 2.60E-02 4.36E-03
<1.2E-10 I-135 1.08E-02 1.39E-02 7.91 E-03 4.07E-03 Total 3.84E-02 6.78E-02 3.04E-02 1.24E-02 Shipments of Radwaste Fermi 2 complies with the extensive federal regulations which govern radioactive waste shipments. Radioactive solid waste shipments from the Fermi 2 site consist of waste generated during water treatment, radioactive trash, irradiated components, etc. Shipment destinations are either licensed burial sites or intermediate processing facilities. Waste shipped to intermediate processing facilities is shipped directly from these facilities to licensed burial sites after processing. The following tables contain estimates of major nuclide composition, by class of waste, of Fermi 2 solid radwaste received at the Barnwell, SC, burial facility or at the Envirocare, UT, facility in 2004.
- a. Spent resins, sludges, etc. Waste in this category in 2004 consisted of spent resins and sludges, and included Class A, B, and C waste. It was initially shipped in either High Integrity Containers or Polyethylene Liners, within shielded transportation casks, either directly to the Barnwell, SC, burial facility or to an intermediate processor. Waste sent directly to the Barnwell disposal facility was dewatered prior to shipment. Waste sent to the intermediate processor was processed by this processor using a combination of pyrolysis and steam reforming gasification technology, after which it was forwarded for disposal to the Envirocare, UT, facility or to the Barnwell Waste Management Facility.
All quantities were determined by measurement.
E-7
Fermi 2 - 2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report
- 1. Class A Resin:
Radionuclide Total Activity (mCi)
Percent of Total Activity Ag-1 Om 1.04E+01
<0.1 Ba-i 33 4.32E-02
<0.1 C-14 3.15E+03 5.3 Ce-1 44 2.38E-03
<0.1 Cm-243 1.82E-08
<0.1 Cm-244 1.69E-08
<0.1 Co-57 2.76E+00
<0.1 Co-58 4.32E+02 0.7 Co-60 2.65E+04 44.8 Cr-51 6.89E+00
<0.1 Cs-134 9.15E+00
<0.1 Cs-1 37 5.63E+02 1.0 Fe-55 1.85E+04 31.3 Fe-59 4.27E+00
<0.1 H-3 1.46E+02 0.2 Hf-181 1.22E-01
<0.1 1-129 (LLD) 1.83E+00 NA Mn-54 6.30E+03 10.7 Nb-95 2.17E-01
<0.1 Ni-59 7.92E+00
<0.1 Ni-63 1.93E+03 3.3 Pu-241 2.27E-06
<0.1 Sb-125 1:72E-01
<0.1 Sr-89 7.08E-02
<0.1 Sr-90 9.15E+00
<0.1 Tc-99 (LLD) 8;48E+01 NA Zn-65 1.56E+03 2.6 Total Activity 5.92E+04 100.0 E-8
Fermi 2-2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report
- 2. Class B Resin:
Radionuclide Total Activity (mCi)
Percent of Total Activity C-14 2.75E+00 0.1 Co-60 3.01 E+03 80.3 Fe-55 4.36E+02 11.6 H-3 4.03E+00 0.1 1-129 (LLD) 1.39E+0O NA Ni-63 2.97E+02 7.9 Tc-99 (LLD) 4.08E+0o NA Total Activity 3.76E+03 100.0
- 3. Class C Resin:
Radionuclide Total Activity (mCi)
Percent of Total Activity C-14 7.44E+00 0.1 Co-60 8.19E+03 80.2 Fe-55 1.19E+03 11.6 H-3 1.09E+01 0.1 1-129 3.77E+00
<0.1 Ni-63 8.03E+02 7.9 Tc-99 1.1OE+01 0.1 Total Activity 1.02E+04 100.0 E-9
Fermi 2-2004 Annual Radioactive Effluent Release and Radiological Environmental Operating Report
- b. Dry compressible waste, contaminated equipment, etc. Waste in this category in 2004 was shipped in strong tight containers, and was classified as dry active waste (DAW). All waste in this category was Class A waste. The DAW was compacted or incinerated by an intermediate processor. After incineration, some of the residue from this waste was solidified in concrete. All quantities were determined by measurement.
Radionuclide Total Activity (mCi)
Percent of Total Activity Ag-11 Om 6.54E-05
<0.1 Ba-133 1.38E-02
<0.1 C-14 6.31 E+00-1.7 Ce-144 6.11 E-04
<0.1 Cm-243 5.86E-09
<0.1 Cm-244 5.41 E-09
<0.1 Co-57 7.95E-05
<0.1 Co-58 6.77E+00 1.9 Co-60 5.68E+01 15.7 Cr-51 6.89E+01 19.0 Cs-1 34 2.27E-01 0.1 Cs-137 6.72E+00 1.9 Fe-55 1.54E+02 42.5 Fe-59 5.71 E+00 1.6 H-3 2.42E+01 6.7 1-129 1.20E-01
<0.1 Mn-54 1.47E+01 4.1 Ni-59 5.55E-03
<0.1 Ni-63 2.21 E+00 0.6 Pu-241 7.27E-07
<0.1 Sb-1 24 2.90E-01 0.1 Sb-125 5.22E-02
<0.1 Sr-90 1.28E-05
<0.1 Tc-99 8.73E+00 2.4 Zn-65 6.20E+00 1.7 Total Activity 3.62E+02 100.0
- c. Irradiated components, control rods, etc.
No waste in this category was shipped.
- d. Other No waste in this category was shipped to a disposal site.
E-10
Appendix F Interlaboratory Comparison Data Framatome ANP Environmental Laboratory's Quality Assurance Programs
Fermi 2-2004Annual Radioactive Effluent Release and Radiological Environmental Operating Report Interlaboratory Comparison Program for 2004 In an interlaboratory comparison program, participant laboratories receive from a commerce source, environmental samples of known activity concentration for analysis.
After the samples have been analyzed by the laboratory, the manufacturer of the sample reports the known activity concentration of the samples to the laboratory. The laboratory compares its results to the reported concentrations to determine any significant deviations, investigates such deviations if found, and initiates corrective action if necessary. Participation in this program provides assurance that the contract laboratory is capable of meeting accepted criteria for radioactivity analysis.
Included in this Appendix are the Semi-Annual Status Reports covering the Framatome ANP Environmental Laboratory's Quality Assurance Programs for the first and second halves of 2004.
F-I
AREVA August 5, 2004 EL 116/04 TO:
Distribution FROM:
J. M. Raimondi
SUBJECT:
Framatome ANP Environmental Laboratory Analytical Service Semi-Annual Quality Assurance Status Report (January - June 2004)
Attached Is the Semi-Annual Status Report covering the Framatome ANP Environmental Laboratory's (E-LAB) Quality Assurance Programs comprising radiological environmental, Part 50/61, and bioassay analytical services for the first half of 2004.
For the Radiological Environmental Monitoring Program (REMP), 99.1 % of 632 individual QC analyses evaluated during this semi-annual period met E-LAB acceptance criteria for bias, while 99.5% of 424 QC analyses met the Laboratory QC acceptance criteria for precision. To provide a perspective of the overall environmental quality program since its inception in 1977, 96.6%of the 17,199 environmental QC analyses processed in the past 27 years met acceptance criteria for-bias, whereas, 99.4% of 15,263 QC samples evaluated for precision met Laboratory criteria for this performance category. DOE program participation (DOEQAP and MAPEP) resulted in all 19 mean results evaluated as in "Agreement' with the acceptance criteria. DOE data is not included in the above summary values.
The Framatome ANP Environmental Laboratory (ID# 11823) received full certification for six radiological analytes in the Potable water and Non-Potable water categories from the State of New York Department of Health under the National Environmental Laboratory Accreditation Program (NELAP). A total of 9 Proficiency Test results, all of which were rated "Acceptable,"
were received during this period.
During the first half of 2004, 94.5% of the 163 Part 50/61 Individual analyses evaluated for bias and 100% of the 151 analyses evaluated for precision met E-LAB acceptance criteria. During the past sixteen years of processing Part 50/61 samples, 4020 QC analyses have been evaluated for bias along with 3870 samples for precision. Overall perfomnance statistics indicate an acceptance rate of 94.0% for bias and 99.2% for precision.
The State of New York Department of Health performed their Initial certification audit of the E-LAB during this semi-annual period. All of the findings have been successfully addressed and resulted in the issuance of full certification for six radionuclides in each of the Potable water and Non-Potable water programs.
WN-62wP M. Raimondi Manager, Environmental Laboratory CAS/cas ATTACHMENTS
Distribution Page 2 EL 116/04 August 4, 2004 Distribution R.Abrams-FP&L V. Ballestrini - Dominion/Millstone J. Barnette - Texas Utilities/Comanche Peak J. Breeden - Dominion/North Anna S. Bromstrup - FP&L/St. Lucie J. Bundick - Indiana Michigan/D. C. Cook D. Burnett - Entergy/River Bend A. Castagnacci - FENOC/Beaver Valley K. Comisky - CY J. Cruickshank - Ameren UE/ Callaway J. Doroski - Dominion/Millstone M. Doty - FENOC/Perry J. D'Souza - PSEG B. Eakin - Dominion/Millstone R. Edwards - FENOC/Davis-Besse E. Floyd - Texas Utilities Comanche Peak R. Gasper - RG&E/Ginna B. Gorman - Entergy/Fitzpatrick S. Grondahl - Dominion/Millstone W. Hamblin - Entergy/Fitzpatrick N. Hansen - Southern California Edison G. Harper - Framatome ANP P. Harris - Dominion/Surry F. Hickey - PPL Susquehanna B. Hilt - Dominion/Surry A. Hoomick, Jr. - PSEG/Hope Creek J. Hornsby - Entergy/Waterford G. Jones - Rochester Electric/Ginna P. Lashley - FENOC/Perry T. Lashley - Detroit Edison/Fermi II T. Lonnett - FENOC/Beaver Valley.
P. McNulty - Entergy/Pilgrim G. Mendoza - FP&LiTurkey Point E. Mercer-MY D. Montt - Rowe/CY R. Moore - FENOC/Beaver Valley J. Pennington - Entergy Operations, Inc.
D. Perkins - FP&L/Seabrook H. Riley - PPL Susquehanna D. Robinson - FP&L/Seabrook F. Sabadini - Framatome ANP QA M. Sanger-Framatome ANP QA K. Sejkora - Entergy/Pilgrim S. Skibniowski - Entergy/ Vermont Yankee P. Sobottke - Indiana Michigan/D. C. Cook G. Stephenson - Entergy/ANO P. Stokes - Entergy/Grand Gulf R. Tolbert - Entergy/Grand Gulf T. Vandermay - Detroit Edison/Fermi II M. Walden - PG&E/Trojan V. Withee - MY Document Control