ML15125A120
| ML15125A120 | |
| Person / Time | |
|---|---|
| Site: | Perry  |
| Issue date: | 04/30/2015 |
| From: | Harkness E J FirstEnergy Nuclear Operating Co |
| To: | Document Control Desk, Office of Nuclear Reactor Regulation |
| Shared Package | |
| ML15125A117 | List: |
| References | |
| L-15-143 | |
| Download: ML15125A120 (131) | |
Text
Enclosure A L-1 5-143 PNPP 2014 Annual Environmental and Effluent Release Report Perry Nuclear Power Plant Annual Environmental and Effluent Release Report 2014 2014 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT for the Perry Nuclear Power Plant PREPARED BY: CHEMISTRY SECTION PERRY NUCLEAR POWER PLANT FIRSTENERGY NUCLEAR OPERATING COMPANY PERRY, OHIO APRIL, 2015 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Table of Contents EXEC UTIVE SUM M A RY ......................................................................................
1 Radioactive Effluent Releases .....................................................................................
1 Radiological Environmental Monitoring
.......................................................................
2 Land Use Census .......................................................................................................
2 Clam/M ussel Monitoring
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3 Herbicide Use ...........................................................................................................
3 Special Environmental Reports ...................................................................................
3 INTRO DUCTIO N ..................................................................................................
3 Radiation Fundamentals
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3 Radiation and Radioactivity
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4 Units of Measure ..........................................................................................................
5 Lower Lim it of Detection
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- .........................................................
5 Other Sources of Radiation Dose to the U.S. Population
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6 Environmental Radionuclides
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7 RAD IO ACTIVE EFFLUENT RELEASES ...............................................................
8 Introduction
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8 Regulatory Lim its .......................................................................................................
9 Liquid Effluents
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9 Gaseous Effluents
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10 Release Sum mary .....................................................................................................
11 Meteorological Data ..................................................................................................
.19 Dose Assessm ent .....................................................................................................
19 CARBON-14 SUPPLEMENTAL INFORMATION
................................................
23 GROUNDWATER MONITORING PROGRAM ....................................................
23 Corrections to Previous Annual Environmental and Effluent Release Reports ..........
26 Abnormal Releases ...................................................................................................
26 ODCM Non-Com pliances .........................................................................................
26 Offsite Dose Calculation Manual Changes ................................................................
26 Process Control Program Changes .........................................................................
26 RADIOLOGICAL ENVIRONMENTAL MONITORING
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27 Introduction
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27 Sam pling Locations
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27 Sam ple Analysis .......................................................................................................
33 Sam pling Program .....................................................................................................
34 Program Changes ......................................................................................................
34 M issed Sam ples ........................................................................................................
34 Atm ospheric Monitoring
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35 Terrestrial Monitoring
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36 Aquatic Monitoring
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37 Direct Radiation Monitoring
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39 Conclusion
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40 Inter-Laboratory Cross-Check Com parison Program ................................................
41 Land Use Census .....................................................................................................
42 CLAM /M USSEL M O N ITO RING .........................................................................
45 Introduction
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45 Corbicula Program .....................................................................................................
45 Dreissena Program ...................................................................................................
46 Table of Contents Page i ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT HERBICIDE APPLICATIONS
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47 S PEC IA L R EPO RTS .................................................................................................
48 Environm ental Protection Plan .................................................................................
48 Un-Reviewed Environmental Questions
...................................................................
48 Appendices Appendix A: 2014 Inter-Laboratory Cross Check Comparison Program Results Appendix B: 2014 REMP Data Summary Reports Appendix C: 2014 REMP Detailed Data Report Appendix D: Corrections to Previous AEERR Appendix E: Abnormal Releases Appendix F: ODCM Non-Compliances Appendix G: ODCM Changes Appendix H: Changes to the Process Control Program Table of Contents Page ii ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT EXECUTIVE
SUMMARY
The Annual Environmental and Effluent Release Report (AEERR) details the results of environmental and effluent monitoring programs conducted at the Perry Nuclear Power Plant (PNPP) from January 01 through December 31, 2014. This report meets all of the requirements in PNPP Technical Specifications, the Offsite Dose Calculation Manual (ODCM), the Environmental Protection Plan (EPP), and Regulatory Guide 1.21. It incorporates the requirements of the Annual Radioactive Effluent Release Report (ARERR), the Annual Radiological Environmental Operating Report (AREOR) and the Annual Environmental Operating Report (AEOR). Report topics include radioactive effluent releases, radiological environmental monitoring, land use census, clam/mussel monitoring, herbicide use, and special reports. The results of the environmental and effluent programs for 2014 indicate that the operations of the PNPP did not result in any significant environmental impact.RADIOACTIVE EFFLUENT RELEASES During the normal operation of a nuclear power plant, small quantities of radioactivity are released to the environment in liquid and gaseous effluents.
Radioactive material is also shipped offsite as solid waste. PNPP maintains a comprehensive program to control and monitor the release of radioactive materials from the site in accordance with Nuclear Regulatory Commission (NRC) release regulations.
The dose to the general public from the plant's liquid and gaseous effluents was below regulatory limits. The calculated maximum individual whole body dose potentially received by an individual resulting from PNPP liquid effluents was 9.00E-04 mrem (0.03% of the limit). The calculated maximum individual whole body dose potentially received by an individual resulting from PNPP gaseous effluents (excluding C-14) was 5.18E-04 mrem (0.01% of the limit).Radioactivity released to the environment in the form of gaseous Carbon-14 (C-14) was estimated based on plant type and power production.
The calculation is based on an industry initiative supported by the Nuclear Energy Institute (NEI), the Electric Power Research Institute (EPRI) and the NRC. The calculated hypothetical maximum individual whole body dose potentially received by an individual resulting from PNPP gaseous effluents including C-14 is 2.47E-01 mrem (4.9% of the limit). Refer to page 23 for additional Carbon-14 information.
The summation of the hypothetical maximum individual dose from effluents in 2014 is less than 1% of the total dose an individual living in the PNPP area receives from all sources of manmade and background radiation.
Shipments of solid waste consisted of waste generated during water treatment, radioactive material generated during normal daily operations and maintenance, and irradiated components.
PNPP complied with regulations governing radioactive shipments of solid radioactive waste.An additional section covers the groundwater monitoring program. It includes a brief history of groundwater tritium issues at the PNPP, and results from current sampling and monitoring activities.
Page 1 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT RADIOLOGICAL ENVIRONMENTAL MONITORING The Radiological Environmental Monitoring Program (REMP) was established in 1981 to monitor the radiological conditions in the environment around PNPP. The REMP is conducted in accordance with PNPP Technical Specifications and the ODCM. This program includes the collection and analysis of environmental samples and evaluation of results.The REMP was established at PNPP six (6) years before the plant became operational.
This pre-operational program was designed to provide data on background radiation and radioactivity normally present in the area. PNPP has continued to monitor the environment during plant operation by collecting and analyzing samples of air, milk, fish, vegetation, water and sediment, as well as by measuring radiation directly.
The results of the REMP program indicate adequate control of radioactivity released from PNPP plant effluents.
These results also demonstrate that PNPP complies with federal regulations.
Air samples were collected to monitor the radioactivity in the atmosphere; the results were similar to those observed for the pre-operational and operational programs from prior years.Terrestrial monitoring included the analysis of milk and vegetation; the results indicated concentrations of radioactivity similar to that found in previous years. Analyses of vegetation samples detected only natural radioactivity similar to those observed in previous years, and indicated no build-up of radioactivity attributable to the operation of PNPP.Aquatic monitoring included the collection and analyses of water, fish, and shoreline sediments.
The analytical results for water and fish samples showed normal background radionuclide concentrations.
The results of sediment sample analyses indicated that the annual average cesium radioactivity was similar to previous years for the control location.Cesium-137 activity was detected in two (2) of the seven (7) samples collected.
The average cesium-1 37 radioactivity for all locations was 68.5 pCi/kg and is lower than the highest identified value of 864 pCi/kg established in 1981 which was due to atmospheric nuclear weapons testing.Direct radiation measurements showed no discernible change from previous years. The indicator locations averaged 64.0 mrem/year and control locations averaged 64.7 mrem/year.
In 2014, radiation dose in the area of PNPP was similar to the radiation dose measured at locations greater than ten (10) miles away from the Plant.Based on these results, during 2014, the operation of the PNPP resulted in no significant increase in the radionuclide concentrations observed in the environment.
LAND USE CENSUS In order to estimate radiation dose attributable to the operation of PNPP, the potential pathways through which public exposure can occur must be known. To identify these exposure pathways, an Annual Land Use Census is performed as part of the REMP.During the census, PNPP personnel travel public roads within a five (5) mile radius of the plant to locate key radiological exposure pathways.
These key pathways include the nearest resident, garden, and milk animal in each of the ten meteorological land sectors that surround the plant. The information obtained from the census is entered into a computer program, which is used to assess the hypothetical dose to members of the public.The predominant land use within the census area continues to. be rural and/or agricultural.
Page 2 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT CLAM/MUSSEL MONITORING Clam and mussel shells can clog plant piping and components that use water from Lake Erie. For this reason, sampling for clams and mussels has been conducted in Lake Erie near PNPP since 1971. The monitoring is specifically for Corbicula (Asiatic clams) since their introduction into the Great Lakes in 1981, and for Dreissena (zebra mussels) since their discovery in Lake Erie in 1989. Since no Corbicula have ever been found at PNPP, routine Corbicula monitoring will provide early detection capability if this pest species arrives at PNPP. The Dreissena program includes both monitoring and control and is directed at minimizing the mussel's impact on plant operation.
As in past years, this program has successfully prevented Dreissena from causing any significant operational problems at PNPP.HERBICIDE USE The use of herbicides on the PNPP site is monitored to ensure compliance with Ohio Environmental Protection Agency (OEPA) requirements and to protect the site's natural areas. Based on the results of on-site herbicide applications and weekly general site inspections, herbicide use has not had a negative impact on the environment around the plant.SPECIAL ENVIRONMENTAL REPORTS Significant environmental events (for example, spills, releases), noncompliance with environmental regulations
[e.g., OEPA discharge limits], and changes in plant design or operation that affect the environment are reported to regulatory agencies as they occur.There were no reports submitted in 2014.INTRODUCTION Nuclear energy provides an alternative energy source, which is readily available and has very limited impact upon the environment.
To more fully understand nuclear energy as a source of generating electricity, one must understand basic radiation concepts and its occurrence in nature.RADIATION FUNDAMENTALS Atoms are the basic building blocks of all matter. Simply described, atoms are made up of positively and negatively charged particles, and particles which are neutral. These particles are called protons, electrons, and neutrons, respectively.
The relatively large protons and neutrons are packed together in the center of the atom called the nucleus. Orbiting around the nucleus are one or more smaller electrons.
In an electrically neutral atom, the positively charged protons in the nucleus balance the negatively charged electrons.
Due to their dissimilar charges, the protons and electrons have a strong attraction for each other, which helps hold the atom together.
Other attractive forces between the protons and neutrons keep the densely packed protons from repelling each other, and preventing the nucleus from breaking apart.Page 3 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Atoms with the same number of protons in their nuclei make up an element. The number of neutrons in the nuclei of an element may vary. Atoms with the same number of protons but different numbers of neutrons are called isotopes.
All isotopes of the same element have the same chemical properties and many are stable or non-radioactive.
An unstable or radioactive isotope of an element is called a radionuclide.
Radionuclides contain an excess amount of energy in the nucleus, which is usually due to an excess number of neutrons.Radioactive atoms attempt to reach a stable, non-radioactive state through a process known as radioactive decay. Radioactive decay is the release of energy from an atom's nucleus through the emission of radiation.
Radionuclides vary greatly in the rate in which their atoms release radiation.
The length of time an atom remains radioactive is defined in terms of its half-life.
Half-life is defined as the time required for a radioactive substance to lose half its activity through the process of radioactive decay. Half-lives vary from millionths of a second to millions of years.RADIATION AND RADIOACTIVITY Radioactive decay is a process in which the nucleus of an unstable atom becomes more stable by spontaneously emitting energy. Radiation refers to the energy that is released when radioactive decay occurs within the nucleus. This section includes a discussion on the three (3) primary forms of radiation produced by radioactive decay.Alpha Particles Alpha particles consist of two protons and two neutrons and have a positive charge.Because of their charge and large size, alpha particles do not travel very far when released (less than 4 inches in air). They are unable to penetrate any solid material, such as paper or skin, to any significant depth. However, if alpha particles are released inside the body, they can damage the soft internal tissues because they deposit all their energy in a small area.Beta Particles Beta particles have the same characteristics as electrons but originate from the nucleus.They are much smaller than alpha particles and travel at nearly the speed of light. Thus they can travel for longer distances than alpha particles.
External beta radiation primarily affects the skin. Because of their electrical charge, paper, plastic or thin metals can stop beta particles.
Gamma Rays Gamma rays are bundles of electromagnetic energy, called photons, which behave as though they were particles.
They are similar to visible light, but of a much higher energy.Gamma rays can travel long distances in air and are often released during radioactive decay, along with alpha and beta particles.
Potassium-40 is an example of a naturally occurring radionuclide found in all humans that decays by emitting a gamma ray.Page 4 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Interaction with Matter When radiation interacts with other materials, it affects the atoms of those materials principally by knocking the negatively charged electrons out of orbit. This causes an atom to lose its electrical neutrality and become positively charged. An atom that is charged, either positively or negatively, is called an ion and the radiation is called ionizing radiation.
UNITS OF MEASURE Some of the units of measure used in this report require explanation.
Activity Activity is the number of atoms in a material that decay per unit of time. Each time an atom decays, radiation is emitted. The curie (Ci) is the unit used to describe the activity of a material and indicates the rate at which the atoms are decaying.
One curie of activity indicates the decay of 37 billion atoms per second. Smaller units of the curie are often used in this report. Two common units are the microcurie (pCi), one millionth of a curie, and the picocurie (pCi), one trillionth of a curie. The mass, or weight, of radioactive material, which would result in one (1) curie of activity, depends on the disintegration rate.For example, one gram of radium-226 is equivalent to one (1) curie of activity.
It would require about 1.5 million grams of natural uranium, however, to equal one (1) curie.Dose Biological damage due to alpha, beta, and gamma radiation may result from the ionization caused by these types of radiation.
Some types of radiation, especially alpha particles, which causes dense local ionization, can result in much more biological damage for the same energy imparted than does gamma or beta radiation.
Therefore, a quality factor must be applied to account for the different ionizing capabilities of various types of ionizing radiation.
When the quality factor is multiplied by the absorbed dose (as measured in rads), the result is the dose equivalent, which is an estimate of the possible biological damage resulting from exposure to any type of ionizing radiation.
The dose equivalent is measured in terms of the Roentgen Equivalent Man (rem). When discussing environmental radiation effects, the rem is a large unit. Therefore, a smaller unit, the millirem (mrem) is often used.One mrem is equivalent to 1/1000 of a rem.LOWER LIMIT OF DETECTION Sample results are often reported as below the Lower Limit of Detection (LLD). The LLD for an analysis is the smallest amount of radioactive material that will show a positive result for which there can be a 95% confidence that radioactivity is present. This statistical parameter is used as a measure of the sensitivity of a sample analysis.
When a measurement is reported as less than the LLD (<LLD), it means that no radioactivity was detected.
Had radioactivity been present at (or above) the stated LLD value, it statistically would have been detected.
The NRC has established the required LLD values for environmental and effluent sample analyses.Page 5 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT OTHER SOURCES OF RADIATION DOSE TO THE U.S. POPULATION This section discusses the doses that the average American typically receives each year from naturally occurring background radiation and all other sources of radiation.
With the information presented in this section, the reader can compare the doses received from a Nuclear Power Plant (NPP) effluents with the doses received from natural, medical, and other sources of radiation.
This comparison provides some context to the concept of radiation dose effects.In March 2009, the National Council on Radiation Protection and Measurements (NCRP)published Report No. 160 as an update to the 1987 NCRP Report No. 93, Ionizing Radiation Exposure of the Population of the United States (Refs. 30, 31). Report No. 160 describes the doses to the U.S. population from all sources of ionizing radiation for 2006, the most recent data available at the time the NCRP report was written. The NCRP report also includes information on the variability of those doses from one individual to another.The NCRP estimated that the average person in the United States receives about 620 mrem of radiation dose each year. NCRP Report No. 160 describes each of the sources of radiation that contribute to this dose, including:
0 Naturally occurring sources (natural background) such as cosmic radiation from space, terrestrial radiation from radioactive materials in the earth, and naturally occurring radioactive materials in the food people eat and in the air people breathe;0 Medical sources from diagnosis and treatment of health disorders using radioactive pharmaceuticals and radiation-producing equipment; 0 Consumer products (such as household smoke detectors);
0 Industrial processes, security devices, educational tools, and research activities; and Exposures of workers that result from their occupations.
Page 6 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Figure 1 Sources of Radiation Exposure to the U.S. Population
$NaCO tbackgroemd) 5%Internal (background) 5% Terredtrial S(back~ground)
C&Mpi4ed tornaraphvy (medical)24%Indusbieil A0I4&10g056 OM n 10 bA ft M nudwwpo~eg~Rflb!"<0.1%-WC0*jg MODn. to waeifrtv7 AucWOwp HOme Me&ae Conoume<0 1% 2% Conventi*na radiograph)'I Iiflooecomy (mnedical) 5%-Nucleur medicine Inuvt.0K onal (med"cal)Isomeose 12%(med-a 7%The chart above shows the contribution of various sources of exposure to the total collective effective dose and the total effective dose per individual in the U.S. population for 2006. Values have been rounded to the nearest 1%, except for those <1 % [less than 1%].Credit: Modification to image courtesy of National Council on Radiation Protection and Measurements.
Figure 1 is a pie chart showing the relative contributions of these sources of radiation to the dose received by the average American.
Larger contributors to dose are represented by proportionally larger slices of the pie. Doses to the public from NPPs are included in the industrial category; doses to workers from nuclear power generation are included in the category of occupational dose. Doses to the public due to effluents from NPPs are less than 0.1% (one-tenth of one percent) of what the average person receives each year from all sources of radiation.
Doses to workers from occupational exposures, including those received from work at NPPs, also are less than 0.1% of the average dose to a member of the public from all sources.ENVIRONMENTAL RADIONUCLIDES Many radionuclides are present in the environment due to sources such as cosmic radiation and fallout from nuclear weapons testing. These radionuclides are expected to be present in many of the environmental samples collected in the vicinity of PNPP. Some of the radionuclides normally present include: Page 7 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Beryllium-7, present as a result of the interaction of cosmic radiation with the upper atmosphere, Potassium-40, a naturally occurring radionuclide normally found in humans and throughout the environment, and Radionuclides from nuclear weapons testing fallout, including tritium and cesium-1 37.These radionuclides may also be released in minute amounts from nuclear facilities.
Beryllium-7 and potassium-40 are especially common in REMP samples. Since they are naturally occurring and are expected to be present, positive results for these radionuclides are not discussed in the section for the 2014 Sampling Program results. These radionuclides are included; however, in Appendix A, 2014 Inter-Laboratory Cross Check Comparison Program Results.RADIOACTIVE EFFLUENT RELEASES INTRODUCTION The source of radioactive material in a nuclear power plant is the generation of fission products (e.g., noble gas, iodine, and particulate) or neutron activation of water and corrosion products (e.g., tritium and cobalt). The majority of the fission products generated remain within the nuclear fuel pellet and fuel cladding.
Most fission products that escape from the fuel cladding, as well as the majority of the activated corrosion products, are removed by plant processing equipment.
During the normal operation of a nuclear power plant, small amounts of radioactive material are released in the form of solids, liquids, and gases. PNPP was designed, and is operated in such a manner as to control and monitor these effluent releases.
Effluents are controlled to ensure any radioactivity released to the environment is minimal and within regulatory limits. Effluent release programs include the operation of monitoring systems, in-plant sampling and analysis, quality assurance, and detailed procedures covering all aspects of effluent monitoring.
The liquid and gaseous radioactive waste treatment systems at PNPP are designed to collect and process these wastes in order to remove most of the radioactivity.
Effluent monitoring systems are used to provide continuous indication of the radioactivity present and are sensitive enough to measure several orders of magnitude lower than the release limits. This monitoring equipment is equipped with alarms and indicators in the plant control room. The alarms are set to provide warnings to alert plant operators when radioactivity levels reach a small fraction of the limits. The waste streams are sampled and analyzed to identify and quantify the radionuclides being released to the environment.
Gaseous effluent release data is coupled with on-site meteorological data in order to calculate the dose to the general public. Devices are maintained at various locations around PNPP to continuously sample the air in the surrounding environment.
Frequent samples of other environmental media are also taken to determine if any radioactive material deposition has occurred.
The Radiological Environmental Monitoring Program (REMP) is described in detail later in this report.Generation of solid waste is carefully monitored to identify opportunities for minimization.
Limiting the amount of material taken into the plant, sorting material as radioactive or non-Page 8 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT radioactive waste, and incinerating waste once it is identified help to lower the volume of radioactive solid waste generated.
Solid waste is shipped to a licensed burial site.REGULATORY LIMITS The Nuclear Regulatory Commission has established limits for liquid and gaseous effluents that comply with: Title 10 of the Code of Federal Regulations, Part 20 (Standards for Protection Against Radiation)
[10CFR20], Appendix B;Title 10 of the Code of Federal Regulations, Part 50 (Domestic Licensing of Production and Utilization Facilities)
[10CFR50], Appendix I; and Title 40 of the Code of Federal Regulations, Part 190 (Environmental Radiation Protection Standards for Nuclear Power Plants) [40CFR1 90].These limits were incorporated into the PNPP Technical Specifications, and subsequently into the PNPP ODCM. The ODCM prescribes the maximum doses and dose rates due to radioactive effluents resulting from the operation of PNPP. These limits are defined in several ways to limit the overall impact on persons living near the plant. Since there are no other fuel sources near the PNPP, the 40CFR1 90 limits, which are described below, were not exceeded in 2014.The 40CFR190 limit for whole body dose is 25 mrem. For 2014, the total whole body dose to a member of the general public, considering all sectors, was 0.247 millirem.
This value was determined by summing the annual whole body doses from liquid and gaseous radioactive effluents and the annual gaseous Carbon-14 dose. Since the direct radiation dose, as determined by TLD, was indistinguishable from natural background (see Figure 9), it was not included in the calculation.
LIQUID EFFLUENTS The concentration of radioactive material released in liquid effluents to unrestricted areas shall be limited to the concentrations specified in 1OCFR20, Appendix B, Table 2, Column 2 for radionuclides other than dissolved or entrained noble gases, as required by the ODCM.For dissolved or entrained noble gases, the concentration is limited to a concentration of 2.OE-04 pCi/ml. These values are the maximum effluent concentrations.
The dose or dose commitment to a member of the public from radioactive materials in liquid effluents released to unrestricted areas shall be limited to the following:
During any calendar quarter: Less than or equal to 1.5 mrem to the whole body, and Less than or equal to 5 mrem to any organ During any calendar year: Less than or equal to 3 mrem to the whole body, and Less than or equal to 10 mrem to any organ Page 9 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT GASEOUS EFFLUENTS The dose rate due to radioactive materials released in gaseous effluents from the site to areas at and beyond the site boundary shall be limited to the following as required by the ODCM: Noble gases: Less than or equal to 500 mrem per year to the whole body, and Less than or equal to 3000 mrem per year to any organ Iodine-1 31, Iodine-1 33, Tritium, and all radionuclides in particulate form with half lives greater than eight days: Less than or equal to 1500 mrem per year to any organ Air dose due to noble gases to areas at, and beyond the site boundary, shall be limited to the following:
During any calendar quarter: Less than or equal to 5 mrad for gamma radiation, and Less than or equal to 10 mrad for beta radiation During any calendar year: Less than or equal to 10 mrad for gamma radiation, and Less than or equal to 20 mrad for beta radiation-Dose to a member of the public from Iodine-1 31, Iodine-1 33, Tritium, and all radionuclides in particulate form with half-lives greater than eight days in gaseous effluents released to areas at and beyond the site boundary shall be limited to the following:
Less than or equal to 7.5 mrem to any organ per any calendar quarter, and Less than or equal to 15 mrem to any organ per any calendar year The PNPP ODCM does not contain a concentration limit for gaseous effluents.
For this reason, effluent concentrations are not used to calculate maximum release rates for gaseous effluents.
Page 10 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT RELEASE
SUMMARY
Effluents are sampled and analyzed to identify both the type and quantity of radionuclides present. This information is combined with effluent path flow measurements to determine the composition, concentration, and dose contribution of the radioactive effluents.
Liquid Effluents The PNPP liquid radioactive waste system is designed to collect and treat all radioactive liquid waste produced in the plant. The treatment process used for radioactive liquid waste depends on its physical and chemical properties.
It is designed to reduce the concentration of radioactive material in the liquid by filtration to remove suspended solids and demineralization to remove dissolved solids. Normally, the effluent from the liquid radioactive waste system is returned to plant systems. To reduce the volume of water stored in plant systems; however, the processed liquid effluent may be discharged from the plant via a controlled release. In this case, effluent activity and dose calculations are performed prior to and after discharging this processed water to Lake Erie to ensure regulatory compliance and dose minimization principles are maintained.
Liquid radioactive waste system effluents may be intermittently released, which are considered to be "batch" releases.
Table 1 provides information on the number and duration of these releases.Table 1: Liquid Batch Releases Quarter 1 Quarter 2 Quarter 3 Quarter 4 Number of batch releases 0 0 0 8 Total time period for batch releases, min NA NA NA 2.17E+03 Maximum time for a batch release, min NA NA NA 3.62E+02 Average time period for a batch release, NA NA NA 2.72E+02 min Minimum time for a batch release, min NA NA NA 2.26E+02 Table 2 provides information on the nuclide composition for the liquid radioactive effluent system releases.
If a radionuclide was not present at a level "greater than or equal to the LLD" (>_LLD), then the value is expressed as "less than the LLD" (<LLD). In each case, LLDs were met, or were below the levels required by the ODCM. Table 2a provides information specific to radioactive effluent batch releases and Table 2b provides information specific to continuous radioactive effluent releases.Page 11 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Table 2: Summation of All Liquid Effluent Releases Quarter 1 Quarter 2 Quarter 3 Quarter 4 Est. Total Error, (%)Fission and Activation Products Total Released, CiI Tota(exluigtu, g s a6.72E-04 8.75E-05 1.78E-03 8.04E-04 1.OOE+01 (excluding tritium, gases, alpha)Average Diluted Concentration, pCi/mL
- 4.75E-1 1 4.55E-12 6.04E-1 1 3.91 E-11 ]1 " Percent of Applicable Limit, % 1.60E-03 1.98E-04 8.43E-04 1.01 E-03 , " Tritium Total Released, Ci 5.84E-02 5.50E-03 5.63E+00 3.88E+00 1.OOE+01 Average Diluted Concentration, ijCi/mL 4.13E-09 2.86E-10 1.91 E-07 1.81 E-07 .Percent of Applicable Limit, % 4.13E-04 2.86E-05 1.91 E-02 1.81 E-02 ' .Dissolved and Entrained Gases Total Released, Ci <LLD <LLD 5.53E-06 6.24E-04 1.OOE+01 Average Diluted Concentration, pCi/mL <LLD <LLD 1.88E-1 3 2.91 E-1 1 Percent of Applicable Limit, % NA NA 9.38E-08 1.45E-05 Gross Alpha Activity, Ci 3.30E-04 <LLD 1.16E-05 <LLD 1.OOE+01 Waste Volume Released, Liters (prior to : 2E0711 E0 .1 +6 1,7-0 dilution)1.25E+07 1.11E+07 4.21 E+06 1.79E+06":";+'"'
dilution)
Weo e eLe1E 1.92E+10 25 0 E1___.Dilution Water Volume Used, Liters 1.41E+10 1.92E+10 2.95E+10 2.15E+10<LLD -Less than the lower limit of detection*Average diluted concentrations are based on total volume of water released during quarter.Table 2a: Summation of Batch Liquid Effluent Releases Quarter 1 Quarter 2 Quarter 3 Quarter 4 Estoilt A. Fission and Activation Products Total Released, Ci NA NA NA 8.29E-05 1.OOE+01 (excluding tritium, gases, alpha)B. Tritium Total Released, Ci NA NA NA 3.88E+00 1.OOE+01 C. Dissolved and Entrained Gases Total Released, Ci NA NA NA 6.25E-04 1.OOE+01 D. Gross Altha Activity, Ci NA NA NA <LLD 1.OOE+01 E. Waste Volume Released, Liters (prior to 0.OOE+00 O.OOE+00 0.OOE+00 1.02E+06 dilution)<LLD -Less than the lower limit of detection Page 12 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Table 2b: Summation of Continuous Liquid Effluent Releases Quarter 1 Quarter 2 Quarter 3 Quarter 4 Est. Total Error, (%)A. Fission and Activation Products Total Released, Ci 6.72E-04 8.75E-05 1.76E-03 7.56E-04 1.OOE+01 (excluding tritium, gases, alpha)B. Tritium Total Released, Ci 5.84E-02 5.50E-03 5.63E+00 3.04E-03 1.00E+01 C. Dissolved and Entrained Gases Total Released, Ci <LLD <LLD 3.77E-06 <LLD 1.00E+01 D. Gross Alpha Activity, Ci 3.30E-04 <LLD 1.16E-05 <LLD 1.OOE+01 E. Waste Volume Released, Liters (prior to 1.25E+07 1.11 E+07 4.21 E+06 7.74E+05 dilution)<LLD -Less than the lower limit of detection Table 3 lists the total number of curies (Ci) of each radionuclide present in liquid effluent releases for each quarter. If a radionuclide was not present at a level "greater than or equal to the LLD" (_LLD), then the value is expressed as "less than the LLD" (<LLD). In each case, the LLDs were either met, or were below the levels required by the ODCM.Page 13 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Table 3 Radioactive Liquid Effluent Nuclide Composition Units Quarter 1 Quarter 2 Quarter 3 Quarter 4 Annual Tritium Ci 5.84E-02 5.50E-03 5.63E+00 3.88E+00 9.57E+00 Sodium-24 Ci <LLD <LLD 1.97E-04 <LLD 1.97E-04 Chromium-51 Ci <LLD <LLD 3.96E-04 4.32E-05 4.39E-04 Manganese-54 Ci 3.34E-07 <LLD 1.50E-04 1.03E-04 2.53E-04 Manganese-56 Ci <LLD <LLD 6.28E-05 <LLD 6.28E-05 Iron-55 Ci <LLD <LLD <LLD <LLD <LLD Iron-59 Ci <LLD <LLD 6.35E-05 1.90E-06 6.54E-05 Cobalt-58 Ci <LLD <LLD 6.96E-05 5.55E-05 1.25E-04 Cobalt-60 Ci 6.68E-04 7.44E-05 6.56E-04 6.23E-04 2.02E-03 Zinc-65 Ci <LLD <LLD 2.90E-05 9.79E-06 3.88E-05 Zinc-69m Ci <LLD <LLD 2.83E-05 <LLD 2.83E-05 Strontium-89 Ci <LLD <LLD <LLD <LLD <LLD Strontium-90 Ci <LLD <LLD <LLD <LLD <LLD Strontium-91 Ci <LLD <LLD 1.08E-05 <LLD 1.08E-05 Strontium-92 Ci <LLD <LLD 1.20E-05 <LLD 1.20E-05 Yttrium-91 m Ci <LLD <LLD 1.59E-05 <LLD 1.59E-05 Zirconium-95 Ci <LLD <LLD 4.26E06 7.41 E-07 5.OOE-06 Niobium-95 Ci <LLD <LLD 9.74E-06 2.70E-06 1.24E-05 Molybdenum-99 Ci <LLD <LLD <LLD <LLD <LLD Technicium-99m Ci <LLD <LLD 3.91 E-06 <LLD 3.91 E-06 Silver-110m Ci <LLD <LLD <LLD 2.46E-07 2.46E-07 Iodine-1 31 Ci <LLD <LLD 8.39E-07 <LLD 8.39E-07 Cesium-134 Ci 1.25E-06 2.19E-06 <LLD <LLD 3.44E-06 Cesium-1 37 Ci 2.84E-06 1.09E-05 2.47E-07 <LLD 1.40E-05 Cerium-141 Ci <LLD <LLD <LLD <LLD <LLD Cerium-144 Ci <LLD <LLD <LLD <LLD <LLD Gold-1 99 Ci <LLD <LLD 6.55E-05 <LLD 6.55E-05 Argon-41 Ci <LLD <LLD 1.76E-06 <LLD 1.76E-06 Xenon-1 33 Ci <LLD <LLD 4.21 E-07 5.99E-04 5.99E-04 Xenon-135 Ci <LLD <LLD 3.35E-06 2.58E-05 2.92E-05 Gross Alpha Ci 3.30E-04 <LLD 1.16E-05 <LLD 3.42E-04<LLD -Less than the lower limit of detection Page 14 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Gaseous Effluents Gaseous effluents are made up of fission and activation gases, iodine and particulate releases.
Gaseous effluents from PNPP exit the plant via one of four effluent vents. Each of these four effluent vents contains radiation detectors that continuously monitor the air to ensure that the levels of radioactivity released are below regulatory limits. Samples are also collected and analyzed on a periodic basis to ensure regulatory compliance.
Gaseous effluents released from PNPP are considered continuous and at ground level.In 2013 PNPP increased the volume of air captured when sampling for tritium in gaseous effluents.
This has increased the detection capability (LLD) by a factor of 20. Gaseous effluent tritium releases are now being detected where before they were too dilute to measure. This has resulted in a reported increase in tritium released over previous years.A summation of all gaseous radioactive effluent releases is given in Table 4.Table 4: Summation of All Gaseous Effluents Quarter 1 Quarter 2 Quarter 3 Quarter 4 Est. Total Error, %A. Fission and Activation Products I I I I _Error,_%Total Released, Ci <LLD <LLD <LLD 6.69E+01 1.OOE+01 Average Release Rate, pCi/sec <LLD <LLD <LLD 8.41 E+00 Percent of Applicable Limit, % N/A N/A N/A N/A B. Iodine Total Iodine-131 Released, Ci <LLD <LLD 7.65E-05 1.90E-04 1.OOE+01 Average Release Rate, pCi/sec <LLD <LLD 9.62E-06 2.39E-05 Percent of Applicable Limit, % N/A N/A N/A N/A C. Particulates with Half-Lives
> 8 days Total Released, Ci <LLD 4.43E-06 6.01 E-06 1.45E-05 1.OOE+01 Average Release Rate, pCi/sec <LLD 5.63E-07 7.56E-07 1.83E-06 Percent of Applicable Limit, % N/A N/A N/A N/A D. Alpha Activity, Ci 1.61 E-06 1.03E-06 6.13E-07 1.73E-06 1.OOE+01 E. Tritium Total Released, Ci 1.39E+00 3.07E+00 2.66E+00 2.35E+00 1.OOE+01 Average Release Rate, pCi/sec 11.79E-01 3.90E-01 3.35E-01 2.96E-01 Percent of Applicable Limit, % N/A N/A N/A N/A F. Carbon-14, Ci 4.56E+00 4.63E+00 4.69E+00 4.07E+00 1.OOE+01<LLD -Less than the lower limit of detection N/A -Not Applicable, the ODCM does not have a release rate limit for gaseous effluents.
Carbon-14 activity was calculated based on power production and using the EPRI provided Spreadsheet.
Page 15 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT The radionuclide composition of all gaseous radioactive effluents for a continuous-mode, ground-level release is given in Table 5. If a radionuclide was not present at a level"greater than or equal to the LLD" (_LLD), then the value is expressed as "less than the LLD" (<LLD). In each case, LLDs were met or were below the levels required by the ODCM. Discussion of Carbon-14 doses is listed on page 23, Carbon-14 supplemental information.
Page 16 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Table 5: Radioactive Gaseous Effluent Nuclide Composition Unit Quarter 1 Quarter 2 Quarter 3 Quarter 4 Annual A. Fission and Activation Products Tritium Ci 1.39E+00 3.07E+00 2.66E+00 2.35E+00 9.47E+00 Argon-41 Ci <LLD <LLD <LLD <LLD <LLD Krypton-85m Ci <LLD <LLD <LLD 6.34E-01 6.34E-01 Krypton-85 Ci <LLD <LLD <LLD <LLD <LLD Krypton-87 Ci <LLD <LLD <LLD 2.86E-01 2.86E-01 Krypton-88 Ci <LLD <LLD <LLD 4.78E-01 4.78E-01 Xenon-133m Ci <LLD <LLD <LLD 4.04E-01 4.04E-01 Xenon-133 Ci <LLD <LLD <LLD 5.32E+01 5.32E+01 Xenon-135m Ci <LLD <LLD <LLD 3.24E+00 3.24E+00 Xenon-1 35 Ci <LLD <LLD <LLD 7.84E+00 7.84E+00 Xenon-138 Ci <LLD <LLD <LLD 7.87E-01 7.87E-01 Total for Period 1.39E+00 3.07E+00 2.66E+00 6.92E+01 7.63E+01 B. Iodine Iodine-1 31 Ci <LLD <LLD 7.65E-05 1.90E-04 2.67E-04 Iodine-133 Ci <LLD <LLD <LLD 3.41 E-04 3.41 E-04 Iodine-135 Ci <LLD <LLD <LLD <LLD <LLD Total for Period NA NA 7.65E-05 5.30E-04 6.07E-04 C. Particulate Chromium-51 Ci <LLD <LLD <LLD <LLD <LLD Manganese-54 Ci <LLD <LLD <LLD <LLD <LLD Iron-59 Ci <LLD <LLD <LLD <LLD <LLD Cobalt-58 Ci <LLD <LLD <LLD <LLD <LLD Cobalt-60 Ci <LLD <LLD <LLD <LLD <LLD Zinc-65 Ci <LLD <LLD <LLD <LLD <LLD Strontium-89 Ci <LLD 4.43E-06 6.01E-06 1.38E-05 2.42E-05 Strontium-90 Ci <LLD <LLD <LLD 7.27E-07 7.27E-07 Strontium-92 Ci <LLD <LLD <LLD <LLD <LLD Zirconium-95 Ci <LLD <LLD <LLD <LLD <LLD Molybdenum-99 Ci <LLD <LLD <LLD <LLD <LLD Cesium-134 Ci <LLD <LLD <LLD <LLD <LLD Cesium-137 Ci <LLD <LLD <LLD <LLD <LLD Cerium-141 Ci <LLD <LLD <LLD <LLD <LLD Cerium-144 Ci <LLD <LLD <LLD <LLD <LLD Total for Period NA 4.43E-06 6.01 E-06 1.45E-05 2.49E-05<LLD -Less than the lower limit of detection Page 17 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Solid Waste All solid radioactive waste from PNPP was processed and combined with waste from several other utilities by intermediate vendors (Energy Solutions and Erwin Resin Solutions).
This waste was ultimately sent to Clive, Utah disposal facilities for burial. The solid radioactive waste summary in Table 6 includes all PNPP shipments.
Table 6: Solid Waste Shipped Offsite for Burial or Disposal A. Type of Solid Waste Shipped Volume Activity Est. Total Error (M3) (Ci) (%)Resins, Filters and Evaporator Bottoms 1.39E+02 1.20E+03 +/- 25 Dry Active Waste 1.13E+03 6.31 E+00 +/- 25 Irradiated components, control rods, etc. O.OOE+00 O.OOE+00 +/- 25 Other Waste 0.OOE+00 0.OOE+00 +/- 25 B. Estimate of Major (1) Nuclide Composition Radionuclide Abundance Est. Total (by type of waste) (%) Error, (%)Resins, Filters and Evaporator Bottoms Mn-54 4.23 +/- 25 Fe-55 27.29 Co-60 61.60 Zn-65 3.85 Dry Active Waste Mn-54 2.37 +/- 25 Fe-55 32.48 Co-60 62.03 Zn-65 1.22 Irradiated Components, Control Rods, etc. N/A N/A N/A Other Waste N/A N/A N/A C. Disposition Number of Mode of Destination Shipments Transportation Solid Waste (2) 63 Highway Carrier Energy Solutions, Bear Creek, TN Solid Waste (2) 22 Highway Carrier Erwin Resin Solutions LLC Erwin TN N/A -Not Applicable (1) -- "Major" is defined as any individual radionuclide identified as >1% of the waste type abundance.
(2) -- This waste was combined with waste from other utilities and disposed of at Clive, Utah.Page 18 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT METEOROLOGICAL DATA The Meteorological Monitoring System at PNPP consists of a 60-meter tower equipped with two independent systems for measuring wind speed, wind direction, and temperature at both 10-meter and 60-meter heights. The tower also has instrumentation to measure dew point and barometric pressure.
Data is logged from the tower through separate data loggers, and transmitted to a common plant computer.
This system compiles the data and calculates a variety of atmospheric parameters, communicates with the Meteorological Information Dose Assessment System (MIDAS), and sends data over communication links to the plant Control Room.A detailed report of the monthly and annual operation of the PNPP Meteorological Monitoring Program is produced under separate cover. For the period of January 1, 2014 through December 31, 2014, the report substantiates the quality and quantity of meteorological data collected in accordance with applicable regulatory guidance.DOSE ASSESSMENT The maximum concentration for any radioactive release is controlled by the limits set forth in Title 10 of the Code of Federal Regulations, Part 20 (1OCFR20).
Sampling, analyzing, processing, and monitoring the effluent stream ensures compliance with these concentration limits. Dose limit compliance is verified through periodic dose assessment calculations.
Some dose calculations are conservatively performed for a hypothetical individual who is assumed to reside on the site boundary at the highest potential dose location all year. This person, called the "maximum individual", would incur the maximum potential dose from direct exposure (air plus ground plus water), inhalation, and ingestion of water, milk, vegetation, and fish. Because no one actually meets these criteria, the actual dose received by a real member of the public is significantly less than what is calculated for this hypothetical individual.
Dose calculations for this maximum individual at the site boundary are performed for two cases. First, they are performed using data for a 360 degree radius around the plant site (land and water based meteorological sectors);
even though some of these sectors are over Lake Erie, Which has no permanent residents.
The second calculation is performed considering only those sectors around the plant in which people reside (land-based meteorological sectors).The calculated hypothetical, maximum individual dose values at the site boundary are provided in Table 7. This table considers all meteorological sectors around PNPP and provides either the whole body or worst-case, organ dose values.Page 19 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Table 7: Maximum Individual Site Boundary Dose, Considering All Sectors Type of Dose Organ Estimated Limit % of Dose, (mrem) Limit Liquid Effluent Whole body 9.OOE-04 3.OE+00 3.OE-02 Liver 1.03E-03 1.OE+01 1.OE-02 Noble Gas Air Dose 2.13E-02 1.OE+01 2.1E-01 Gamma -mrad Air Dose 3.10E-02 2.OE+01 1.6E-01 Beta -mrad Noble Gas Whole body 1.70E-02 5.OE+00 3.4E-01 Skin 3.52E-02 1.5E+01 2.3E-01 Particulate
& Iodine Thyroid 5.47E-03 1.5E+01 3.6E-02 The calculated hypothetical, maximum 50-mile radius population dose values at the site boundary are provided in Table 8. This table considers all meteorological sectors around PNPP and provides either the whole body or worst-case, organ dose values.Table 8: Population Dose, Considering All Sectors out to 50 miles.Organ Estimated Dose (person-rem)
Liquid Effluent Whole body 1.5E-01 Thyroid 1.3E-01 Gaseous Effluent Whole body 1 .9E-03 Thyroid 2.5E-03 Page 20 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Table 9 provides the calculated hypothetical maximum site boundary dose values considering only the land-based sectors.Table 9: Maximum Individual Site Boundary Dose, Considering Sectors on Land Type of Dose Organ Estimated Limit % of Dose, (mrem) Limit Liquid Effluent Whole Body 9.OOE-04 3.OE+00 3.OE-02 Liver 1.03E-03 1.OE+01 1.OE-02 Noble Gas Air Dose 2.43E-03 1.OE+01 2.4E-02 Gamma -mrad Air Dose 3.60E-03 2.OE+01 1.8E-02 Beta -mrad Noble Gas Whole Body 5.18E-04 5.OE+00 1.OE-02 Skin 1.28E-03 1.5E+01 8.5E-03 Particulate
& Iodine Thyroid 5.61 E-04 1.5E+01 3.7E-03 Carbon-14
- Whole Body 2.46E-01 5.OE+00 4.9E+00**C-14 Dose calculated at nearest garden.Other dose calculations are performed for a hypothetical individual who is assumed to be inside the site boundary for some specified amount of time. This person would receive the maximum dose during the time spent inside site boundary.
Because no one actually meets the criteria established for these conservative calculations, the actual dose received by a member of the public is significantly less than what is calculated for this hypothetical individual.
This dose is assessed relative to the offsite dose, and considers dilution, dispersion, and occupancy factors.The highest hypothetical dose from liquid effluents to a member of the public inside the site boundary is to a person who is fishing on Lake Erie from the shore on PNPP property.
The calculations assume that this person will spend 60 hours6.944444e-4 days <br />0.0167 hours <br />9.920635e-5 weeks <br />2.283e-5 months <br /> per year fishing, with a liquid dilution factor of 10. The ratio of the exposure pathway to the doses calculated for offsite locations yields the dose values shown in Table 10.Table 10: Maximum Site Dose from Liquid Effluents Whole Body Dose, Organ Dose (mrem) (mrem)First Quarter 7.1 E-05 8.3E-05 Second Quarter 8.7E-06 1.OE-05 Third Quarter 4.OE-05 4.7E-05 Fourth Quarter 5.2E-05 6.2E-05 Annual 1.7E-04 2.OE-04 Page 21 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Although several cases were evaluated to determine the highest hypothetical dose from gaseous effluents to members of the public inside site boundary, the activity inside the site boundary with the highest dose potential is also shoreline fishing. The cases evaluated included traversing a public road within the site boundary, shoreline fishing (assuming fishing 60 hours6.944444e-4 days <br />0.0167 hours <br />9.920635e-5 weeks <br />2.283e-5 months <br /> per year), non-plant related training, car-pooling, and job interviews.
The maximum on-site gaseous doses generated are shown in Table 11.Table 11: Maximum Site Dose from Gaseous Effluents Whole Body Dose, Organ Dose (mrem) (mrem)First Quarter 6.OE-05 6.OE-05 Second Quarter 1.4E-04 1.4E-04 Third Quarter 1.3E-04 .8E-04 Fourth Quarter 1.8E-03 4.4E-03 Annual 2.2E-03 4.8E-03 An average whole body dose to individual members of the public at or beyond the site boundary is then determined by combining the dose from gaseous and liquid radiological effluents.
The dose from gaseous radiological effluents is based upon the population that lives within 50 miles of PNPP. The dose from liquid radiological effluents is determined for the population that receives drinking water from intakes within 50 miles of PNPP. The results of this calculation are provided in Table 12.Table 12: Average Individual Whole Body Dose Liquid Effluents Gaseous Effluents (mrem) (mrem)First Quarter 4.2E-06 4.6E-08 Second Quarter 5.8E-06 1.2E-07 Third Quarter 4.2E-05 1.5E-07 Fourth Quarter 9.2E-06 3.4E-07 Annual 6.1E-05 6.6E-07 Page 22 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT CARBON-14 SUPPLEMENTAL INFORMATION Carbon-14 (C-14), with a half-life of 5730 years, is a naturally occurring isotope of carbon produced by cosmic ray interactions in the atmosphere.
Nuclear weapons testing in the 1950s and 1960s significantly increased the amount of C-14 in the atmosphere.
C-14 is also produced in commercial nuclear reactors, but the amounts produced are much less than those produced naturally or from weapons testing. C-14 is released primarily from BWRs through the off-gas system in the form of carbon dioxide (C02). The quantity of gaseous C-14 released to the environment can be estimated using a C-14 source term scaling factor based on power generation.
The U.S. Nuclear Regulatory Commission (NRC) requires an assessment of gaseous C-14 dose impact to a member of the public resulting from routine releases in radiological effluents.
Prior to 2011, the industry did not estimate the dose impact of C-14 releases.Since the dose contribution had been considered negligible compared to the dose impact from effluent releases of noble gases, tritium, particulates and radioiodines.
At PNPP, improvements over the years in effluent management practices and fuel performance have resulted in a decrease in the concentration and changes in the distribution of gaseous radionuclides released to the environment.
This report contains estimates of the gaseous C-14 radioactivity released in 2014 and the resulting public dose resulting from this release. This calculation is done using a spreadsheet provided by EPRI and is based on power production.
This method for estimating C-14 release has been endorsed by the NRC. Because the dose contribution of C-14 from liquid radioactive waste is much less than that contributed by gaseous radioactive waste, evaluation of C-14 in liquid radioactive waste at PNPP is not required.Refer to Table 4 and Table 9 for C-14 estimated release values and doses.GROUNDWATER MONITORING PROGRAM Based on the ERM hydrogeology study, 12 wells were recommended for the site. Since most groundwater flow drains north towards Lake Erie, the majority of wells are drilled there. A set of control wells was drilled south of the plant, to assess what a typical groundwater profile would be.There are 4 sets of triplet wells installed at each location.
Each triplet has a shallow well (approximately 25 feet), a mid-depth well of approximately 50 feet, and a deep well of approximately 75 feet. These 3 depths are designated A, B and C, from shallowest to deepest, respectively.
Refer to Figure 2 for locations of Groundwater wells 1A through 4C.These wells encompass the groundwater monitoring locations at PNPP.Page 23 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Figure 2: Underdrain System and On-Site Groundwater Wells* Manholes SPezormeters Groundwater Webls 0* 0..a Ask*E I a.......Ai ;Page 24 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT The monitoring wells are sampled twice annually, in spring and fall. The sampling is done by personnel from FirstEnergy's BETA Laboratories.
The samples are shipped to Midwest Laboratories in Illinois.
Midwest analyzes the sample for gamma isotopic and tritium. Any positive result less than 500 pCi/L is considered as background activity and not due to plant operations.
There was no indication of any effluent releases via groundwater.
Table 13: Summary of Onsite Groundwater Samples Monitoring Well Spring Fall H-3, pCi/L H-3, pCi/L 1A <LLD <LLD 1B <LLD <LLD 1C <LLD <LLD 2A <LLD <LLD 2B <LLD <LLD 2C <LLD <LLD 3A 170 <LLD 3B <LLD <LLD 3C <LLD <LLD 4A <LLD <LLD 4B <LLD <LLD 4C <LLD <LLD Page 25 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT CORRECTIONS TO PREVIOUS ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORTS See Appendix D for description of corrections to previous Annual Environmental and Effluent Release Reports.ABNORMAL RELEASES See Appendix E for description of an Abnormal Release from the Nuclear Closed Cooling (NCC) system and Feedwater Venturi Leak.ODCM NON-COMPLIANCES See Appendix F for description of ODCM Non-Compliances.
OFFSITE DOSE CALCULATION MANUAL CHANGES See Appendix G for description of changes to the ODCM.PROCESS CONTROL PROGRAM CHANGES See Appendix H for description of changes to the Process Control Program Page 26 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT RADIOLOGICAL ENVIRONMENTAL MONITORING INTRODUCTION The Radiological Environmental Monitoring Program (REMP) was established at PNPP for several reasons. First, it verifies the adequacy of plant design and operation to control radioactive materials and limit effluent releases.
Second, it assesses the radiological impact, if any, that the plant has had on the surrounding environment.
Third, it ensures compliance with regulatory guidelines.
The REMP is conducted in accordance with the PNPP Operating License, Appendix B, Technical Specifications and the ODCM. The Nuclear Regulatory Commission (NRC) established the REMP requirements.
A variety of samples are collected as part of the PNPP REMP. The selection of sample types, locations, and collection frequency are based on many things. Potential pathways for the transfer of radionuclides through the environment to humans, sample availability, local meteorology, population characteristics, land use and NRC requirements are all factors.To ensure that the REMP data are meaningful and useful, detailed sampling methods and procedures are followed.
This ensures that samples are collected in the same manner and from the same locations each time. All samples are packaged on site, and then shipped to an independent vendor laboratory for analysis.
The vendor laboratory analyzes the samples and reports results to the PNPP Chemistry Unit staff, the Lake County General Health District, and the State of Ohio Department of Health. Additionally the Lake County General Health District obtains monthly "split" samples of milk, water and vegetation.
This permits an independent verification of PNPP's radiological environmental monitoring program.SAMPLING LOCATIONS REMP samples are collected at numerous locations, both on site and up to 20.6 miles away from the plant. Sampling locations are divided into two general categories:
indicator and control. Indicator locations are those that monitor for any environmental impact due to plant operations.
They are relatively close to the plant. Control locations are those that are unaffected by plant operation; they are a greater distance from the plant and in the least prevalent wind directions.
Data obtained from the indicator locations are compared with data from the control locations.
This comparison allows naturally occurring background radiation to be taken into account when evaluating any radiological impact PNPP may have had on the environment.
Table 14, Figure 3, Figure 4 and Figure 5 identify the PNPP REMP sampling locations.
Many REMP samples are collected in addition to those required by the PNPP ODCM. The ODCM requirements for each sample type are discussed in more detail later in the report.Page 27 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Table 14: REMP Sampling Locations Location # Description Miles Direction Media (1)1 Chapel Road 3.2 ENE TLD, AlP 2 Kanda Garden 2.0 ENE Food Products 3 Meteorological Tower 1.0 SE TLD, AlP 4 Site Boundary 0.7 S TLD, AlP 5 Quincy Substation 0.6 SW TLD, AlP 6 Concord Service Center 11.1 SSW TLD, AlP 7 Site Boundary 0.6 NE TLD, AlP 8 Site Boundary 0.7 E TLD 9 Site Boundary 0.7 ESE TLD 10 Site Boundary 0.6 SSE TLD 11 Parmly Rd. 0.6 SSW TLD 12 Site Boundary 0.6 WSW TLD 13 Madison-on-the-Lake 4.6 ENE TLD 14 Hubbard Rd. 4.9 E TLD 15 Eagle St. Substation 5.1 ESE TLD 16 Eubank Garden 0.9 S Food Products 18 Kijauskas Farm (goat) 2.6 E Food Products, Milk 19 Goodfield Dairy 9.2 S Milk 20 Rainbow Farms 1.9 E Food Products 21 Hardy Rd. 5.1 WSW TLD 23 High St. Substation 7.9 WSW TLD 24 St. Clair Ave. 15.0 SW TLD 25 Offshore -PNPP 2.0 NNW Sediment, Fish discharge 28 CEI Ashtabula Plant 20.6 ENE Water Intake 29 River Rd. 4.5 SSE TLD 30 Lane Rd. 4.9 SSW TLD 31 Wood and River Rd. 4.9 SE TLD 32 Offshore -Mentor 15.8 WSW Sediment, Fish 33 River Rd. 4.7 S TLD 34 PNPP Intake 0.2 NW Water Page 28 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Location # Description Miles Direction Media (1)35 Site Boundary 0.7 E TLD, AlP 36 Lake County Water Plant 4.0 WSW TLD, Water 37 Gerlica Farm 1.6 ENE Food Products 41 Tuttle Farm (goat) 5.8 SSE Milk 51 Rettger Milk Farm (cow) 9.7 S Milk 53 Great Lakes Nuclear 0.7 WSW TLD Services 54 Hale Rd. School 4.7 SW TLD 55 Center Rd. 2.5 S TLD 56 Madison High School 4.0 ESE TLD 57 Perry High School 1.7 S TLD 58 Antioch Rd. 0.8 ENE TLD 59 Lake Shoreline at Green 4.0 ENE Water Rd.60 Lake Shoreline at Perry 1.0 WSW Water Park 64 Northwest Drain Mouth 0.4 WNW Sediment 66 Lake Shore, Metropolitan 1.4 NE Sediment Park I I I _I 70 H&H Farm Stand 17.1 SSW Food Products (1) AlP = Air, Iodine and Particulate TLD = Thermoluminescent Dosimeter Page 29 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Figure 3: REMP Sampling Locations Within Two Miles of Plant Site NNW N NNE NW WNW W WSW SW NE ENE E ESE SE SSW S SSE I 0 I 2 MILES 6= = M ýMmýýPage 30 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Figure 4: REMP Sampling Locations Between Two and Eight Miles of the Plant Site SW SSW S 0 1 2 3 4 5 WLE 10 MILES se I ---I Page 31 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Figure 5: REMP Sampling Locations Greater Than Eight Miles from the Plant Site I S 1 o i1 20 MILES L [<M F I I I Page 32 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT SAMPLE ANALYSIS When environmental samples are analyzed for radioactivity, several types of measurements are performed to provide information about the types of radiation and radionuclides present.The major analyses that are performed are discussed below.Gross beta activity measures the total amount of beta-emitting radioactivity present in a sample, and acts as a tool to identify samples that may require further analysis.
Beta radiation may be released by many different radionuclides.
Since beta decay results in a continuous energy spectrum rather than the discrete energy levels, or "peaks", associated with gamma radiation, identification of specific beta-emitting nuclides is more difficult.
Therefore, gross beta activity only indicates whether the sample contains normal or abnormal amounts of beta-emitting radioactivity; it does not specifically identify the radionuclides present.Gamma spectral analysis provides more specific information than does the analysis for gross beta activity.
Gamma spectral analysis identifies each radionuclide, and the amount of radioactivity, present in the sample emitting gamma radiation.
Each radionuclide has a very specific "fingerprint" that allows for accurate identification and quantification.
Iodine activity analysis measures the amount of radioactive iodine present in a sample.Some media (for example, air sample charcoal cartridges) are analyzed directly by gamma spectral analysis.
With other media (for example, milk), the radioiodines are extracted by chemical separation before being analyzed by gamma spectral analysis.Tritium activity analysis measures the amount of the radionuclide tritium (H-3) present in a sample. Tritium is an isotope of hydrogen that emits low-energy beta particles.
Tritium occurs naturally and is also man-made.Gamma doses received by Thermoluminescent Dosimeters (TLD) while in the field are determined by a special laboratory procedure.
Thermoluminescence is a process by which ionizing radiation interacts with the sensitive phosphor material in the TLD. Energy is trapped in the TLD material and can be stored for months or years. This capability provides a method to measure the dose received over long periods of time. The amount of energy that was stored in the TLD as a result of interaction with radiation is released by a controlled heating process and measured in a calibrated reading system. As the TLD is heated, the phosphor releases the stored energy as light. The amount of light is directly proportional to the amount of radiation to which the TLD was exposed. Table 15 provides a list of the analyses performed on environmental samples collected for the PNPP REMP.Sample results are often reported as less than the lower limit of detection
(< LLD), which is defined as the smallest amount of radioactive material that will show a positive result for which there can be confidence that radioactivity is present. This statistical parameter is used as a measure of the sensitivity of a sample analysis.
When a measurement is reported as< LLD, it means that no radioactivity was detected.
The required detection limits for samples is determined by the sample media and the radionuclide that is being analyzed for and is listed in the ODCM. The NRC has established LLD values for REMP sample analyses.
The vendor laboratory for REMP sample analyses complied with those values.Page 33 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Table 15: REMP Sam le Analyses Type Sample Frequency Analysis Atmospheric Airborne Weekly & Gross Beta Activity &Monitoring Particulates Quarterly Gamma Spectral Analysis Airborne Radioiodine Weekly Iodine-I31 Terrestrial Gamma Spectral Analysis &Monitoring Milk Bi-Monthly Iodine-1 31 Broadleaf Monthly during Vegetation growing season Aquatic Monitoring Water Monthly Gross Beta Activity &AutMoirn WtrMtlGamma Spectral Analysis Quarterly Tritium Activity Fish Annually Gamma Spectral Analysis Sediment Biannually Gamma Spectral Analysis Direct Radiation TLD Quarterly
& Gamma Dose Monitoring Annually SAMPLING PROGRAM The contribution of radionuclides to the environment resulting from PNPP operation is assessed by comparing results from the environmental monitoring program with pre-operational data (i.e., data from before 1986), operational data from previous years, and control location data. The results for each sample type are discussed below and compared to historical data to determine if there are any observable trends. All results are expressed as concentrations.
Refer to Appendix B, 2014 REMP Data Summary Reports for a detailed listing of these results. The NRC requires special reporting whenever sample analysis results exceed set limits. No values exceeded those limits.PROGRAM CHANGES Due to beach erosion sample location #65 for sediment was no longer accessible.
In its place a new location, #66, was selected 1.4 miles NE of the plant. A new direct radiation (TLD) monitoring location, #57, was established at the Perry High School.MISSED SAMPLES On occasion, samples cannot be collected.
This can be due to a variety of events, including equipment malfunction, animal husbandry practices, or lost shipments.
Events may also occur which prevent a sample from being collected in the normal way, or prevent a complete sample from being collected.
The drying period for goats is an annual occurrence, since unlike cows, goats do not normally produce milk year-round.
Food products are weather dependent and are susceptible to excessive spring rains or summer drought that can significantly impact the garden harvest. Shoreline lake water samples are collected by grab Page 34 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT sample utilizing a container and scoop. During the winter months the shoreline can become inaccessible due to ice and snow buildup, preventing the safe collection of these samples.Shoreline sediment samples are collected with spoon and container.
On occasion, the accessibility of these locations and sample collection may be impacted due to high lake levels, shifting lake-bottom sediment, bluff erosion and shoreline collapse.
There was no impact to the program requirements as a result of any missed samples. Table 16 provides information on missed samples.Table 16: Missed REMP Sam pes in 2014 Media Location Date Reason Lake Water 59, 60 Jan -Mar Sample unavailable due to frozen shoreline Milk 18 Jan -Mar Drying period for goats/sample availability Drying period for goats/sample 41 Jan. -Apr, Oct. -Dec availability ATMOSPHERIC MONITORING Air Air sampling is conducted to detect any increase in the concentration of airborne radionuclides.
The PNPP REMP maintains an additional two (2) air sampling locations above the five (5) locations (four indicators and one control) required by the ODCM. Six (6)of these locations are within four miles of the plant site; the seventh is used as a control location and is eleven miles from PNPP. Air sampling pumps draw continuous samples at a rate of approximately two cubic feet per minute. The air is drawn through glass fiber filters (to collect particulate material) and a charcoal cartridge (to adsorb iodine). The samples are collected on a weekly basis, 52 weeks a year, from each of the seven (7) air sampling stations.Air samples are analyzed weekly for gross beta activity and radioiodine activity.
The air samples are also analyzed by gamma spectral analysis quarterly.
A total of 364 air particulate and 364 air radioiodine samples were collected and analyzed.Gross beta activity was detected in all the air samples and ranged up to 0.048 pCi/m3. The average gross beta activity for the indicator locations was 0.023 pCi/m3 and the controls was 0.024 pCi/m3. Historically, the concentration of gross beta in air has been essentially identical at indicator and control locations.
Figure 6 reflects the average gross beta activity for 2014 and the previous years. All radioiodine samples were less than the lower limit of detection for Iodine-1 31.Except for naturally occurring Beryllium-7, no radionuclides were identified in the quarterly gamma spectral analysis above the LLD values.Page 35 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Figure 6: Annual Average Gross Beta Activity, in Air 0.05 0.04 0.03 0.02 0.01 0 N~~~ M' Co 1r-Cl NMeWt Year 0Indicator s Control TERRESTRIAL MONITORING Collecting and analyzing samples of milk and food products provides data to assess the build-up of radionuclides that may be ingested by humans. The historical data from soil and vegetation samples provides information on the atmospheric radionuclide deposition.
Milk Samples of milk are collected once each month from November through March, and twice each month from April through October. Sampling is increased during the summer because animals usually feed outside on pasture and not on stored feed. The PNPP REMP includes four (4) milk locations located 2.5, 5.8, 8.7 and 9.6 miles away from the plant.Since the milk sampling locations do not meet the requirements of the ODCM (only one milk-producing animal is located within the required distance vs. two required), food product sampling (discussed below) is done. Milk is collected from the available location to augment food product sampling.
If new locations that meet the ODCM requirements are identified in the future, they will be added to the program.Milk samples are analyzed by gamma spectral analysis for radioiodines and other radionuclides.
A total of sixty-four (64) milk samples were collected.
With the exception of naturally occurring Potassium-40, no other radionuclides were detected.Broadleaf Vegetation Because there are not a sufficient number of milk sampling locations, the PNPP REMP samples broadleaf vegetation.
These samples are collected monthly during the growing season from six (6) gardens in the vicinity of PNPP and one control location 16.2 miles SSW from PNPP.Seventy-three (73) samples were collected and analyzed by gamma spectral analysis.Page 36 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Four (4) vegetation types were grown and collected:
mustard, collard greens, turnip greens and Swiss chard. Beryllium-7 and Potassium-40, naturally-occurring radionuclides, were found in the samples, which is expected.
No other radionuclides were detected above the required LLDs.AQUATIC MONITORING Radionuclides may be present in Lake Erie from many sources other than the PNPP. These sources include atmospheric deposition, run-off/soil erosion, and releases of radioactivity in liquid effluents from hospitals, universities or other industrial facilities.
These sources provide two forms of potential radiation exposure, external and internal.
External exposure can occur from contact with water or shoreline sediments, while internal exposure can occur from either direct ingestion of radionuclides or the transfer of radionuclides through the aquatic food chain. Direct ingestion can occur from drinking the water, while the transfer via the aquatic food chain occurs from the eventual consumption of aquatic organisms, such as fish. To monitor these pathways, PNPP samples water, shoreline sediments, and fish.Water Water is sampled from five (5) locations along Lake Erie in the vicinity of the PNPP as required by the PNPP ODCM. Samples from three (3) locations are collected using composite sample pumps. The pumps are designed to collect water at regular intervals and composite it in a sample container.
Samples from the two (2) other locations are manually collected weekly and combined.
The containers are emptied monthly and the samples shipped to the vendor laboratory for analysis.Fifty-four (54) water samples were collected and analyzed for gross beta activity and gamma spectral analysis.
From these monthly samples, eighteen (18) quarterly composite samples were analyzed for tritium activity.Gross beta activity was detected in fifty-one (51) of the fifty-four (54) samples collected.
The indicator average gross beta activity was 2.2 pCi/L and the control average gross beta activity was 2.2 pCi/L. Refer to Figure 7 for the annual average gross beta activity for both indicator and control locations.
No tritium or gamma activity was detected.Page 37 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Figure 7: Annual Average Gross Beta Activity, In Water 4.5 4 .03 .3.5.) 3.0 2.5 2.0 1.5 1.0 0.5 0.0 Cs4 Cf -O 0) 0 -04J M' IT U)( CI I- CO 0) 0 -N Ce) 'q o -M9 21 0) M0g 0 0 0 0 0 0 0 0 0 0 -Z- '-0) 0>)0)00)0))0)0))
0 0 D0 000 000-~ ~ --N ' ' ' % N ( ( N ( N ( N ( N (Year a Indicator EControl There were no tritium or radionuclides detected by gamma spectral analysis.Sediment Sampling lake-bottom sediments can provide an indication of the accumulation of particulate radionuclides which may lead to internal exposure to humans through the ingestion of fish, the re-suspension into drinking water, or as an external radiation source to fishermen and swimmers from shoreline exposure.
Sediment was sampled from five (5) locations.
Sediment samples from offshore are collected using a hand dredge. Shoreline samples are collected using a scoop.Seven (7) sediment samples were collected in 2014 and analyzed by gamma spectroscopy.
The predominant radionuclide detected by gamma spectral analysis was naturally occurring Potassium-40.
Cesium-1 37 activity was detected in two (2) of the seven (7) samples collected.
The indicator Cesium-1 37 activity was 56.5 pCi/kg and the control activity was 80.4 pCi/kg. The average Cesium-137 radioactivity for all locations was 68.5 pCi/kg and is lower than the highest identified value of 864 pCi/kg established in 1981. Year-to-year variations in lake bottom sediment sample activity is expected and beyond the control of PNPP. For example, Cesium-1 37 activity variations (refer to Figure 8) in the control locations from year-to-year may be contributed to:* The movement of sediment on the lake bottom due to wave action and currents.* Difficulty in duplicating exact location and composition of bottom sediment sample from year to year even with assistance of GPS.Page 38 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Figure 8: Annual Average Cesium-137 Concentration in Sediment 1600 1400 1200 1000 S 800 600 400 200 n ,0o,0 0= 0 0) 0 0 0, 0 -.- --,- ) 0-- 0) 0) 0) 0) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Year o indicator IControl Fish Fish are analyzed primarily to quantify the dietary radionuclide intake by humans, and secondarily to serve as indicators of radioactivity in the aquatic ecosystem.
Fish are collected from two (2) locations, annually during the fishing season as required by the ODCM. An important sport or commercial species is targeted, and only the fillets are sent to the laboratory for analysis.
Fish sampling was performed for PNPP by a local licensed sport fisherman.
Twenty-two (22) fish samples were collected and analyzed -eleven (111) indicator and eleven (11) control. The species were smallmouth bass, white perch, walleye, redhorse sucker, gizzard shad, channel catfish and steelhead.
Naturally occurring Potassium-40 was found in all samples. No other radionuclides were detected.DIRECT RADIATION MONITORING Thermoluminescent Dosimeter (TILD)Environmental radiation is measured directly at twenty seven (27) locations around the PNPP site and two (2) control locations.
The locations are positioned in two rings around the plant as well as at the site boundary.
The inner ring is within a one-mile radius of the plant site; the outer ring is four miles to five miles from the plant. The control locations are over ten miles from the plant in the two least prevalent wind directions.
Each location has three TLDs, two of which are changed quarterly and one is changed annually.A total of 261 TLDs were collected and analyzed.
This includes 232 collected on a quarterly basis and twenty nine (29) collected annually.
Annual TLDs are not required per the ODCM and are used for supplemental data only.The annual average dose for all indicator locations was 64.0 mrem, and 64.7 mrem for the control locations.
The average quarterly dose for the indicator locations was 12.3 mrem, and 11.9 mrem for the control locations.
Refer to Figure 9.Page 39 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Figure 9: Average Quarterly TLD Dose W E 18 16 14 12 10 8 6 4 2 0 lhb 1---- I -I"-=-I -I -I--I- -IN -I [minimills 1111010 IEEEI EEEEEIINs11 111IEEIs I!IIIIII In in in In in In In in In Is [11 to is In in in to Is to is In IS" BW--4 M I 1111 11 of 11 11 11 11 11 11 11 11 11 of 11 11 11 V 11 of 11 11 11 I 111 11 11 of 11 11 11 11 of 11 11 11 11 11 11 11 of 11 11 11 111 11 1 N 90 f N~ M) V 0 WD I- W 0) 0 -N M~ V~0 00 8 0 0 0 0O 0 0 0 00 0~-~-~-~- --'j~' eJ N N N eJ ( N N4 N N (N N (N Year*Indicator SControl CONCLUSION Operation of the Perry Nuclear Power Plant is having no detectable radiological effect on the surrounding environment.
Page 40 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT INTER-LABORATORY CROSS-CHECK COMPARISON PROGRAM Introduction The purpose of the Inter-laboratory Cross-Check Comparison Program is to provide an independent check on the vendor laboratory's analytical procedures.
Samples with a known concentration of specific radionuclides are provided to the vendor laboratory.
The vendor laboratory measures and reports the concentration of specified radionuclides.
The known values are then compared to the vendor results. Results consistently outside established acceptance criteria indicate a need to check instruments or procedures.
Regulatory Guide 4.15 specifically required that contractor laboratories that performed environmental measurement participate in the EPA's Environmental Radioactivity Laboratory Inter-Comparison Studies Program, or an equivalent program.The EPA's program is no longer funded or offered. The reason that the EPA program was referenced in the regulatory guide is that the EPA standards were traceable to National Bureau of Standards (now known as National Institute Standard Technology).
In response to this problem, Teledyne (PNPP vendor lab) incorporated a program offered by Environmental Resource Associates (ERA Company), which covered the same analyses in the same matrix at the same frequency as the EPA program. The ERA Company has received NIST accreditation for its program, as an equivalent program. In addition to comparison cross checks performed with the ERA Company, the vendor laboratory routinely monitors the quality of their analyses by: Analyzing "spiked" samples (samples with a specific quantity of radioactive material present in them) and Participating in the Department of Energy's Mixed Analyte Performance Program (MAPEP).See Appendix A, for the vendor Inter-Laboratory Cross-Check Comparison Program Results.Page 41 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT LAND USE CENSUS Introduction Each year a Land Use Census is conducted to identify the locations of the nearest milk animal, garden (of greater than 500 square feet), and residence in each of the meteorological sectors that is over land. Information gathered during the Land Use Census is used for off-site dose assessment and to update sampling locations for the REMP. The census is conducted by traveling all roads within a five-mile radius of the plant site, and recording and mapping the location of the nearest resident, milk animal and vegetable garden. The Land Use Census was conducted on September 26th 2014. The census identified the garden, residence and milk animal locations tabulated in Tables 17, 18 and 19 and depicted in Figure 10. Note that the W, WNW, NW, NNW, N, and NNE sectors extend over Lake Erie, and are not included in the survey.Discussions and Results In general, the predominant land use within the census area continues to be rural/agricultural.
In recent years however, it has been noted that tracts of land once used for farming are now being developed as mini-industrial parks and residential housing tracts.This is reflected in the loss of available milking animals within a five mile radius of PNPP to support the REMP.Table 17 identifies the nearest residences, by sector, to the PNPP. There were no changes from last year's Land Use Census.Table 17: Nearest Residence, By Sector Sector Location Address Miles from Map Locator PNPP Number NE 4384 Lockwood 0.7 1 ENE 4602 Lockwood 1.1 2 E 2626 Antioch 1.0 3 ESE 2836 Antioch 1.1 4 SE 4495 North Ridge 1.3 5 SSE 3119 Parmly 0.9 6 S 3121 Center 0.9 7 SSW 3850 Clark 0.9 8 SW 2997 Perry Park 1.2 9 WSW 3460 Parmly 1.0 10 Page 42 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Table 18 identifies the nearest milking animal by sector, to the PNPP. There were no changes from last year's LUC.Table 18: Nearest Milk Animal, By Sector Sector Location Address Miles from Map Locator PNPP Number E 2591 McMackin Rd. 2.6 21 Table 19 lists the nearest gardens occupying at least 500 square feet identified during the Land Use Census. The only change was correcting the address listed for the garden in the SW sector.Table 19: Nearest Garden, By Sector Sector Location Address Miles from Map Locator PNPP Number NE 2340 Hemlock 0.9 11 ENE 4630 Lockwood 1.1 12 E 2626 Antioch 1.0 3 ESE 2836 Antioch 1.1 4 SE 4671 North Ridge 1.3 15 SSE 4225 Red Mill Valley 1.1 16 S 3121 Center Rd. 0.9 7 SSW 3431 Perry Park 1.9 17 SW 3021 Perry Park 1.3 13 WSW 3460 Parmly 1.0 14 Page 43 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Figure 10: Land Use Census Map I o~m~ -M IIgMbIU Page 44 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT CLAM/MUSSEL MONITORING INTRODUCTION Sampling for macro-invertebrates (clams and mussels) has been conducted in Lake Erie in the vicinity of PNPP, since 1971. The clam/mussel program currently focuses on two species: Corbicula fluminea (Asiatic clam) and Dreissena polymorpha (zebra mussel).CORBICULA PROGRAM Monitoring specifically for Corbicula was initiated in response to a NRC bulletin and concerns of the Atomic Safety and Licensing Board. The monitoring was done as part of the Environmental Protection Plan (Operating License, Appendix B). The program consists of visually inspecting the raw water systems, when they are opened for maintenance.
The purpose of this program is to detect Corbicula, should it appear at PNPP.Monitoring Samples were collected from the Service Water (SW) and Emergency Service Water (ESW)pump houses at PNPP and examined for shells and fragments.
Samples were either collected by hand scoop or scraper. In addition to sample collections, plant components that use raw water are inspected when opened for maintenance or repair. Sample collection/inspection dates are listed in Table 20.'able 20: 2014 Corbicula Monitoring Date Sample Location 1/30/2014 1 P54D0906 (Fire Protection)
-Strainer for foam system water supply inlet 1/30/2014 1P54D0920 (Fire Protection) 4/23/2014 0P43B0001C (Nuclear Closed Cooling) -Heat Exchanger 5/02/2014 (Fire Protection)
-Hydrant No. 17 5/08/2014 1N34BOOO1B (Lube Oil)6/06/2014 (Fire Protection)
-Fire Hydrant and Hose House 6/18/2014 1 P54D1 240 Fire Protection)
-Aux. Bldg. Plenum Deluge Header Strainer 6/18/2014 1 P54D1240 (Fire Protection)
-Aux. Bldg. Plenum Deluge Header Strainer 6/26/2014 OP54D0519 Fire Protection) 6/27/2014 1N34BOO01A (Lube oil)8/23/2014 N43 Turbine Building Lube Oil 'Cooler "A" 10/20/2014 (Fire Protection)
-Hydrant No. 37 10/30/2014 (Fire Protection)
-OP54F0756 Hose Reel Page 45 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Conclusions The sample collected in June, 1987, was the only indication of Corbicula in the vicinity of PNPP. Although the presence of Corbicula was detected at the Eastlake Power Plant, it has not been demonstrated that their presence has created any operational problems there, or at PNPP. As in the past, the 2014 monitoring program did not identify Corbicula in any sample collected.
DREISSENA PROGRAM Dreissena or zebra mussels were first discovered at PNPP in September, 1988. The initial collection of nineteen (19) mussels was made as part of the Corbicula monitoring program.The Dreissena monitoring program began in 1989, with monitoring and testing. The current control program was designed and implemented in 1990.Monitoring In addition to visually inspecting the plant's raw water systems when they are opened for maintenance or repair, monitoring methods include the use of commercial divers and side-stream monitors.
Commercial divers monitor mussel infestation during the inspection of forebays, basins, and the intake and discharge structures.
Divers have also been used to take underwater videotapes of the water basins and intake tunnel. Side-stream monitors are flow-through containers that receive water diverted from plant systems and are set up at two in-plant locations during the mussel season.Treatment Chemicals used for mussel control included sodium hypochlorite and a commercial molluscicide.
The chlorine is intermittently injected into the plant service water, emergency service water, and circulating water systems by metering sodium hypochlorite into each system's influent.
Sodium bisulfite is added at the plant discharge structure for dechlorination prior to return into Lake Erie.The Ohio Environmental Protection Agency (OEPA) has approved the use of a commercial molluscicide.
The chemical selected for use at the PNPP was alkyl-dimethyl-benzyl-ammonium chloride.
Treatment was applied once in 2014. The active ingredients were detoxified by adsorption using bentonite clay, prior to discharge into Lake Erie.Results The effectiveness of the intermittent biocide treatment has been determined in several ways.First, visual inspections of raw water system components are conducted when systems are open during maintenance or repair. In addition, settlement monitors were inspected for new settlement.
No live settlement has been found in any plant component to date.The effectiveness of the application of the commercial molluscicide was measured by observing mortality of mussels placed in a flow-through container placed in plant service water and subjected to the chemical treatment.
The observed mortality rate utilizing the flow-through container was 100%Page 46 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT To date, PNPP has had no significant problems related to zebra mussels.Conclusions PNPP has taken the approach that the best method for avoiding problems with zebra mussels is preventive treatment of plant water systems. The current program of monitoring and chemical treatment will be continued to minimize the possibility that PNPP will experience future problems due to zebra mussels.HERBICIDE APPLICATIONS Herbicides are used sparingly on the PNPP site. A request must be made to and approved by the PNPP Chemistry Unit prior to spraying to ensure that only approved chemicals are used, and only in approved areas.In 2014, four (4) general and four (4) specific herbicide requests were initiated for chemical applications.
Each application was in compliance with the Ohio Environmental Protection Agency's rules and regulations.
There were no adverse environmental impacts observed during weekly site environmental inspections as a result of these applications.
The herbicides used were Round-Up Promax, Brushmaster and a Broadleaf Weed Spray. For each application, the type of weed to be treated dictated the herbicide and concentration to be used. Table 21 provides detailed documentation for each application.
The quantity represents the amount of herbicide applied, prior to any dilution.Table 21: 2014 Herbicide Applications Chemical Amount (gal)Round-Up Promax 15.6 Brushmaster 51.5 Broadleaf Weed Spray 1.2 Page 47 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT SPECIAL REPORTS NPDES Permit The Ohio Environmental Protection Agency (OEPA) issues the National Pollutant Discharge Elimination System (NPDES) permit. It establishes monitoring requirements and limits for discharges from the PNPP. It also specifies the locations from which the plant is allowed to discharge.
There were no environmental violations in 2014.ENVIRONMENTAL PROTECTION PLAN The Environmental Protection Plan (EPP), which is Appendix B of the PNPP Operating License, requires a non-radiological environmental monitoring and reporting program be established at the PNPP.An Environmental Evaluation was performed, along with a Design Interface Evaluation on the Minor Stream Modification.
The Engineering Change Package (ECP) 13-0802 provides for modifications required to restore Minor Stream design basis capabilities.
UN-REVIEWED ENVIRONMENTAL QUESTIONS All proposed changes to the PNPP design or operation, as well as tests or experiments, must be evaluated for potential environmental impacts in accordance with the EPP and administrative quality assurance procedures.
Page 48 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Appendix A Inter-Laboratory Cross Check Comparison Program Results
@AT' Environmental, Inc.Midwest Laboratory 700 Landwehl' Roed -Northbrook.
XL 60062-2310 phone (847) 564-0700 .fax J847) 564-4517 APPENDIX A INTERLABORATORY COMPARISON PROGRAM RESULTS NOTE: Environmental Inc., Midwest Laboratory participates in intercomparison studies administered by Environmental Resources Associates, and serves as a replacement for studies conducted previously by the U.S. EPA Environmental Monitoring Systems Laboratory, Las Vegas, Nevada. Results are reported in Appendix A. TLD Intercomparison results, in-house spikes, blanks, duplicates and mixed analyte performance evaluation program results are also reported.
Appendix A is updated four times a year; the complete Appendix is included in March, June, September and December monthly progress reports only.January, 2014 through December, 2014 Appendix A Interlaboratory Comparison Program Results Environmental, Inc., Midwest Laboratory has participated in interlaboratory comparison (crosscheck) programs since the formulation of it's quality control program in December 1971. These programs are operated by agencies which supply environmental type samples containing concentrations of radionuclides known to the issuing agency but not to participant laboratories.
The purpose of such a program is to provide an independent check on a laboratory's analytical procedures and to alert it of any possible problems.Participant laboratories measure the concentration of specified radionuclides and report them to the issuing agency. Several months later, the agency reports the known values to the participant laboratories and specifies control limits. Results consistently higher or lower than the known values or outside the control limits indicate a need to check the instruments or procedures used.Results in Table A-1 were obtained through participation in the environmental sample crosscheck program administered by Environmental Resources Associates, serving as a replacement for studies conducted previously by the U.S. EPA Environmental Monitoring Systems Laboratory, Las Vegas, Nevada.Table A-2 lists results for thermoluminescent dosimeters (TLDs), via International Intercomparison of Environmental Dosimeters, when available, and internal laboratory testing.Table A-3 lists results of the analyses on in-house "spiked" samples for the past twelve months. All samples are prepared using NIST traceable sources. Data for previous years available upon request.Table A-4 lists results of the analyses on in-house "blank" samples for the past twelve months. Data for previous years available upon request.Table A-5 lists REMP specific analytical results from the in-house "duplicate" program for the past twelve months. Acceptance is based on the difference of the results being less than the sum of the errors.Complete analytical data for duplicate analyses is available upon request.The results in Table A-6 were obtained through participation in the Mixed Analyte Performance Evaluation Program.Results in Table A-7 were obtained through participation in the environmental sample crosscheck program administered by Environmental Resources Associates, serving as a replacement for studies conducted previously by the Environmental Measurement Laboratory Quality Assessment Program (EML).Attachment A lists the laboratory precision at the 1 sigma level for various analyses.
The acceptance criteria in Table A-3 is set at +/- 2 sigma.Out-of-limit results are explained directly below the result.Al Attachment A ACCEPTANCE CRITERIA FOR "SPIKED" SAMPLES LABORATORY PRECISION:
ONE STANDARD DEVIATION VALUES FOR VARIOUS ANALYSESa One standard deviation Analysis Level for single determination Gamma Emitters 5 to 100 pCi/liter or kg 5.0 pCi/liter> 100 pCi/liter or kg 5% of known value Strontium-89b 5 to 50 pCi/liter or kg 5.0 pCi/liter> 50 pCi/liter or kg 10% of known value Strontium-90b 2 to 30 pCi/liter or kg 5.0 pCi/liter> 30 pCi/liter or kg 10% of known value Potassium-40
ý 0.1 g/liter or kg 5% of known value Gross alpha < 20 pCi/liter 5.0 pCi/liter> 20 pCi/liter 25% of known value Gross beta < 100 pCi/liter 5.0 pCi/liter> 100 pCi/liter 5% of known value Tritium < 4,000 pCi/liter
+/- lo =169.85 x (known)'0 9 3 3> 4,000 pCi/liter 10% of known value Radium-226,-228 a 0.1 pCi/liter 15% of known value Plutonium
? 0.1 pCi/liter, gram, or sample 10% of known value Iodine-131, S 55 pCi/liter 6 pCi/liter Iodine-129b
> 55 pCi/liter 10% of known value Uranium-238, :s 35 pCi/liter 6 pCi/liter Nickel-63b
> 35 pCi/liter 15% of known value Technetlum-99b Iron-55b 50 to 100 pCi/liter 10 pCi/liter> 100 pCi/liter 10% of known value Other Analyses b 20% of known value From EPA publication, "Environmental Radioactivity Laboratory Intercomparison Studies Program, Fiscal Year, 1981-1982, EPA-600/4-81-004.
b Laboratory limit.A2 TABLE A-1. Interlaboratory Comparison Crosscheck program, Environmental Resource Associates (ERA)a.Concentration (pCi/L)Lab Code Date Analysis Laboratory ERA Control Result b Result c Limits Acceptance ERW-1384 ERW-1384 ERW-1385 ERW-1 385 ERW-1385 ERW-1385 ERW-1 385 ERW-1388 ERW-1388 ERW-1391 ERW-1394 ERW-1394 ERW-1394 ERW-1397 ERW-5382 ERW-5382 ERW-5385 ERW-5385 ERW-5385 ERW-5385 ERW-5385 ERW-5388 ERW-5388 ERW-5392 ERW-5394 ERW-5394 ERW-5394 ERW-5397 4/7/2014 4/7/2014 4/7/2014 4/7/2014 4/7/2014 4/7/2014 4/7/2014 4/7/2014 4/7/2014 4/7/2014 4/7/2014 4/7/2014 4/7/2014 4/7/2014 10/6/2014 10/6/2014 10/6/2014 10/6/2014 10/6/2014 10/6/2014 10/6/2014 10/6/2014 10/6/2014 10/6/2014 10/6/2014 10/6/2014 10/6/2014 10/6/2014 Sr-89 Sr-90 Ba-133 Co-60 Cs- 134 Cs-137 Zn-65 Gr. Alpha Gr. Beta 1-131 Ra-226 Ra-228 Uranium H-3 Sr-89 Sr-90 Ba-133 Cs-134 Cs-1 37 Co-60 Zn-65 Gr. Alpha G. Beta 1-131 Ra-226 Ra-228 Uranium H-3 40.29 +/- 5.76 24.08 +/- 2.35 78.23 +/- 3.93 62.75 +/- 3.53 44.97 +/- 3.99 88.54 +/- 4.93 249.1 +/- 10.4 56.70 +/- 2.47 32.10 +/- 1.20 25.52 +/- 1.12 12.30 +/- 0.61 5.08 +/- 1.16 10.76 +/- 0.74 8982 +/- 279 29.40 +/- 5.32 19.19 +/- 1.85 43.54 +/- 4.54 81.95 +/- 7.49 95.76 +/- 5.50 90.25 +/- 2.77 327.4 +/- 23.3 30.88 +/- 8.05 20.47 +/- 4.75 19.58 +/- 2.35 15.10 +/- 1.81 4.42 +/- 0.86 5.51 +/- 0.37 6876 +/- 383 36.70 26.50 87.90 64.20 44.30 89.10 235.0 61.00 33.00 25.70 12.40 4.26 10.20 8770 31.40 21.80 49.10 89.80 98.80 92.10 310.0 37.60 27.40 20.30 14.70 4.31 5.80 6880 27.50 +/- 43.60 19.20 +/- 30.90 74.00 +/- 96.70 57.80 +/- 73.10 35.50 +/- 48.70 80.20 +/- 101.00 212.0 -275.0 31.90 +/- 75.80 21.40 +/- 40.70 21.30 +/- 30.30 9.26 +/- 14.30 2.46 +/- 5.86 7.95 +/- 11.80 7610 -9650 22.80 +/- 38.10 15.60 +/- 25.70 40.30 +/- 54.50 73.70 +/- 98.80 88.90 +/- 111.00 82.90 +/- 104.00 279.0 -362.0 19.40 +/- 46.10 17.30 +/- 35.30 16.80 +/- 24.40 11.00 +/- 16.90 2.50 +/- 5.92 4.34 +/- 6.96 5940 -7570 Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass 8 Results obtained by Environmental, Inc., Midwest Laboratory as a participant In the crosscheck program for proficiency testing in dunking water conducted by Environmental Resources Associates (ERA).b Unless otherwise indicated, the laboratory result is given as the mean +/- standard deviation for three determinations.
c Results are presented as the known values, expected laboratory precision (1 sigma, I determination) and control limits as provided by ERA.Al-I TABLE A-2. Thermoluminescent Dosimetry, (TLD, CaSO 4: Dy Cards).mR Lab Code Date Known Lab Result Control Description Value +/- 2 sigma Limits Acceptance Environmental, Inc.2014-1 2014-1 2014-1 2014-1 2014-1 2014-1 2014-1 2014-1 2014-1 2014-1 2014-1 2014-1 2014-1 5/15/2014 5/15/2014 5/15/2014 5/15/2014 5/15/2014 5/15/2014 5/15/2014 5/15/2014 5/15/2014 5/15/2014 5/15/2014 5/15/2014 5/15/2014 50 cm.60 cm.70 cm.75 cm.80 cm.90 cm.100 cm.110 cm.120 cm.135 cm.150 cm.165 cm.180 cm.26.83 18.63 13.69 11.93 10.48 8.28 6.71 5.54 4.66 3.68 2.98 2.46 2.07 34.43 +/- 3.76 22.20 +/- 1.16 14.74 +/- 0.80 12.68 +/- 1.05 11.81 +/- 0.91 7.72 +/- 0.71 6.46 +/- 0.71 5.25 t 1.03 4.76 +/- 0.48 2.87 +/- 0.46 2.30 +/- 0.15 2.09 +/- 0.28 1.75 +/- 0.21 18.78 -34.88 13.04 -24.22 9.58 -17.80 8.35 -15.51 7.34 -13.62 5.80 -10.76 4.70 -8.72 3.88 -7.20 3.26 -6.06 2.58 -4.78 2.09 -3.87 1.72 -3.20 1.45 -2.69 Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Environmental, Inc.2014-2 2014-2 2014-2 2014-2 2014-2 2014-2 2014-2 2014-2 2014-2 2014-2 2014-2 2014-2 2014-2 12/9/2014 12/9/2014 12/9/2014 12/9/2014 12/9/2014 12/9/2014 12/9/2014 12/9/2014 12/9/2014 12/9/2014 12/9/2014 12/9/2014 12/9/2014 30 cm.30 cm.60 cm.60 cm.120 cm.120 cm.150 cm.150 cm.150 cm.180 cm.180 cm.180 cm.180 cm.77.04 77.04 19.26 19.26 4.82 4.82 3.08 3.08 3.08 2.14 2.14 2.14 2.14 84.03 +/- 8.47 83.74 +/- 12.02 20.39 +/- 2.37 20.33 +/- 1.19 5.15 +/- 0.20 5.20 +/- 0.45 3.84 +/- 0.61 3.17 +/- 0.38 3.31 +/- 0.32 2.27 +/- 0.51 2.23 +/- 0.12 2.74 +/- 0.48 1.97 +/- 0.41 53.90 -100.20 53.90 -100.20 13.50 -25.00 13.50 -25.00 3.40 -6.30 3.40 -6.30 2.20 -4.00 2.20 -4.00 2.00 -4.00 1.50 -2.80 1.50 -2.80 1.50 -2.80 1.50 -2.80 Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass A2-1 TABLE A-3. In-House "Spiked" Samples Concentration (pCi/L)a Lab Code b Date Analysis Laboratory results Known Control 2s, n=1 c Activity Limits" Acceptance SPW-1011 SPAP-103 SPAP-105 SPAP-105 SPW-107 SPW-129 SPW-129 SPW-129 SPW-130 SPW-133 SPMI-135 SPMI-135 W-12014 W-12014 SPW-297 SPW-657 SPW-1 127 SPW-1917 SPW-1786 SPW-2168 SPW-2168 SPW-2168 SPW-2168 SPMI-2170 SPMI-2170 SPMI-2170 SPMI-2170 SPW-2792 SPW-2796 WW-2836 WW-2836 WW-2836 1/13/2014 111312014 1/13/2014 1/13/2014 1/13/2014 1/15/2014 1/15/2014 1/15/2014 1/15/2014 1/15/2014 1/15/2014 1/15/2014 1/20/2014 1/20/2014 1/29/2014 2/25/2014 3/26/2014 3/28/2014 4/25/2014 5/21/2014 5/21/2014 5/21/2014 5/21/2014 5/21/2014 5/21/2014 5/21/2014 5/21/2014 6/18/2014 6/18/2014 6/30/2014 6/30/2014 6/30/2014 Ra-228 Gr. Beta Cs-134 Cs-137 H-3 Cs-134 Cs-137 Sr-90 Ni-63 C-14 Cs-134 Cs-137 Gr. Alpha Gr. Beta Tc-99 Ra-226 U-238 Pu-238 Tc-99 Cs-134 Cs-137 Sr-89 Sr-90 Cs-134 Cs-137 Sr-89 Sr-90 U-238 C-14 Co-60 Cs-137 H-3 35.47 +/- 2.55 43.91 +/- 0.34 2.46 t 0.67 102.4 +/- 2.7 62,380 +/- 707 69.90 +/- 3.71 84.36 +/- 7.06 39.48 +/- 1.52 255.8 +/- 3.8 3153 +/- 15 76.80 +/- 4.04 80.44 +/- 6.63 19.69 +/- 0.41 30.35 +/- 0.33 104.2 +/- 1.7 15.84 +/- 0.45 43.28 +/- 2.56 27.37 +/- 2.13 531.1 +/- 8.7 70.90 +/- 5.81 79.72 +/- 6.49 83.35 +/- 5.05 33.37 +/- 1.52 64.15 +/- 4.93 76.21 +/- 6.91 65.82 +/- 4.89 40.90 +/- 1.59 44.80 +/- 1.54 3495 +/- 9 131.8 +/- 6.9 143.8 +/- 9.1 6220 +/- 238 30.85 44.82 2.82 99.9 62,246 78.00 75.77 39.20 204.0 4737 78.00 75.80 20.00 30.90 107.8 16.70 41.72 23.80 539.15 69.50 75.17 72.85 38.87 69.50 75.17 72.85 38.87 41.70 4,737 140.90 145.60 6,361 21.60 -40.11 26.89 -62.75 1.69 -3.95 89.9 -109.9 49,797 -74,695 68.00 -88.00 65.77 -85.77 31.36 -47.04 142.8 -265.2 2842 -6632 68.00 -88.00 65.80 -85.80 10.00 -30.00 20.90 -40.90 75.5 -140.2 11.69 -21.71 29.20 -54.24 14.28 -33.32 377.41 -700.90 59.50 -79.50 65.17 -85.17 58.28 -87.42 31.10 -46.64 59.50 -79.50 65.17 -85.17 58.28 -87.42 31.10 -46.64 29.19 -54.21 2,842 -'6632 126.81 -154.99 131.04 -160.16 5,089 -7633 Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass A3-1 TABLE A-3. In-House "Spiked" Samples Concentration (pCi/L)e Lab Code b Date Analysis Laboratory results Known Control 2s, n=1 ' Activity Limits d Acceptance SPW-3486 SPW-080714 SPW-080714 SPW-081214 SPW-4093 SPW-4093 SPW-4093 SPMI-4095 SPMI-4095 SPW-4104 SPW-4106 SPW-4108 SPW-4108 SPAP-4110 SPF-4112 SPF-4112 SPF-4112 SPW-081414 W081614 W082614 SPW-090414 SPW-090414 7/17/2014 8/7/2014 81712014 8/12/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8113/2014 8/13/2014 8/14/2014 8/16/2014 8/26/2014 9/4/2014 9/4/2014 9/29/2014 10/7/2014 10/7/2014 11/10/2014 11/10/2014 11/25/2014 12/8/2014 12/8/2014 Fe-55 Gr. Alpha Gr. Beta Pu-238 1-131(G)Sr-90 Sr-89 1-131(G)1-131 Ni-63 H-3 Cs-134 Cs- 137 Gr. Beta 1-131 Cs-134 Cs-137 H-3 Ra-226 Ra-228 Gr. Alpha Gr. Beta Ra-228 Gr. Alpha Gr. Beta Gr. Alpha Gr. Beta Ra-226 Gr. Alpha Gr. Beta 2211 +/- 72 18.42 +/- 0.40 31.70 +/- 0.40 22.59 +/- 2.15 59.95 +/- 6.17 39.46 +/- 1.55 105.5 +/- 4.9 59.92 +/- 6.17 60.05 +/- 0.72 200.1 +/- 3.4 59,597 +/- 695 2.45 +/- 0.81 90.20 +/- 3.74 43.65 +/- 0.11 2.64 +/- 0.38 0.91 +/- 0.03 2.61 +/- 0.06 14,663 +/- 788 14.30 +/- 0.37 27.18 +/- 2.13 17.85 +/- 0.39 30.03 +/- 0.33 32.93 +/- 2.38 18.56 +/- 0.40 27.71 +/- 0.32 17.84 +/- 0.38 30.12 +/- 0.33 16.63 +/- 0.41 19.29 +/- 0.41 27.93 +/- 0.32 217.53 +/- 3.25 2319 20.10 32.40 22.70 59.62 38.65 115.0 59.62 59.62 203.2 60,261 2.32 98.56 44.19 2.86 1.03 2.39 17,700 16.70 30.49 20.10 30.90 31.94 20.10 30.90 20.10 30.90 16.70 20.10 30.90 1855 -2783 10.05 -30.15 22.40 -42.40 18.16- 27.24 49.62 -69.62 28.65 -48.65 92.0 -149.5 49.62 -69.62 47.70 -71.54 142.2 -264.1 48209 -72313 0.00 -12.32 88.56 -108.56 34.19 -54.19 0.00 -12.86 0.00 -11.03 0.00 -12.39 14160 -21240 11.69 -21.71 20.49 -40.49 10.05 -30.15 20.90 -40.90 21.94 -41.94 10.05 -30.15 20.90 -40.90 10.05 -30.15 20.90 -40.90 11.69 -21.71 10.05 -30.15 20.90 -40.90 Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass SPW-5124 W100714 W100714 Wl11014 W111014 W112514 W120814 W120814 SPW-7149 12/26/2014 Ni-63 203.10 142.17 -264.03 8 Liquid sample results are reported in pCi/Liter, air filters( pCi/m3), charcoal (pCI/charcoal canister), and solid samples (pCi/kg).b Laboratory codes : W (Water), MI (milk), AP (air filter), SO (soil), VE (vegetation), CH (charcoal canister), F (fish), U (urine).c Results are based on single determinations.
d Control limits are established from the precision values listed in Attachment A of this report, adjusted to +/- 2s.NOTE: For fish, Jello is used for the spike matrix. For vegetation, cabbage Is used for the spike matrix.A3-2 TABLE A-4. In-House "Blank" Samples Concentration (pCi/L)a Lab Code Sample Date Analysisb Laboratory results (4.66n) Acceptance Type LLD Activityc Criteria (4.66 ()SPW-1001 SPAP-102 SPAP-104 SPAP-104 SPW-106 SPW-128 SPW-128 SPW-128 SPW-130 SPW-133 SPMI-134 SPMI-134 W-12014 W-12014 SPW-297 SPW-656 SPW-1 126 SPW-1 127 SPW-1 127 SPW-1917 SPW-1785 SPW-1831 SPW-2167 SPW-2167 SPW-2167 SPW-2167 SPW-2167 SPMI-2169 SPMI-2169 SPMI-2169 SPMI-2169 SPMI-2169 SPW-2793 Water Air Particulate Air Particulate Air Particulate Water Water Water Water Water Water Milk Milk Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Milk Milk Milk Milk Milk Water 1/13/2014 1/13/2014 1/13/2014 1/13/2014 1/13/2014 1/15/2014 1/15/2014 1/15/2014 1/15/2014 1/15/2014 1/15/2014 1/15/2014 1/20/2014 1/20/2014 1/29/2014 2/25/2014 3/26/2014 3/26/2014 3/26/2014 3/28/2014 4/25/2014 4/30/2014 5/21/2014 5/21/2014 5/21/2014 5/21/2014 5/21/2014 5/21/2014 5/21/2014.5/21/2014 5/21/2014 5/21/2014 6/18/2014 Ra-228 Gr. Beta Cs- 134 Cs-137 H-3 Cs- 134 Cs- 137 Sr-90 Ni-63 C-14 Cs- 134 Cs-137 Gr. Alpha Gr. Beta Tc-99 Ra-226 U-238 U-233/234 U-238 Pu-238 Tc-99 1-131 Cs- 134 Cs-137 1-131(G)Sr-89 Sr-90 Cs-134 Cs-137 1-131(G)Sr-89 Sr-90 U-238 0.74 0.003 0.006 0.004 151.0 2.85 2.52 0.61 10.85 13.51 4.43 1.92 0.48 0.78 5.63 0.03 0.13 0.13 0.00 0.02 5.61 0.21 2.29 2.46 2.77 0.81 0.52 4.45 3.91 4.31 0.98 0.61 0.08 0.39 +/- 0.39 0.015 +/- 0.003 0.005 +/- 0.005-0.002 +/- 0.005 115.0 +/- 97.0 0.59 +/- 1.46 0.68 +/- 1.64 0.74 +/- 0.36 1.57 +/- 6.60 3.10 +/- 8.27 0.14 +/- 2.46-2.07 +/- 2.48-0.31 +/- 0.31-0.24 +/- 0.54-4.42 +/- 3.34 0.01 +/- 0.02 0.08 +/- 0.12 0.11 +/- 0.13 0.08 +/- 0.12 0.01 +/- 0.01-4.33 +/- 3.33 0.07 +/- 0.12-0.79 +/- 1.35 0.36 +/- 1.48 0.25 +/- 1.53 0.01 +/- 0.62 0.03 +/- 0.24-0.55 +/- 2.39-0.52 +/- 2.60 2.57 +/- 2.21-0.02 +/- 0.83 0.35 +/- 0.32 0.02 +/- 0.06 2 0.01 0.05 0.05 200 10 10 1 20 200 10 10 2 4 10 1 1 1 1 1 10 0.5 10 10 20 5 1 10 10 20 5 1 1 A4-1 TABLE A-4. In-House "Blank" Samples Concentration (pCi/L)r Lab Code Sample Date Analysisb Laboratory results (4.66r3) Acceptance Type LLD Activityc Criteria (4.66 a)SPW-3485 SPW-4092 SPW-4092 SPW-4092 SPW-4092 SPW-4092 SPMI-4094 SPMI-4094 SPMI-4094 SPMI-4094 SPMI-4094 SPMI-4094 SPW-4103 SPW-4105 SPW-4107 SPW-4107 SPW-4107 SPAP-4109 SPF-4111 SPF-41 11 SPF-4111 W-081614 W-082614 W-092314 W-5123 W-100714 W-100714 W-111014 W-111014 W-112514 W-120814 W-120814 SPW-7148 Water Water Water Water Water Water Milk Milk Milk Milk Milk Milk Water Water Water Water Water Air Particulate Fish Fish Fish Water Water Water Water Water Water Water Water Water Water Water Water 7/17/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/1312014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/13/2014 8/16/2014 8/16/2014 9/23/2014 9/29/2014 10/7/2014 10/7/2014 11/10/2014 11/10/2014 11/25/2014 12/8/2014 12/8/2014 12/26/2014 Fe-55 1-131(G)Cs-134 Cs-137 Sr-89 Sr-90 1-131 1-131(G)Cs- 134 Cs- 137 Sr-89 Sr-90 Ni-63 H-3 1-131(G)Cs- 134 Cs-137 Gr. Beta Cs-134 Cs-137 Co-60 Ra-226 Ra-228 Ra-226 Ra-228 Gr. Alpha Gr. Beta Gr. Alpha Gr. Beta Ra-226 Gr. Alpha Gr. Beta Ni-63 597.6 3.59 3.71 2.71 0.89 0.52 0.35 4.50 4.30 3.45 0.80 0.47 0.12 138.1 3.21 2.72 2.56 0.004 0.01 0.01 0.01 0.04 0.62 0.02 0.70 0.39 0.76 0.39 0.75 0.05 0.42 0.74 10.80 10.3 +/- 363.3 0.91 +/- 1.95-0.31 +/- 1.77-2.20 +/- 1.98 0.11 +/- 0.63-0.05 +/- 0.23 0.03 +/- 0.20-0.41 +/- 2.44-0.84 +/- 2.02 0.96 +/- 2.51-0.19 +/- 0.79 0.71 +/- 0.30 0.02 +/- 0.07 104.1 +/- 78.1-3.68 +/- 1.33-0.62 +/- 1.49 0.75 +/- 1.62-0.003 +/- 0.00 0.00 +/- 0.01-0.01 +/- 0.01 0.00 +/- 0.01 0.05 +/- 0.03 0.29 +/- 0.40 0.04 +/- 0.02 0.43 +/- 0.38 0.04 +/- 0.28-0.06 +/- 0.53 0.01 +/- 0.28-0.25 +/- 0.52 0.02 +/- 0.03 0.04 +/- 0.30-0.42 +/- 0.51-1.80 +/- 6.50 1000 20 10 10 5 1 0.5 20 10 10 5 1 20 200 20 10 10 0.01 100 100 100 1 2 1 2 2 4 2 4 2 2 4 20 a Liquid sample results are reported in pCI/Liter, air filters( pCi/m 3), charcoal (pCi/charcoal canister), and solid samples (pCi/kg).b 1-131(G);
iodine-131 as analyzed by gamma spectroscopy.
c Activity reported is a net activity result.A4-2 TABLE A-5. In-House "Duplicate" Samples Concentration (pCi/L)a Averaged Lab Code Date Analysis First Result Second Result Result Acceptance AP-7829, 7830 AP-7913, 7914 AP-7871, 7872 S-43, 44 SG-64, 65 SG-64. 65 SG-64, 65 S-136, 137 S-136, 137 WW-220.221 WW-262, 263 WW-346, 347 SWU-367, 368 F-409, 410 F-409, 410 AP-7829, 7830 AP-7913, 7914 AP-7871, 7872 S-43, 44 SG-64, 65 SG-64, 65 SG-64, 65 S-136, 137 S-136, 137 WW-220, 221 WW-262, 263 WW-346, 347 SWU-367, 368 F-409, 410 F-409, 410 WW-491,492 WW-575, 576 W-617, 618 SWU-743, 744 S-700, 701 S-806, 807 SG-928, 929 SG-928, 929 SG-928, 929 SG-928, 929 SG-928, 929 SG-928, 929 SG-928, 929 1/2/2014 1/2/2014 1/3/2014 1/9/2014 1/9/2014 1/9/2014 1/9/2014 1/13/2014 1/13/2014 1/13/2014 1/21/2014 1/24/2014 1/29/2014 2/2/2014 2/2/2014 1/2/2014 1/2/2014 1/3/2014 1/9/2014 1/9/2014 1/9/2014 1/9/2014 1/13/2014 1/13/2014 1/13/2014 1/21/2014 1/24/2014 1/29/2014 2/2/2014 2/2/2014 2/6/2014 2/13/2014 2/14/2014 2/25/2014 2/26/2014 3/4/2014 3/11/2014 3/11/2014 3/11/2014 3/11/2014 3/11/2014 3/11/2014 3/11/2014 Be-7 Be-7 Be-7 K-40 Gr. Alpha Ra-226 Ra-228 Be-7 K-40 H-3 H-3 H-3 Gr. Beta Cs-137 Gr. Beta Be-7 Be-7 Be-7 K-40 Gr. Alpha Ra-226 Ra-228 Be-7 K-40 H-3 H-3 H-3 Gr. Beta Cs-137 Gr. Beta H-3 H-3 H-3 Gr. Beta K-40 K-40 Ac-228 Bi-214 K-40 Pb-212 Pb-214 Th-228 TI-208 0.08 +/- 0.02 0.07 +/- 0.01 0.05 +/- 0.02 19.28 +/- 0.57 686.08 +/- 69.97 97.30 +/- 9.78 91.90 +/- 9.30 14.90 +/- 0.39 3.29 +/- 0.36 231.85 +/- 80.45 294.80 + 89.80 934.97 +/- 118.47 0.74 +/- 0.38 0.05 +/- 0.02 3.60 +/- 0.07 0.08 +/- 0.02 0.07 +/- 0.01 0.05 +/- 0.02 19.28 +/- 0.57 686.08 +/- 69.97 97.30 +/- 9.78 91.90 +/- 9.30 14.90 +/- 0.39 3.29 +/- 0.36 231.85 +/- 80.45 294.80 +/- 89.80 934.97 +/- 118.47 0.74 +/- 0.38 0.05 +/- 0.02 3.60 +/- 0.07 474.00 +/- 101.10 196.69 +/- 82.94 526.29 +/- 97.65 1.61 +/- 0.65 21.32 +/- 0.64 24.79 +/- 0.57 6.78 +/- 0.34 5.32 +/- 0.20 4.79 +/- 0.80 2.70 +/- 0.09 5.39 +/- 0.17 6.10 +/- 2.07 0.92 +/- 0.06 0.06 +/- 0.01 0.06 +/- 0.01 0.06 +/- 0.01 19.24 +/- 0.57 642.46 +/- 65.59 92.20 +/- 9.27 97.10 +/- 9.87 14.88 +/- 0.38 3.93 +/- 0.36 273.46 +/- 82.47 265.00 +/- 88.47 965.59 +/- 119.52 1.31 +/- 0.42 0.05 +/- 0.02 3.72 +/- 0.07 0.06 +/- 0.01 0.06 +/- 0.01 0.06 +/- 0.01 19.24 +/- 0.57 642.46 +/- 65.59 92.20 +/- 9.27 97.10 +/- 9.87 14.88 +/- 0.38 3.93 +/- 0.36 273.46 +/- 82.47 265.00 +/- 88.47 965.59 +/- 119.52 1.31 +/- 0.42 0.05 +/- 0.02 3.72 +/- 0.07 583.10 +/- 105.30 154.68 +/- 80.89 579.51 +/- 99.77 1.73 +/- 0.71 21.15 +/- 0.59 24.17 +/- 0.59 6.94 +/- 0.35 5.34 +/- 0.22 6.24 +/- 1.01 2.75 +/- 0.09 5.53 +/- 0.17 4.76 +/- 1.93 0.91 +/- 0.06 0.07 +/- 0.01 0.06 +/- 0.01 0.06 +/- 0.01 19.26 +/- 0.40 664.27 +/- 47.95 94.75 +/- 6.74 94.50 +/- 6.78 14.89 +/- 0.27 3.61 +/- 0.25 252.66 +/- 57.60 279.90 +/- 63.03 950.28 +/- 84.14 1.02 +/- 0.28 0.05 +/- 0.01 3.66 +/- 0.05 0.07 +/- 0.01 0.06 +/- 0.01 0.06 +/- 0.01 19.26 +/- 0.40 664.27 +/- 47.95 94.75 +/- 6.74 94.50 +/- 6.78 14.89 +/- 0.27 3.61 +/- 0.25 252.66 +/- 57.60 279.90 +/- 63.03 950.28 +/- 84.14 1.02 +/- 0.28 0.05 +/- 0.01 3.66 +/- 0.05 528.55 +/- 72.99 175.69 +/- 57.93 552.90 +/- 69.80 1.67 +/- 0.48 21.24 +/- 0.44 24.48 +/- 0.41 6.86 +/- 0.24 5.33 +/- 0.15 5.52 +/- 0.64 2.73 +/- 0.06 5.46 +/- 0.12 5.43 +/- 1.42 0.92 + 0.04 Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass A5-1 TABLE A-5. In-House "Duplicate" Samples Concentration (pCi/L)a Averaged Lab Code Date Analysis First Result Second Result Result Acceptance S-2119, 2120 S-2119, 2120 S-2119, 2120 S-2119, 2120 F-1594,1595 SO-1115,1116 SO-1115, 1116 SO-1115, 1116 SO-1115,1116 SO-1115,1116 S-1033,1034 S-1033, 1034 S-1033, 1034 S-1033, 1034 S-1033, 1034 S-1033,1034 W-1094,1095 W-1094,1095 AP-1197, 1198 AP-1698, 1699 E-1218,1219 E-1218,1219 SWU-1260,1261 AP-1615,1616 AP-1657,1658 AP-1804,1805 P-1489,1490 BS-1531,1532 S-1909, 1910 SWU-1867,11868 AP-1930,1931 SL-1888,1889 SL-1888,1889 SL-1888,1889 SL-1888,1889 SO-1972,1973 SO-1972,1973 SO-1972,1973 SO-1972,1973 W-617, 618 AP-2077, 2078 3/12/2014 3/12/2014 3/12/2014 3/12/2014 3/16/2014 3/18/2014 3/18/2014 3/18/2014 3/18/2014 3/18/2014 3/19/2014 3/19/2014 3/19/2014 3/19/2014 3/19/2014 3/19/2014 3/23/2014 3/23/2014 3/27/2014 3/31/2014 4/1/2014 4/1/2014 4/1/2014 4/1/2014 4/2/2014 4/3/2014 4/7/2014 4/16/2014 4/22/2014 4/29/2014 5/1/2014 5/1/2014 5/1/2014 5/1/2014 5/1/2014 5/1/2014 5/1/2014 5/1/2014 5/1/2014 5/8/2014 5/8/2014 Ac-228 Cs-137 K-40 Pb-214 Cs-137 Cs-137 Gr. Beta K-40 U-233/4 U-238 Ac-228 Bi-214 Cs- 137 K-40 Pb-214 TI-208 Ra-226 Ra-228 Be-7 Be-7 Gr. Beta K-40 Gr. Beta Be-7 Be-7 Be-7 H-3 K-40 K-40 Gr. Beta Be-7 Be-7 Cs-137 Gr. Beta K-40 Cs-137 Gr. Alpha Gr. Beta K-40 H-3 Be-7 0.76 +/- 0.20 0.13 +/- 0.05 17.48 +/- 1.48 0.73 +/- 0.18 0.02 +/- 0.01 0.06 +/- 0.01 23.30 +/- 2.10 12.63 +/- 0.18 0.11 +/- 0.02 0.13 +/- 0.02 0.99 +/- 0.20 1.02 +/- 0.18 0.15 +/- 0.04 15.39 +/- 1.19 1.09 +/- 0.13 0.36 +/- 0.05 0.30 +/- 0.20 1.10 +/- 0.79 0.17 +/-0.08 0.06 +/- 0.02 1.57 +/- 0.04 1.26 +/- 0.14 2.81 +/- 0.51 0.07 +/- 0.01 0.07 +/- 0.01 0.05 +/- 0.02 582.31 +/- 101.85 0.51 +/- 0.19 14.71 +/- 0.54 2.28 +/- 0.40 0.16 +/-0.09 0.80 +/- 0.04 0.01 +/- 0.00 11.57 +/- 0.72 1.04 +/- 0.05 0.12 +/- 0.03 7.51 +/- 3.24 29.89 +/- 3.25 20.45 +/- 0.85 175.13 +/- 83.82 0.23 +/- 0.11 0.73 +/- 0.21 0.11 +/-0.05 18.39 +/- 1.53 0.63 +/- 0.12 0.03 +/- 0.02 0.06 +/- 0.00 24.40 +/- 2.20 12.84 +/- 0.15 0.12 +/- 0.02 0.14 +/- 0.02 1.13 +/- 0.26 0.98 +/- 0.16 0.14 +/- 0.04 15.13 +/- 1.19 0.88 +/- 0.17 0.31 +/- 0.05 0.70 +/- 0.20 1.13 +/- 0.86 0.14 +/- 0.08 0.07 +/- 0.02 1.57 +/- 0.04 1.31 +/- 0.18 2.94 +/- 0.50 0.07 +/- 0.02 0.08 +/- 0.01 0.06 +/- 0.01 505.07 +/- 98.72 0.58 +/- 0.23 14.78 +/- 0.53 1.67 +/- 0.35 0.19 +/-0.11 0.76 +/- 0.08 0.01 +/- 0.00 12.67 +/- 0.78 1.00 +/- 0.09 0.10 +/- 0.02 9.09 +/- 3.63 31.42 +/- 3.04 20.88 +/- 0.76 177.17 +/- 83.92 0.18 +/--0.11 0.75 +/- 0.15 0.12 +/- 0.04 17.94 +/- 1.06 0.68 +/- 0.11 0.03 +/- 0.01 0.06 +/- 0.00 23.85 +/- 1.52 12.74 +/- 0.12 0.12 +/- 0.01 0.14 +/- 0.01 1.06 +/- 0.16 1.00 +/- 0.12 0.15 +/- 0.03 15.26 +/- 0.84 0.99 +/- 0.11 0.34 +/- 0.04 0.50 +/- 0.14 1.12 +/- 0.58 0.15 +/- 0.05 0.07 +/- 0.01 1.57 +/- 0.03 1.29 +/-0.11 2.88 +/- 0.36 0.07 +/- 0.01 0.07 +/- 0.01 0.06 +/- 0.01 543.69 +/- 70.92 0.54 +/- 0.15 14.75 +/-0.38 1.98 +/- 0.27 0.17 +/- 0.07 0.78 +/- 0.05 0.01 +/- 0.00 12.12 +/- 0.53 1.02 +/- 0.05 0.11 +/- 0.02 8.30 +/- 2.43 30.66 +/- 2.23 20.66 +/- 0.57 176.15 +/- 59.31 0.20 +/- 0.08 Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass A5-2 TABLE A-5. In-House "Duplicate" Samples Concentration (pCi/L)a Averaged Lab Code Date Analysis First Result Second Result Result Acceptance S-2205,2206 S-2205, 2206 VE-2184, 2185 VE-2184, 2185 DW-50102, 50103 DW-50102, 50103 SW-2226, 2227 DW-50087, 50088 DW-50090, 50091 DW-50090, 50091 DW-50098, 50099 AP-2289, 2290 PM-3174, 3175 G-2415, 2416 G-2415, 2416 G-2415, 2416 WW-2541, 2542 SW-2817,2818 SS-2943,2944 S-3048,3049 SWT-3216, 3217 AP-3699,3700 S-3300, 3301 S-3300, 3301 S-3300,3301 VE-3237,3238 CF-3384,3385 S-3447,3448 WW-3573,3574 VE-3594,3595 WW-3762,3763 SWT-3867, 3868 S-3804,3805 S-3804,3805 LW-3931, 3932 5/15/2014 5/15/2014 5/19/2014 5/19/2014 5/20/2014 5/20/2014 5/21/2014 5/21/2014 5/21/2014 5/21/2014 5121/2014 5/22/2014 5/28/2014 6/2/2014 6/2/2014 6/2/2014 6/4/2014 6/16/2014 6/24/2014 6/27/2014 7/1/2014 7/3/2014 7/8/2014 7/8/2014 7/8/2014 7/8/2014 7/14/2014 7/16/2014 7/18/2014 7/22/2014 7/25/2014 7/29/2014 7/30/2014 7/30/2014 7/31/2014 Be-7 K-40 Be-7 K-40 Ra-226 Ra-228 H-3 Gr. Alpha Ra-226 Ra-228 Gr. Alpha Be-7 K-40 Be-7 Gr. Beta K-40 H-3 H-3 K-40 K-40 Gr. Beta Be-7 K-40 Ac-228 Ra-226 K-40 K-40 K-40 H-3 K-40 H-3 Gr. Beta Ac-228 Pb-214 Gr. Beta 0.50 +/-0.19 33.60 +/- 0.79 0.62 +/- 0.18 5.30 +/- 0.44 7.07 +/- 0.76 5.44 +/- 0.85 14318.00 +/- 347.00 1.76 +/- 1.09 0.61 +/- 0.09 0.97 +/- 0.41 13.04 +/- 1.36 0.14 +/- 0.08 30.68 +/- 1.30 0.73 +/- 0.16 5.89 +/- 0.09 5.30 +/- 0.49 5107.00 +/- 223.00 13303.00 +/- 336.00 11.49 +/- 0.79 42.51 +/- 1.31 2.27 +/- 0.94 0.06 +/- 0.01 4.85 +/- 0.97 10.23 +/- 0.43 70.14 +/- 2.37 2.54 +/- 0.27 11.10 +0.58 19.63 +/- 0.64 381.58 +/- 85.76 3.04 +/-0.19 315.47 +/- 87.02 1.10 +/-0.53 0.67 +/- 0.11 0.56 +/- 0.05 1.04 +/- 0.40 0.70 +/- 0.18 33.52 +/- 0.70 0.53 +/-0.17 5.14 +/- 0.44 8.31 +/- 0.90 6.02 +/- 0.67 14350.00 +/- 347.00 2.67 +/- 1.01 0.47 +/- 0.09 1.26 +/- 0.52 10.76 +/- 1.26 0.24 +/- 0.10 32.64 +/- 1.24 0.62 +/- 0.28 5.90 +/- 0.09 5.19 +/- 0.65 5029.00 +/- 222.00 13130.00 +/- 334.00 11.81 +/- 0.70 40.04 +/- 1.39 2.53 +/- 1.05 0.07 +/- 0.02 5.91 +/- 1.17 10.18 +/- 0.32 72.01 +/- 2.38 2.63 +/- 0.24 10.69 +/- 0.60 21.03 +/- 0.96 401.30 +/- 86.67 3.21 +/- 0.15 327.30 +/- 87.56 1.51 +/- 0.58 0.61 +/-0.10 0.51 +/- 0.04 0.95 +/- 0.41 0.60 +/-0.13 33.56 +/- 0.53 0.58 +/- 0.12 5.22 +/- 0.31 7.69 +/- 0.59 5.73 +/- 0.54 14334.00 +/- 245.37 2.22 +/- 0.74 0.54 +/- 0.06 1.12 +/--0.33 11.90 +/- 0.93 0.19 +/- 0.06 31.66 +/- 0.90 0.68 +/-0.16 5.89 +/- 0.06 5.25 +/- 0.41 5068.00 +/- 157.33 13216.50 +/- 236.88 11.65 +/-0.53 41.28 +/- 0.95 2.40 +/- 0.70 0.07 +/- 0.01 5.38 +/- 0.76 10.21 +/-0.27 71.08 +/- 1.68 2.59 +/-0.18 10.90 +/- 0.42 20.33 +/- 0.58 391.44 +/- 60.96 3.13 +/- 0.12 321.39 +/- 61.72 1.31 +/- 0.39 0.64 +/- 0.07 0.54 +/- 0.03 1.00 +/- 0.29 Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass A5-3 TABLE A-5. In-House "Duplicate" Samples Concentration (pCi/L)a Averaged Lab Code Date Analysis First Result Second Result Result Acceptance G-3952,3953 G-3952,3953 G-3952,3953 G-3952,3953 WW-4036, 4037 VE-4204,4205 WW-4394,4395 VE-4183,4184 AV-4455, 4456 AV-4455, 4456 WW-4500, 4501 AP-090214A/B SG-5089, 5090 SG-5089, 5090 SG-5194,5 SG-5194,5 SG-5194,5 S-5632,3 S-5632,3 S-5632,3 S-5632,3 S-5632,3 S-5632,3 S-5632,3 DW-50243,4 AP-101414A/B SG-5590,1 SG-5590,1 DW-50251,2 U-5842.3 CF-6074,5 CF-6074,5 8/4/2014 8/4/2014 8/4/2014 8/4/2014 8/5/2014 8/11/2014 8/13/2014.
8/14/2014 8/22/2014 8/22/2014 8/26/2014 9/2/2014 9/1912014 9/19/2014 10/1/2014 10/1/2014 10/1/2014 10/8/2014 10/8/2014 10/8/2014 10/8/2014 10/8/2014 10/8/2014 10/8/2014 10/13/2014 10/14/2014 10/15/2014 10/15/2014 10/16/2014 10/20/2014 10/21/2014 10/21/2014 K-40 Be-7 Gr. Beta H-3 H-3 K-40 H-3 K-40 Be-7 K-40 H-3 Gr. Beta Ac-228 Bi-214 Gr. Alpha Pb-2114 Ac-228 K-40 Cs-137 TI-208 Pb-212 Pb-214 Bi-212 Ac-228 Gr. Alpha Gr. Beta Pb-214 Ac-228 Ra-226 H-3 H-3 K-40 5.42 + 0.42 1.29 +/- 0.19 8.53 +/- 0.20 140.16 +/- 93.50 190.60 +/- 82.60 6.28 +/- 0.38 1540.26 +/- 136.52 5.70 +/- 0.41 286.67 +/- 102.30 2547.90 +/- 255.70 347.00 +/- 100.00 0.03 +/- 0.04 8.26 +/- 0.63 4.71 +/- 0.29 276.20 +/- 9.51 43.56 +/- 0.73 59.90 +/- 1.37 19.28 +/- 0.88 0.15 +/- 0.03 0.32 +/- 0.03 0.92 +/- 0.05 1.25 +/- 0.08 1.25 +/- 0.29 1.08 +/-0.14 2.99 +/- 0.94 0.02 +/- 0.00 80.30 +/- 8.08 64.50 +/- 1.87 0.55 +/-0.13 7376 +/- 949 7509 +/- 283 3.09 +/- 0.31 5.35 +/- 0.34 1.24 +/-0.16 8.63 +/- 0.20 127.25 +/- 92.99 164.70 +/- 81.30 6.60 +/-0.37 1499.15 +/- 135.43 5.73 +/- 0.34 251.99 +/- 98.94 2201.40 +/- 203.90 321.00 +/- 98.00 0.03 +/- 0.04 9.48 +/- 0.68 4.41 +/- 0.31 258.60 +/- 9.26 43.94 +/- 0.78 62.80 +/- 1.73 17.94 +/- 0.89 0.13 +/-0.03 0.34 +/- 0.03 0.92 +/- 0.05 1.09+/- 0.09 1.34 +/- 0.47 1.10 +/- 0.14 4.98 +/- 1.17 0.02 +/- 0.00 73.40 +/- 7.51 62.80 +/- 1.15 0.32 +/-0.10 7342 +/-947 7969 +/- 291 3.30 +/- 0.38 5.38 +/- 0.27 1.27 +/- 0.13 8.58 +/- 0.14 133.70 +/- 65.94 177.65 +/- 57.95 6.44 +/- 0.27 1519.71 +/- 96.15 5.72 +/- 0.27 269.33 +/- 71.16 2374.65 +/- 163.52 334.00 +/- 70.01 0.03 +/- 0.00 8.87 +/- 0.46 4.56 +/- 0.21 267.40 +/- 6.64 43.75 +/- 0.53 61.35 +/- 1.10 18.61 +/- 0.63 0.14 +/- 0.02 0.33 +/- 0.02 0.92 +/- 0.03 1.17 +/- 0.06 1.29 +/- 0.27 1.09 +/- 0.10 3.99 +/- 0.75 0.02 + 0.00 76.85 + 5.52 63.65 +/- 1.10 0.44 +/- 0.08 7359 +/- 670 7739 +/- 203 3.20 +/- 0.25 Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass A5-4 TABLE A-5. In-House "Duplicate" Samples Concentration (pCi/L)a Averaged Lab Code Date Analysis First Result Second Result Result Acceptance VE-6269,70 VE-6269,70 SO-6500,1 SO-6500,1 SO-6500,1 SO-6500,1 SO-6500,1 SO-6500,1 SO-6500,1 SO-6500,1 SO-6500,1 SO-6500,1 SO-6500,1 SO-6500,1 DW-50262,3 DW-50264,5 DW-50264,5 AP-120214A/B AP-120814A/B SG-7068,9 SG-7068,9 S-7152,3 11/3/2014 11/3/2014 11/5/2014 11/512014 11/5/2014 11/5/2014 11/5/2014 11/5/2014 11/5/2014 11/5/2014 11/5/2014 11/5/2014 11/5/2014 11/5/2014 11/10/2014 11/10/2014 11/10/2014 12/2/2014 12/8/2014.
12/19/2014 12/19/2014 12/25/2014 K-40 Be-7 Sr-90 Gr. Alpha Gr. Beta U-233/4 U-238 Th-228 Th-230 Th-232 Bi-214 Pb-2114 Ac-228 Cs- 137 Gr. Alpha Ra-226 Ra-228 Gr. Beta Gr. Beta Pb-214 Ac-228 K-40 6.25 + 0.54 0.81 +/- 0.28 0.07 +/- 0.03 11.77 +/- 1.73 26.69 +/- 1.62 0.14 +/- 0.04 0.18 +/- 0.05 0.47 + 0.11 0.38 +/- 0.07 0.41 +/- 0.08 0.75 +/- 0.02 0.78 +/- 0.08 1.02 +/-0.11 0.40 +/- 0.01 8.95 +/- 1.26 3.89 +/- 0.24 2.96 +/- 0.63 0.03+/- 0.00 0.03 +/- 0.01 4.27 +/- 0.23 2.72 +/- 0.36 20.83 +/- 0.88 6.56 +/- 0.49 0.74 +/- 0.18 0.07 +/- 0.02 12.18 +/- 1.62 24.19 +/- 1.13 0.14 +/- 0.05 0.13 +/- 0.04 0.34 +/- 0.06 0.29 +/- 0.05 0.41 +/- 0.06 0.78 +/- 0.02 0.86 +/- 0.09 1.13 +/- 0.13 0.39 +/- 0.01 7.84 +/- 1.24 3.71 +/- 0.20 2.33 +/- 0.59 0.03 +/- 0.00 0.03 +/- 0.01 4.38 +/- 0.33 3.27 +/- 0.49 20.16 +/- 0.62 6.41 +/- 0.36 0.77 +/- 0.17 0.07 +/- 0.02 11.98 +/- 1.19 25.44 +/- 0.99 0.14 +/- 0.03 0.15 +/- 0.03 0.41 +/- 0.06 0.34 +/- 0.04 0.41 +/- 0.05 0.77 +/- 0.01 0.82 +/- 0.06 1.08 +/- 0.09 0.39 +/- 0.01 8.40 +/- 0.88 3.80 +/- 0.16 2.65 +/- 0.43 0.03 +/- 0.00 0.03 +/- 0.00 4.33 +/- 0.20 3.00 +/- 0.30 20.49 +/- 0.54 Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass A5-5 TABLE A-6. Department of Energy's Mixed Analyte Performance Evaluation Program (MAPEP).Concentration a Known Control Lab Code b Date Analysis Laboratory result Activity Limits ' Acceptance MAW-1140 2/1/2014 Gr. Alpha MAW-1 140 2/1/2014 Gr. Beta MAW-1 142 2/1/2014 1-129 MAW-1 184 MAW-1184 MAW-1184 MAW-1 1846 MAW-1184 e MAW-1 184 MAW-1 184 MAW-1184 MAW-1184 MAW-1 184 MAW-1 184 MAW-1 184 MAW-1184 MAW-1 184 MAW-1 184 MAW-1184 MAVE-1 148 MAVE-1 148 MAVE-1 148 MAVE-1 148 MAVE-1 148 MAVE-1 148 MAAP-1 151 MAAP-1151 d MAAP-1 151 MAAP-1 151 MAAP-1 151 MAAP-1 151 MAAP-1 151 MAAP-1151 MAAP-1 151 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 Fe-55 H-3 Ni-63 Pu-238 Pu-239/240 Sr-90 Tc-99 U-233/234 U-238 Co-57 Co-60 Cs-134 Cs-137 K-40 Mn-54 Zn-65 Co-57 Co-60 Cs-134 Cs-137 Mn-54 Zn-65 Am-241 Co-57 Co-60 Cs-i 34 Cs-137 Mn-54 Pu-238 Pu-239/240 Zn-65 0.77 +/- 0.06 4.31 +/- 0.08-0.01 +/- 8.00 0.40 +/- 3.20 345.10 +/- 10.60 32.40 +/- 3.20 1.28 +/- 0.12 0.91 +/- 0.10 7.00 +/- 0.70 8.10 +/- 0.60 0.20 +/- 0.07 1.25 +/- 0.18 27.86 +/- 0.38 15.99 +/- 0.27 21.85 +/- 0.54 28.74 +/- 0.49 1.80 +/- 2.00 14.06 +/- 0.40 0.00 +/- 0.19 11.63 +/- 0.19 7.28 +/- 0.18 6.29 +/- 0.29 5.18 +/- 0.20 9.22 +/- 0.26 8.59 +/- 0.40 0.09 +/- 0.02 1.60 +/- 0.05 1.38 +/- 0.08 1.75 +/- 0.11 1.81 +/- 0.10 0.01 +/- 0.03 0.08 +/- 0.02 0.10 +/- 0.02-0.24 +/- 0.09 0.85 4.19 0.00 0.26-1.44 2.10 -6.29 NA 0.00 321.00 34.00 0.83 0.68 8.51 10.30 0.23 1.45 27.50 16.00 23.10 28.90 0.00 13.90 0.00 10.10 6.93 6.04 4.74 8.62 7.86 0.09 0.00 1.39 1.91 1.76 0.00 0.00 0.08 0.00-0.01 -2.00 225.00 -417.00 23.80 -44.20 0.58 -1.08 0.47 -0.88 5.96-11.06 7.20 -13.40 0.16 -0.29 1.02-1.89 19.30 -35.80 11.20 -20.80 16.20 -30.00 20.20 -37.60 0.00 -10.00 9.70 -18.10-0.01 -0.00 7.10 -13.10 4.85 -9.01 4.23 -7.85 3.32 -6.16 6.03 -11.21 5.50 -10.22 0.06 -0.12 NA 0.97 -1.81 1.34 -2.48 1.23 -2.29 NA NA 0.05 -0.10-0.50 -1.00 Pass Pass Pass Pass Pass Pass Fail Fall Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Fail Pass Pass Pass Pass Fail Pass Pass A6-1 TABLE A-6. Department of Energy's Mixed Analyte Performance Evaluation Program (MAPEP).Concentration a Known Control Lab Code b Date Analysis Laboratory result Activity Limits ' Acceptance MAAP- 1151 MAAP-1 151 MAAP-1 151 MAAP-1 154 MAAP-1 154 MASO-1 146 MASO-1 146 MASO-1 146'MASO-1 146 MASO-1146 MASO-1 146 MASO-1 146 MASO-1 146 MASO-1 146 MASO-1146 e MASO-1146 a MASO-1 146 MASO-1 146 MASO-1146 9 MASO-11469 MASO-4439 MASO-4439 MASO-4439 MASO-4439 MASO-4439 MASO-4439 MASO-4439 MASO-4439 MASO-4439 MASO-4439 MAW-4431 MAW-4431 MAW-4431 MAW-4431 MAW-4431 MAW-4431 h MAW-4431 MAW-4431 2/1/2014 2/1/2014 2/1/2014 2/11/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/11/2014 2/11/2014 2/1/2014 2/1/2014 2/1/2014 2/11/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 2/1/2014 8/1/2014 8/1/2014 8/11/2014 8/1/2014 8/1/2014 8/1/2014 8/1/2014 8/1/2014 8/1/2014 8/1/2014 8/1/2014 8/1/2014 8/1/2014 8/1/2014 8/1/2014 8/1/2014 8/1/2014 8/1/2014 U-233/234 U-238 Sr-90 Gr. Alpha Gr. Beta Co-57 Co-60 Cs-134 Cs-137 K-40 Mn-54 Zn-65 Am-241 Ni-63 Pu-238 Pu-239/240 Sr-90 Tc-99 U-233/234 U-238 Am-241 Ni-63 Pu-239/240 Sr-90 Tc-99 Cs- 134 Co-57 Co-60 Mn-54 Zn-65 Am-241 Cs-137 Co-57 Co-60 H-3 Fe-55 Mn-54 Zn-65 0.03 +/- 0.01 0.13 +/- 0.02 1.11 +/- 0.14 0.56 +/- 0.06 0.98 +/- 0.06 0.02 0.13 1.18 1.77 0.77 0.01 -0.03 0.09 -0.17 0.83 -1.53 0.53 -3.01 0.39 -1.16 1064.50 +/- 3.60 1.70 +/- 0.50 6.10 +/- 1.80 1364.30 +/- 5.30 728.90 +/- 15.90 1588.00 +/- 6.00 763.50 +/- 6.80 68.20 +/- 9.00 4.80 +/- 15.30 140.60 +/- 15.50 102.00 +/- 13.10 1.23 +/- 1.37-0.30 +/- 12.00 22.90 +/- 3.00 32.00 +/- 3.60 65.90 +/- 6.70 771.62 +/- 23.29 55.63 +/- 5.81 778.34 +/- 17.82 458.20 +/- 9.20 520.60 +/- 7.09 1135.00 +/- 7.40 768.20 +/- 7.70 1050.70 +/- 12.60 407.89 +/- 15.03 0.79 +/- 0.08 18.62 +/- 0.54 24.85 +/- 0.42 12.27 +/- 0.38 207.20 +/- 10.60 55.10 +/- 14.80 14.36 +/- 0.53 11.46 +/- 0.78 966.00 1.22 0.00 1238.00 622.00 1430.00 695.00 68.00 0.00 96.00 76.80 0.00 0.00 81.00 83.00 85.50 980.00 58.60 858.00 589.00 622.00 1116.00 779.00 1009.00 541.00 0.88 18.40 24.70 12.40 208.00 31.50 14.00 10.90 676.00 -1256.00 NA d NA 867.00 -1609.00 435.00 -809.00 1001.00 -1859.00 487.00 -904.00 47.60 -88.40 NA 67.00 -125.00 53.80 -99.80 NA NA 57.00 -105.00 58.00 -108.00 59.90 -111.20 686.00 -1274.00 41.00 -76.20.601.00 -1115.00 412.00 -766.00 435.00 -809.00 781.00 -1451.00 545.00 -1013.00 706.00 -1312.00 379.00 -703.00 0.62 -1.14 12.90 -23.90 17.30 -32.10 8.70 -16.10 146.00 -270.00 22.10 -41.00 9.80 -18.20 7.60 -14.20 Pass Pass Pass Pass Pass Pass Pass Fail Pass Pass Pass Pass Pass Pass Fail Fail Pass Pass Fail Fail Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Fail Pass Pass A6-2 TABLE A-6. Department of Energy's Mixed Analyte Performance Evaluation Program (MAPEP).Concentration a Known Control Lab Code b Date Analysis Laboratory result Activity Limits c Acceptance MAW-4431 8/11/2014 Tc-99 6.10 +/- 0.50 6.99 4.89 -9.09 Pass MAW-4431 8/1/2014 Pu-238 0.59 t 0.07 0.62 0.43 -0.80 Pass MAW-4431 8/1/2014 U-233/234 0.22 +/- 0.04 0.21 0.14 -0.27 Pass MAW-4431 8/11/2014 U-238 1.25 +/- 0.10 1.42 0.99 -1.85 Pass MAW-4493 8/11/2014 Gr. Alpha 0.93 +/- 0.07 1.40 0.42 -2.38 Pass MAW-4493 8/11/2014 Gr. Beta 6.31 +/- 1.35 6.50 3.25 -9.75 Pass MAAP-4433 8/1/2014 Am-241 0.06 +/- 0.02 0.07 0.05 -0.09 Pass MAAP-4433 8/11/2014 Pu-238 0.10 +/- 0.03 0.11 0.08 -0.14 Pass MAAP-4433 8/11/2014 Pu-239/240 0.04 +/- 0.02 0.05 0.03 -0.06 Pass MAAP-4433 8/11/2014 Sr-90 0.74 +/- 0.10 0.70 0.49 -0.91 Pass MAAP-4433 8/11/2014 U-233/234 0.03 +/- 0.01 0.04 0.03 -0.05 Pass MAAP-4433 8/1/2014 U-238 0.21 +/- 0.03 0.25 0.18 -0.33 Pass MAAP-4444 8/1/2014 Sr-89 7.82 +/- 0.52 9.40 6.60 -12.20 Pass MAAP-4444 8/1/2014 Sr-90 0.76 +/- 0.10 0.76 0.53 -0.99 Pass MAVE-4436 8/1/2014 Cs-1 34 7.49 +/- 0.18 7.38 5.17 -9.59 Pass MAVE-4436 8/1/2014 Co-57 11.20 +/- 0.19 9.20 6.40-12.00 Pass MAVE-4436 8/1/2014 Co-60 6.84 +/- 0.17 6.11 4.28 -7.94 Pass MAVE-4436 8/1/2014 Mn-54 8.11 +/- 0.26 7.11 4.97 -9.23 Pass MAVE-4436 8/1/2014 Zn-65 7.76 +/- 0.43 6.42 4.49 -8.35 Pass a Results are reported in units of Bq/kg (soil), Bq/L (water) or Bq/total sample (filters, vegetation).
b Laboratory codes as follows: MAW (water), MAAP (air filter), MASO (soil), MAVE (vegetation).
'MAPEP results are presented as the known values and expected laboratory precision (1 sigma, I determination) and control limits as defined by the MAPEP. A known value of "zero" indicates an analysis was included in the testing series as a "false positive".
MAPEP does not provide control limits.d Interference from Eu-152 resulted in misidentification of Co-57.e The high bias on the plutonium crosscheck samples was traced to contamination from a newly purchased standard.The results of reanalysis with replacement tracer purchased from NIST: MAW-1184 Pu-238 0.68 +/- 0.10 BqIL MAW-1184 Pu-239/240 0.66 +/- 0.10 Bq/L MASO-1146 Pu-238 95.15 +/- 8.98 Bq / kg MASO-1 146 Pu-239/240 67.21 +/- 7.54 Bq / kg Insufficient sample remained to reanalyze the Air filter sample(MAAP-1151).
High bias results due to same contaminated tracer f Cs-134 was positively Identified in both library peaks, calculation on the second peak; 2.78 +/- 0.93 Bq/kg.9 80% of participating laboratories were outside the acceptable range.Parallel reanalysis was run on ERA spiked sample with acceptable results.h Result of reanalysis Fe-55 32.63 +/- 16.30 Bq I L A6-3 TABLE A-7. Interlaboratory Comparison Crosscheck program, Environmental Resource Associates (ERA)8.Concentration (pCi/L) b Lab Code b Date Analysis Laboratory ERA Control Result C Result Limits Acceptance ERAP-1044 ERAP-1044 ERAP- 1044 ERAP-1044 ERAP-1044 ERAP-1044 ERAP-1044 ERAP-1044 ERAP-1044 ERAP-1044 ERAP-1044 ERAP-1044 ERAP-1044 ERAP-1044 ERAP-1044 ERSO-1050 ERSO-1050 ERSO-1050 ERSO-1050 ERSO-1050 ERSO-1050 ERSO-1050 ERSO-1050 ERSO-1050 ERSO- 1050 ERSO-1050 ERSO-1050 ERSO-1050 e ERSO-1050 ERSO-1050 ERSO-1050 ERSO-1050 ERSO-1050 ERSO-1050 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/1712014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 Am-241 Co-60 Cs-134 Cs-137 Fe-55 Gr. Alpha Gr. Beta Mn-54 Pu-238 Pu-239/240 Sr-90 U-233/234 U-238 Uranium Zn-65 Am-241 Ac-228 Bi-212 Bi-214 Co-60 Cs-134 Cs-137 K-40 Mn-54 Pb-212 Pb-214 Pu-238 Pu-239/240 Sr-90 Th-234 U-233/234 U-238 Uranium Zn-65 54.2 +/- 3.0 1177.9 +/- 14.3 1010.5 +/- 15.8 938.3 +/- 45.7 142.3 +/- 87.3 52.3 +/- 0.5 64.4 +/- 2.6< 4.9 63.0 +/- 2.6 52.8 +/- 1.9 81.4 +/- 1.6 30.4 +/- 1.7 30.4 +/- 1.4 62.0 +/- 3.5 852.2 +/- 26.1 426.6 +/- 155.5 1260.0 +/- 107.0 1331.9 +/- 309.7 1804.5 +/- 50.4 6738.8 +/- 167.6 3262.9 +/- 108.8 8538.6 +/- 55.0 11241.3 +/- 296.6< 21.6 1119.6 +/- 26.1 1861.7 +/- 54.9 1085.5 +/- 167.7 681.6 +/- 128.6 2338.0 +/- 144.0 3474.9 +/- 226.0 3319.5 +/- 250.2 3375.6 +/- 252.6 6810.6 +/- 551.1 5968.0 +/- 226.1 59.7 1120.0 1010.0 828.0 240.0 46.0 53.8 0.0 56.3 48.6 78.9 36.4 36.1 74.3 667.0 399.0 1240.0 1240.0 1960.0 6830.0 3390.0 8490.0 10500.0 0.0 1240.0 2070.0 578.0 471.0 2780.0 3360.0 2780.0 3360.0 6910.0 5400.0 36.8 -80.8 867.0 -1400.0 643.0 -1250.0 622.0 -1090.0 74.4 -469.0 15.4-71.4 34.0 -78.4 NA 38.6 -74.0 35.2 -63.5 38.6 -118.0 22.6 -54.9 23.3 -49.9 41.1 -113.0 478.0 -921.0 233.0 -518.0 795.0 -1720.0 330.0 -1820.0 1180.0 -2820.0 4620.0 -9400.0 2220.0 -4070.0 6510.0 -10900.0 7660.0 -14100.0 NA 812.0 -1730.0 1210.0 -3090.0 348.0 -797.0 308.0 -651.0 1060.0 -4390.0 1060.0 -6320.0 1060.0 -4390.0 2080.0 -4260.0 3750.0 -9120.0 4300.0 -7180.0 Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Fail Fail Pass Pass Pass Pass Pass Pass A7-1 TABLE A-7. Interlaboratory Comparison Crosscheck program, Environmental Resource Associates (ERA)a.Concentration (pCi/L) b Lab Code b Date Analysis Laboratory ERA Control Result ' Result d Limits Acceptance ERVE-1051 ERVE-1051 ERVE-1 051 ERVE-1051 ERVE-1051 ERVE-1051 ERVE-1051 ERVE-1051 ERVE-1051 ERVE-1051 ERVE-1051 ERVE-1051 ERVE-1051 ERVE-1051 ERW-1054 ERW-1054 ERW-1054 ERW-1054 ERW-1054 ERW-1064 ERW-1054 ERW-1054 ERW-1054 ERW-1054 ERW-1054 ERW-1055 ERW-1055 ERW-1055 ERW-1055 ERW-1060 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 311712014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/17/2014 3/1712014 3/17/2014 Am-241 Cm-244 Co-60 Cs- 134 Cs- 137 K-40 Mn-54 Pu-238 Pu-239/240 Sr-90 U-233/234 U-238 Uranium Zn-65 Am-241 Co-60 Cs-134 Cs-137 Mn-54 Pu-238 Pu-239/240 U-233/234 U-238 Uranium Zn-65 Fe-55 Gr. Alpha Gr. Beta Sr-90 H-3 1532.0 +/- 149.5 519.8 +/- 94.6 981.2 +/- 41.8 701.4 +/- 58.6 961.9 +/- 46.3 32789.7 +/- 758.2<25.9 2724.1 +/- 259.4 4361.4 +/- 323.4 2405.7 +/- 263.2 1612.2 +/- 162.0 1574.3 +/- 159.6 3255.4 +/- 356.7 1124.1 +/- 101.2 104.6 +/- 3.4 1195.2 +/- 18.9 1474.9 +/- 47.5 2591.0 +/- 23.4< 4.3 54.1 +/- 3.6 185.9 +/- 17.6 74.8 +/- 6.3 76.4 +/- 7.8 154.3 +/- 14.6 1818.5 +/- 56.4 636.3 +/- 176.0 120.9 +/- 3.5 141.6 +/- 2.3 873.9 +/- 56.9 5818.0 +/- 230.0 1490.0 516.0 926.0 646.0 880.0 31900.0 0.0 2110.0 3740.0 2580.0 1760.0 1750.0 3580.0 919.0 114.0 1270.0 1660.0 2690.0 0.0 44.1 160.0 82.4 81.8 168.0 1800.0 1200.0 133.0 174.0 890.0 5580.0 911.0 -1980.0 253.0 -804.0 639.0 -1290.0 415.0 -839.0 638.0 -1220.0 23000.0 -44800.0 NA 1260.0 -2890.0 2300.0 -5150.0 1470.0 -3420.0 1160.0 -2260.0 1170.0 -2220.0 2430.0 -4460.0 663.0 -1290.0 76.8 -153.0 1100.0 -1490.0 1220.0 -1910.0 2280.0 -3220.0 NA 32.6 -54.9 124.0 -202.0 61.9 -106.0 62.4 -100.0 123.0 -217.0 1500.0 -2270.0 716.0 -1630.0 47.2 -206.0 99.6 -258.0 580.0 -1180.0 3740.0 -7960.0 Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Pass Fail Pass Pass Pass Pass S Results obtained by Environmental, Inc., Midwest Laboratory as a participant in the crosscheck program for proficiency testing administered by Environmental Resources Associates, serving as a replacement for studies conducted previously by the Environmental Measurements Laboratory Quality Assessment Program (EML).b Laboratory codes as follows: ERW (water), ERAP (air filter), ERSO (soil), ERVE (vegetation).
Results are reported In units of pCiIL, except for air filters (pCi/Filter), vegetation and soil (pCi/kg).c Unless otherwise indicated, the laboratory result is given as the mean +/- standard deviation for three determinations.
d Results are presented as the known values, expected laboratory precision (1 sigma, 1 determination) and control limits as provided by ERA. A known value of "zero" Indicates an analysis was included in the testing series as a "false positive".
Control limits are not provided.e The high bias on the plutonium crossoheck samples was traced to contamination from a newly purchased standard.The results of reanalysis with replacement tracer purchased from NIST: ERSO-1050 Pu-238 634.7 +/- 98.50 Bq / kg ERSO-1050 Pu-239/240 451.8 +/- 82.80 Bq / kg f An error in the efficiency calculation was found. The result of recalculation was 932 pCI/L.The sample was repeated, result of reanalysis, 1066 pCi/L.A7-2 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Appendix B 2014 REMP Data Summary Reports Environmental Radiological Monitoring Program Annual Summary Perry Nuclear Power Plant Docket Number 50-440/50-441 Lake County, Ohio Reporting Period: 2014 Mean for All Mean for Indicator Location with Hi hest Annual Mean Mean for Control Pathway Type and Total Locations Locations Mean Locations Sampled Number of Lower Limit of Location #Analyses Detection (LLD) Detected/Collected Detected/Collected Distance & Detected/Collected Detected/Collected Units Performed Range Range Direction Range Range 0.058 0.058 5 0.064 0.06 Air Be-7 N/A 28/28 24/24 0.8 4/4 4/4 pCi/m3 28 0.044 -0.069 0.044 -0.069 S 0.061 -0.069 0.057 -0.066< LLD < LLD < LLD Air Co-58 N/A 0/28 0/24 0/4 pCi/m3 28< LLD < LLD < LLD Air Co-60 N/A 0/28 0/24 0/4 pCi/m3 28< LLD < LLD < LLD Air Cs-134 0.037 0/28 0/24 0/4 pCi/m3 28< LLD < LLD < LLD Air Cs-137 0.045 0/28 0/24 0/4 pCi/m3 28 0.023 0.023 5 0.024 0.024 Air Gross Beta 0.0075 364/364 312/312 0.06 52/52 52/52 pCi/m3 364 p_____ 0.010 -0.048 0.010 -0.048 SW 0.014 -0.043 0.012 -0.041<LLD <LLD <LLD Air 1-131 0.05 0/364 0/312 0/52 pCi/m3 364 B-1 Environmental Radiological Monitoring Program Annual Summary Perry Nuclear Power Plant Docket Number 50-440/50-441 Lake County, Ohio Reporting Period: 2014 Pathway Type and Total Mean for All Mean for Indicator Location with Highest Annual Mean Mean for Control Pathay Tpe nd TtalLocations Locations Ma oain Sampled Number of Lower Limit of Location # Mean Locations Analyses Detection (LLD) Detected/Collected Detected/Collected Distance & Detected/Collected Detected/Collected Units Performed Range Range Direction Range Range 1479.3 1592.2 25 1592.2 1366.4 Fish K-40 N/A 22/22 11 /11 2.0 11 /11 11 /11 pCi/gm wet 22 630-2284 630-2138 NNW 630-2138 728 -2284< LLD < LLD < LLD Fish Mn-54 94 0/22 0/11 -0/11 pCi/gm wet 22< LLD < LLD < LLD Fish Fe-59 195 0/22 0/11 0/11 pCi/gm wet 22< LLD < LLD < LLD Fish Co-58 97 0/22 0/11 0/11 pCi/gm wet 22< LLD < LLD < LLD Fish Co-60 97 0/22 0/11 0/11 pCi/gm wet 22< LLD < LLD < LLD Fish Zn-65 195 0/22 0/11 0/11 pCi/gm wet 22< LLD < LLD < LLD Fish Cs-1 34 97 0/22 0/11 -0/11 pCi/gm wet 22 B-2 Environmental Radiological Monitoring Program Annual Summary Perry Nuclear Power Plant Docket Number 50-440/50-441 Lake County, Ohio Reporting Period: 2014 Pathway Type and Total Mean for All Mean for Indicator Location with Highest Annual Mean Mean for Control Pathay Tpe nd TtalLocations Locations Ma oain Sampled Number of Lower Limit of Location # Mean Locations Analyses Detection (LLD) Detected/Collected Detected/Collected Distance & Detected/Collected Detected/Collected Units Performed Range Range Direction Range Range< LLD < LLD < LLD Fish Cs-137 112 0/22 0/11 --0/11 pCi/gm wet 22 Broadleaf 398.2 372.5 2 519.8 493.3 Vegetation N/A 61/73 48/58 2.0 12/13 13/15 pCi/Kg wet 73 117 -838 117-838 ENE 188 -838 154 -775 Broadleaf 4328.3 4298.2 20 4762.7 4444.9 Vegetation N/A 73/73 58/58 1.9 15/15 15/15 pCi/Kg wet 73 2582 -6643 2582- 6643 E 2792- 6643 2821 -6523 Broadleaf
< LLD < LLD < LLD Vegetation Co-58N/A 0/73 0/58 -0/15 pCi/Kg wet 7 Broadleaf C60< LLD < LLD < LLD Vegetation N/A 0/73 0/58 0/15 p~i/K wet 73 -pCi/Kg wet 7 -Broadleaf
< LLD < LLD < LLD Vegetation 345 0/73 0/58 0/15 pCi/Kg wet 73 Broadleaf
< LLD < LLD < LLD Vegetation Cs1445 0 /73 0 /58 -0 / 15 pCi/Kg wet B-3 Environmental Radiological Monitoring Program Annual Summary Perry Nuclear Power Plant Docket Number 50-440/50-441 Lake County, Ohio Reporting Period: 2014 Mean for All Mean for Indicator Location with Highest Annual Mean Mean for Control Pathway Type and Total Locations Locations Mean Locations Sampled Number of Lower Limit of Location #Analyses Detection (LLD) Detected/Collected Detected/Collected Distance & Detected/Collected Detected/Collected Units Performed Range Range Direction Range Range Broadleaf
< LLD < LLD < LLD Vegetation 60 0/73 0/58 --0/15 pCi/Kg wet 7 1463.4 1514.6 18 1689.3 1341.9 Milk K-40 N/A 64/64 45/45 2.6 16/16 19/19 pCi/L 64 p____ 1107-2009 1107-2009 E 1397-1887 1202-1442< LLD < LLD < LLD Milk 1-131 0.8 0/64 0/45 0/19 pCi/L 64< LLD < LLD < LLD Milk Cs-1 34 11 0/64 0/45 0/19 pCi/L 64< LLD < LLD < LLD Milk Cs-137 13 0/64 0/45 0/19 pCi/L 64< LLD < LLD < LLD Milk Ba-140 45 0/64 0/45 0/19 pCi/L 64< LLD < LLD < LLD Milk La-140 11 0/64 0/45 0/19 pCi/L 64 B-4 Environmental Radiological Monitoring Program Annual Summary Perry Nuclear Power Plant Docket Number 50-440/50-441 Lake County, Ohio Reporting Period: 2014 Mean for All Mean for Indicator Location with Highest Annual Mean Mean for Control Pathway Type and Total Locations Locations Mean Locations Sampled Number of Lower Limit of Location #Analyses Detection (LLD) Detected/Collected Detected/Collected Distance & Detected/Collected Detected/Collected Units Performed Range Range Direction Range Range 8617.0 7797.8 32 13532.0 13532.0 Sediment K-40 N/A 7/7 6/6 15.8 1 /1 1/1 pCi/kg wet 7 6125-13532 6125-10765 WSW 13532-13532 13532 -13532< LLD < LLD < LLD Sediment Co-58 50 0/7 0/6 -0/1 pCi/kg wet 7< LLD < LLD < LLD Sediment Co-60 40 0/7 0/6 0/1 pCi/kg wet 7< LLD < LLD < LLD Sediment Cs-1 34 112 0/7 0/6 -0/1 pCi/kg wet 7 68.5 56.5 32 80.4 80.4 Sediment Cs-137 135 2/7 1/6 15.8 1/1 1/1 pCi/kg wet 7 p______wet 7 56.5-80.4 56.5-56.5 WSW 80.4 -80.4 80.4 -80.4 12.5 12.5 33 18.2 11.5 TLD Direct 1.0 115/116 107/108 4.7 4/4 8/8 mR/91 days 116 mR/91 days 116 7.1 -19.1 7.1 -19.1 S 17.5-19.1 9.7-14.0 12.0 12.0 31 15.9 12.3 TLD Direct 1.0 116/116 108/108 4.9 4/4 8/8 mR/91 days 116___________________
7.3 -19.2 7.3 -19.2 SE 15.5 -16.4 10.5 -15.5 B-5 Environmental Radiological Monitoring Program Annual Summary Perry Nuclear Power Plant Docket Number 50-440/50-441 Lake County, Ohio Reporting Period: 2014 Mean for All Mean for Indicator Location with Highest Annual Mean Mean for Control Pathway Type and Total Locations Locations Mean Locations Sampled Number of Lower Limit of Location #Analyses Detection (LLD) Detected/Collected Detected/Collected Distance & Detected/Collected Detected/Collected Units Performed Range Range Direction Range Range 64.1 64.0 31 83.2 64.7 TLD Direct 1.0 29/29 27/27 4.9 1/1 2/2 mRI365 days 29 50.1 -83.2 50.1 -83.2 SE 83.2-83.2 61.6-67.8 2.2 2.2 60 2.8 2.2 Water Gross Beta 3.0 51/54 40-42 1.0 9/9 11/12 pCi/L 1.0-4.5 1.0-4.5 WSW 1.5-4.5 1.0-3.2< LLD < LLD < LLD Water H-3 1500 0/18 0/14 0/4 pCi/L 18< LLD < LLD < LLD Water Mn-54 11 0/54 0/42 0/12 pCi/L 54< LLD < LLD < LLD Water Fe-59 22 0/54 0/42 0/12 pCi/L 54< LLD < LLD < LLD Water Co-58 11 0/54 0/42 0/12 pCi/L 54< LLD < LLD < LLD Water Co-60 11 0/54 0/42 0/12 pCi/L 54 B-6 Environmental Radiological Monitoring Program Annual Summary Perry .Nuclear Power Plant Docket Number 50-440/50-441 Lake County, Ohio Reporting Period: 2014 Mean for All Mean for Indicator Location with Hi-hest Annual Mean Mean for Control Pathway Type and Total Locations Locations Mean Locations Sampled Number of Lower Limit of Location #Analyses Detection (LLD) Detected/Collected Detected/Collected Distance & Detected/Collected Detected/Collected Units Performed Range Range Direction Range Range< LLD < LLD < LLD Water Zn-65 22 0/54 0/42 0/12 pCi/L 54< LLD < LLD < LLD Water Zr-95 22 0/54 0/42 -0/12 pCi/L 54< LLD < LLD < LLD Water Nb-95 11 0/54 0/42 -0/12 pCi/L 54< LLD < LLD < LLD Water Cs-i134 11 0/54 0/42 -0/12 pCi/L 54< LLD < LLD < LLD Water Cs-1 37 13 0/54 0/42 -0/12 pCi/L 54< LLD < LLD < LLD Water Ba-140 45 0/54 0/42 -0/12 pCi/L 54< LLD < LLD < LLD Water La-140 11 0/54 0/42 -0/12 pCi/L 54 B-7 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Appendix C 2014. REMP Detailed Data Report Inc.*qMidwest Laboratory 700 Landwehr Road
- Nortdxook.
IL 60062-2310 ph. (847) 564.0700 .ftx (847) 564-4517 MONTHLY PROGRESS REPORT to FIRST ENERGY CORPORATION RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (REMP)FOR THE PERRY NUCLEAR POWER PLANT Reporting Period: January-December, 2014 Prepared and Submitted by ENVIRONMENTAL, INC., MIDWEST LABORATORY Project Number: 8033 Reviewed and Approved B. Grob, M.S.Laboratory Manager Date Distribution:
J. Bumett R. Leidy, Ohio Department of Health J. Lucia, Lake County Health Department C-1 TABLE OF CONTENTS Section Page List of T ables ..................................................................................
..iii
1.0 INTRODUCTION
................................................................................
iv 2.0 LISTING OF MISSED SAMPLES ..........................................................
v 3.0 DATA TABLES ..................................................................................
vi Appendices A Interlaboratory Comparison Program Results ...........................................
A-1 B Data Reporting Conventions
.................................................................
B-1 C-2 LIST OF TABLES No. Title Page 1 Direct Radiation, Quarterly and Annual .......................................................
1-1 2 Airborne Particulate Filters and Charcoal Canisters
......................................
2-1 3 Airborne Particulate Filters ........................................................................
3-1 4 Lake Water ......................................................................................
4-1 5 M ilk .....................................................................................................
5 -1 7 Food P rod ucts ........................................................................................
7-1 9 F is h ....................................................................................................
9 -1 1 1 S e d im e nts ............................................................................................
1 1-1 C-3
1.0 INTRODUCTION
The following constitutes the current 2014 Monthly Progress Report for the Radiological Environmental Monitoring Program conducted at the Perry Nuclear Power Plant in Perry, Ohio. Results of completed analyses are presented in the attached tables.The data obtained in the program were within ranges previously encountered and to be expected in the environmental media sampled.All concentrations, except gross beta, are decay corrected to the time of collection.
Airborne iodine is decay corrected to the midpoint of the collection period.All samples were collected within the scheduled period, unless noted otherwise in Table 2.0, Listing of Missed Samples.C-4 Table 1. Direct Radiation (TLDs), Quarterly Exposure.Units: mRI91 days 1st Qtr. 2nd Qtr. 3rd Qtr. 4th Qtr.Date Placed 01-13-14 04-01-14 07-02-14 10-15-14 Date Removed 04-01-14 07-02-14 10-10-14 01-12-15 E-1 12.0 +/- 1.6 12.2 +/-0.9 11.4 +/- 1.2 12.7 +/- 1.5 E-3 12.3 +/- 0.6 9.4 +/- 1.1 10.5 +/- 0.8 12.1 +/- 1.2 E-4 14.5 +/-0.7 11.7 +/-0.6 11.5 +/-0.7 12.8 +/- 1.0 E-5 13.4 +/- 0.8 8.3 +/- 0.6 11.8 +/- 0.9 8.0 +/- 0.8 E-6 14.0 +/- 1.4 9.7 +/- 0.7 13.6 +/- 1.0 9.7 +/- 0.9 E-7 13.3 +/- 1.0 10.7 +/-0.8 13.2 +/-0.9 11.0 +/- 1.1 E-8 13.1 +/-0.7 9.8 +/-0.7 12.6 +/-0.7 9.7 1.1 E-9 10.8 +/-0.6 9.5 +/-0.6 10.8 +/-0.7 11.8 +/-1.0 E-10 10.8 +/- 1.0 11.4 +/- 0.8 11.9 +/- 0.8 11.2 +/-0.9 E-11 14.6 +/-0.9 10.0 +/-0.7 15.4 +/- 1.0 9.8 +/-1.1 E-12 14.7 +/-1.1 9.8 +/-1.0 11.8 +/-0.8 15.1 +/-1.8 E-13 13.4 +/- 1.0 10.9 +/-0.8 12.6 +/-0.9 11.1 +/-1.0 E-14 10.1 +/- 0.7 10.7 +/- 0.7 10.1 +/- 1.1 10.2 +/-0.9 E-15 7.8 +/-0.7 11.3 +/- 1.0 7.9 +/-0.8 7.1 +/-0.8 E-21 13.4 +/- 0.8 12.0 +/- 0.7 16.3 +/- 0.7 17.0 +/-0.9 E-23 16.4 +/- 1.0 12.6 +/- 0.8 13.2 +/- 0.8 17.0 +/- 1.1 E-24 12.9 +/- 0.9 10.5 +/- 0.9 10.8 +/- 0.7 10.6 +/- 1.2 E-29 15.5 +/- 0.8 14.9 +/- 1.0 15.3 +/- 0.7 17.6 +/- 1.4 E-30 14.6 +/- 1.7 14.0 +/- 0.7 13.9 +/- 0.7 14.1 +/-1.2 E-31 14.9 +/-0.9 12.6 +/- 1.0 14.8 +/-0.9 11.5 +/-1.2 E-33 18.3 +/- 1.0 17.5 +/- 1.2 19.1 +/- 0.9 17.9 +/- 0.9 E-35 12.6 +/-0.6 9.9 +/-0.7 11.9 +/-0.8 9.5 +/-0.9 E-36 16.5 +/-0.7 11.9 +/-0.6 16.0 +/-0.7 11.3 +/- 1.0 E-53 13.1 +/-0.7 11.1 +/-0.9 14.4 +/-0.8 10.4 +/-1.0 E-54 17.1 +/- 1.3 10.6 +/-0.6 12.7 +/-0.8 10.0 +/-0.7 E-55 16.5 +/- 1.3 11.9 +/- 1.1 14.3 +/- 1.4 13.3 +/- 1.3 E-56 14.6 +/- 0.6 12.7 +/- 0.7 13.2 +/- 0.6 12.0 +/-0.9 E-57 NDa 13.0 +/- 1.0 10.3 +/- 0.7 13.3 +/- 1.2 E-58 11.9 +/- 0.7 9.0 +/- 0.7 10.2 +/- 0.6 10.8 +/-0.8 Mean +/-s.d. 13.7 +/- 2.3 11.4 +/- 1.9 12.8 +/- 2.3 12.0 +/-2.8 E-Control 1 8.5 +/- 1.6 8.1 +/- 0.7 7.6 +/- 1.0 8.7 +/- 1.0 E-Control 2 5.8 +/- 0.8 5.9 +/- 0.6 6.4 +/- 0.7 6.1 +/- 0.7 a Not enough counts above background for calculation.
Placed 3/17/14, removed 4/1/14.C-5 Table 1. Direct Radiation (TLDs), Quarterly Exposure.Units: mR/91 days Date Placed Date Removed 1st Qtr.01-13-14 04-01-14 Q-1 Q-3 Q-4 Q-5 Q-6 Q-7 Q-8 Q-9 Q-1 0 Q-1 1 Q-1 2 Q-13 Q-14 Q-15 Q-21 Q-23 Q-24 Q-29 Q-30 Q-31 Q-33 Q-35 Q-36 Q-53 Q-54 Q-55 Q-56 Q-57 Q-58 13.1 +/- 1.5 11.2 +/- 1.2 13.3 +/- 0.8 7.9 +/- 0.7 12.7 +/- 0.8 11.9 +/- 0.6 8.6 +/- 0.7 12.1 +/- 0.7 10.5 +/- 0.7 11.6 +/-0.7 13.2 +/- 0.5 9.0 +/- 0.5 11.1 +/- 0.5 11.4 +/- 0.7 11.1 +/-0.5 11.1 +/-0.9 13.3 +/- 1.9 16.1 +/- 0.7 14.7 +/- 0.8 15.9 +/- 1.3 13.4 +/- 0.7 13.5 +/- 0.6 17.9 +/- 0.5 13.1 +/- 0.4 13.8 +/- 0.8 14.1 +/- 0.7 14.1 +/- 0.7 13.1 +/- 5.0 8.0 +/- 0.8 2nd Qtr.04-01-14 07-02-14 11.1 +/-1.4 7.3 +/- 1.2 10.7 +/- 1.1 9.7 +/- 1.2 11.2 +/- 1.2 11.4 +/- 1.1 8.7 +/- 1.1 8.3 +/- 1.1 11.7 +/- 1.1 13.1 +/- 1.1 10.7 +/- 1.1 10.5 +/- 1.3 10.3 +/- 1.2 10.3 +/- 1.3 11.2 +/- 1.2 14.3 +/- 1.5 11.5 +/-1.1 15.1 +/- 1.4 11.2 +/- 1.0 15.6 +/- 1.1 16.8 +/- 1.2 8.9 +/- 1.1 13.5 +/- 1.2 12.1 +/- 1.1 13.1 +/- 1.1 10.3 +/- 1.5 12.7 +/- 1.2 11.4 +/- 1.2 8.9 +/- 1.1 3rd Qtr.07-02-14 10-10-14 9.0 +/- 0.8 10.0 +/- 0.5 11.9 +/- 0.6 7.8 +/- 0.4 12.1 +/- 0.8 12.9 +/- 0.4 8.8 +/- 0.5 10.5 +/- 1.1 11.5 +/-0.5 11.4 +/-0.5 12.4 +/- 0.4 9.0 +/- 0.4 11.0 +/- 0.6 8.9 +/- 0.7 11.4 +/- 0.5 11.2 +/- 0.8 11.9 +/- 1.1 14.6 +/- 0.7 13.8 +/- 0.6 15.5 +/- 0.6 13.5 +/- 0.5 11.2 +/- 0.5 14.8 +/- 0.5 12.4 +/- 0.5 12.6 +/- 0.6 12.6 +/- 0.5 12.2 +/- 0.5 13.3 +/- 1.2 7.7 +/- 0.6 4th Qtr.10-15-14 01-12-15 13.8 +/- 1.9 8.7 +/- 1.5 14.1 +/- 1.9 13.7 +/- 1.7 15.5 +/- 1.5 15.9 +/- 1.4 10.4 +/- 1.3 11.5 +/- 1.3 12.2 +/- 1.2 13.7 +/- 1.3 11.2 +/- 1.5 10.5 +/- 1.5 15.1 +/- 1.4 10.1 +/- 1.3 11.3 +/- 1.4 14.6 +/- 1.7 10.5 +/- 1.2 15.9 +/- 1.5 11.5 +/- 1.3 16.4 +/- 1.2 19.2 +/- 1.5 8.6 +/- 1.2 13.2 +/- 1.3 12.8 +/- 1.4 13.0 +/- 1.3 10.1 +/- 1.4 14.7 +/- 1.8 11.1 +/- 1.3 9.7 +/- 1.2 Mean +/- s.d.0-Control 1 0-Control 2 12.4 +/- 2.3 8.3 +/- 0.5 6.8 +/- 0.5 11.4 +/- 2.2 5.5 +/- 1.1 6.4 +/- 1.1 11.6 +/-2.0 7.9 +/- 0.4 6.6 +/-0.4 12.7 +/-2.6 5.7 +/- 1.3 6.9 +/- 1.2' Placed 3/1 7/1 4, removed 4/1/14.C-6 Table 1. Direct Radiation (TLDs), Annual Exposure.Units: mR/365 days Date Placed Date Removed A-1 A-3 A-4 A-5 A-6 A-7 A-8 A-9 A-1 0 A-11 A-1 2 A-1 3 A-1 4 A-15 A-21 A-23 A-24 A-29 A-30 A-31 A-33 A-35 A-36 A-53 A-54 A-55 A-56 A-57 A-58 Mean + s.d.A-Control 1 A-Control 2 2014 01-13-14 01-12-15 58.8 +/- 4.0 56.2 +/- 2.5 62.4 +/- 2.6 59.0 +/- 2.5 67.8 +/- 2.6 59.3 +/- 3.6 61.8 +/- 3.5 50.1 +/- 3.0 63.0 +/- 2.4 65.8 +/- 2.6 63.7 +/- 3.0 64.5 +/- 2.6 55.1 +/- 2.8 53.4 +/- 2.4 70.9 +/- 4.8 57.0 +/- 2.4 61.6 +/- 3.3 78.7 +/- 3.9 63.0 +/- 3.1 79.6 +/- 4.3 81.7 +/- 2.4 52.7 +/- 1.7 83.2 +/- 2.1 67.1 +/- 2.8 67.9 +/- 2.3 68.4 +/- 2.6 66.0 +/- 2.4 64.8 +/- 4.6 55.0 +/- 2.7 a 64.1 +/- 8.6 26.3 +/- 1.8 26.5 +/- 1.4 a Placed 03-17-14; removed 01-12-15.C-7 Table 2. Airborne particulates and charcoal canisters, analyses for gross beta and iodine-1 31.Location:
P-1 Units: pCi/m 3 Collection:
Continuous, weekly exchange.Date Volume Date Volume Collected (ma) Gross Beta 1-131 Collected (mi) Gross Beta 1-131 Required LLD 0.0075 0.050 0.0075 0.050 01-08-14 01-15-14 01-22-14 01-30-14 02-06-14 02-13-14 02-20-14 02-27-14 03-05-14 03-13-14 03-19-14 03-27-14 04-03-14 454 558 538 617 551 542 532 522 452 224 448 611 542 0.030 +/- 0.004 0.034 +/- 0.003 0.028 +/- 0.003 0.018 +/- 0.002 0.029 +/- 0.003 0.034 +/- 0.003 0.037 +/- 0.003 0.032 +/- 0.003 0.038 +/- 0.004 0.037 +/- 0.006 0.020 +/- 0.003 0.028 +/- 0.003 0.024 +/- 0.003< 0.011< 0.006< 0.005< 0.009< 0.011< 0.005< 0.012< 0.008< 0.005< 0.022< 0.007< 0.010< 0.010 07-10-14 07-17-14 07-23-14 07-31-14 08-07-14 08-14-14 08-21-14 08-28-14 09-04-14 09-11-14 09-18-14 09-25-14 10-02-14 558 538 482 630 536 560 554 516 561 546 537 531 552 0.018 +/- 0.003 < 0.010 0.018 +/- 0.003 < 0.005 0.023 +/- 0.003 < 0.005 0.016 +/- 0.002 < 0.006 0.026 +/- 0.003 < 0.007 0.020 +/- 0.003 < 0.011 0.019 +/-0.003 < 0.009 0.021 +/- 0.003 < 0.013 0.021 +/- 0.003 < 0.007 0.022 +/- 0.003 < 0.007 0.015 +/- 0.003 < 0.005 0.026 +/- 0.003 < 0.007 0.026 +/- 0.003 < 0.007 1Q 2014 Mean +/- s.d.04-09-14 04-17-14 04-24-14 05-01-14 05-08-14 05-15-14 05-21-14 05-28-14 06-05-14 06-12-14 06-19-14 06-26-14 07-03-14 455 608 532 547 534 566 505 571 657 556 557 562 548 0.030 +/- 0.006 0.017 +/- 0.003 0.026 +/- 0.003 0.030 +/- 0.003 0.016 +/- 0.003 0.015 +/- 0.003 0.019 +/- 0.003 0.020 +/- 0.003 0.014 +/- 0.003 0.016 +/- 0.002 0.015 +/- 0.003 0.014 +/- 0.003 0.013 +/- 0.003 0.018 +/- 0.003< 0.022< 0.010< 0.011< 0.008< 0.011< 0.006< 0.011< 0.008< 0.006< 0.006< 0.005< 0.012< 0.011< 0.013 3Q 2014 Mean +/- s.d.10-09-14 10-16-14 10-23-14 10-30-14 11-06-14 11-13-14 11-20-14 11-26-14 12-04-14 12-10-14 12-18-14 12-25-14 12-31-14 532 545 544 532 616 608 585 503 727 504 680 586 514 0.021 +/- 0.004 < 0.013 0.023 +/- 0.003 < 0.012 0.018 +/- 0.003 < 0.009 0.014 +/- 0.003 < 0.011 0.026 +/- 0.003 < 0.007 0.020 +/- 0.002 < 0.010 0.020 +/- 0.002 < 0.007 0.024 +/- 0.003 < 0.007 0.031 +/- 0.003 < 0.011 0.030 +/- 0.002 < 0.005 0.033 +/- 0.003 < 0.012 0.039 +/- 0.003 < 0.004 0.016 +/- 0.003 < 0.008 0.025 +/- 0.003 < 0.013 2Q 2014 Mean +/- s.d.0.018 +/- 0.005< 0.013 4Q 2014 Mean +/- s.d.Cumulative Average 0.025 +/- 0.007 <0.013 0.023 C-8 Table 2. Airborne particulates and charcoal canisters, analyses for gross beta and iodine-1 31.Location:
P-3 Units: pCi/m 3 Collection:
Continuous, weekly exchange.Date Volume Date Volume Collected (ma) Gross Beta 1-131 Collected (ma) Gross Beta 1-131 Required LLD 0.0075 0.050 0.0075 0.050 01-08-14 01-15-14 01-22-14 01-30-14 02-06-14 02-13-14 02-20-14 02-27-14 03-05-14 03-13-14 03-19-14 03-27-14 04-03-14 472 593 548 639 544 548 543 520 463 222 460 620 546 0.028 +/- 0.003 0.034 +/- 0.003 0.028 +/- 0.003 0.024 +/- 0.003 0.031 +/- 0.003 0.033 +/- 0.003 0.036 +/- 0.003 0.030 +/- 0.003 0.039 +/- 0.004 0.035 +/- 0.006 0.016 +/- 0.003 0.025 +/- 0.003 0.021 +/- 0.003< 0.010< 0.006< 0.005< 0.008< 0.011< 0.005< 0.011< 0.008< 0.005< 0.032< 0.007< 0.010< 0.010 07-10-14 07-17-14 07-23-14 07-31-14 08-07-14 08-14-14 08-21-14 08-28-14 09-04-14 09-11-14 09-18-14 09-25-14 10-02-14 627 572 528 665 628 578 606 562 608 587 586 580 589 0.018 +/- 0.002 < 0.009 0.019 +/- 0.003 < 0.005 0.021 +/- 0.003 < 0.005 0.016 +/- 0.002 < 0.006 0.022 +/- 0.003 < 0.006 0.019 +/- 0.003< 0.011 0.015 +/- 0.003 < 0.008 0.021 +/- 0.003 < 0.012 0.021 +/- 0.003 < 0.006 0.018 +/- 0.003 < 0.006 0.015 +/- 0.002 < 0.004 0.023 +/- 0.003 < 0.006 0.026 +/- 0.003 < 0.006 1Q 2014 Mean +/- s.d.04-09-14 04-17-14 04-24-14 05-01-14 05-08-14 05-15-14 05-21-14 05-28-14 06-05-14 06-12-14 06-19-14 06-26-14 07-03-14 451 610 534 544 523 611 501 579 681 607 607 603 590 0.029 +/- 0.006 0.020 +/- 0.003 0.022 +/- 0.003 0.029 +/- 0.003 0.012 +/- 0.003 0.013 +/- 0.003 0.020 +/- 0.003 0.018 +/- 0.003 0.016 +/- 0.003 0.015 +/- 0.002 0.017 +/- 0.003 0.014 +/- 0.002 0.015 +/- 0.003 0.018 +/- 0.003< 0.032< 0.010< 0.011< 0.008< 0.011< 0.006< 0.010< 0.008< 0.006< 0.006< 0.005< 0.011< 0.010< 0.012 3Q2014 Mean+/-s.d.10-09-14 10-16-14 10-23-14 10-30-14 11-06-14 11-13-14 11-20-14 11-26-14 12-04-14 12-10-14 12-18-14 12-25-14 12-31-14 559 598 573 601 670 682 678 587 800 585 790 678 573 0.020 +/- 0.003 < 0.012 0.024 +/- 0.003 < 0.011 0.017 +/- 0.003 < 0.008 0.015 +/- 0.002 < 0.010 0.026 +/- 0.003 < 0.006 0.021 +/- 0.002 < 0.009 0.019 +/- 0.002 < 0.007 0.023 +/- 0.002 < 0.006 0.034 +/- 0.003 < 0.010 0.027 +/- 0.002 < 0.005 0.030 +/- 0.003 < 0.010 0.037 +/- 0.002 < 0.004 0.016 +/- 0.002 < 0.007 0.025 +/- 0.003 < 0.012 2Q 2014 Mean +/- s.d.0.018 +/- 0.005< 0.012 4Q 2014 Mean +/- s.d.Cumulative Average 0.024 +/- 0.007 < 0.012 0.023 C-9 Table 2. Airborne particulates and charcoal canisters, analyses for gross beta and iodine-1 31.Location:
P-4 Units: pCi/m 3 Collection:
Continuous, weekly exchange.Date Volume Date Volume Collected (me) Gross Beta 1-131 Collected (me) Gross Beta 1-131 Required LLD 0.0075 0.050 0.0075 0.050 01-08-14 456 01-15-14 552 01-22-14 535 01-30-14 621 02-06-14 529 02-13-14 537 02-20-14 525 02-27-14 509 03-05-14 448 03-13-14 210 03-19-14 445 03-27-14 604 04-03-14 529 0.028 +/- 0.003 < 0.011 0.032 +/- 0.003 < 0.006 0.031 +/- 0.003 < 0.005 0.021 +/- 0.003 < 0.008 0.033 +/- 0.003 < 0.011 0.035 +/- 0.003 < 0.005 0.037 +/- 0.003 < 0.012 0.029 +/- 0.003 < 0.009 0.043 +/- 0.004 < 0.005 0.032 +/- 0.007 < 0.020 0.019 +/- 0.003 < 0.007 0.024 +/- 0.003 < 0.010 0.024 +/- 0.003 < 0.010 07-10-14 07-17-14 07-23-14 07-31-14 08-07-14 08-14-14 08-21-14 08-28-14 09-04-14 09-11-14 09-18-14 09-25-14 10-02-14 493 476 469 613 565 539 558 512 564 540 489 294 533 0.017 +/-0.003 < 0.011 0.019 +/- 0.003 < 0.006 0.020 +/- 0.003 < 0.006 0.018 +/- 0.002 < 0.006 0.027 +/- 0.003 < 0.007 0.021 +/- 0.003 < 0.012 0.020 +/- 0.003 < 0.009 0.021 +/-0.003 < 0.013 0.023 +/- 0.003 < 0.007 0.018 +/- 0.003 < 0.007 0.017 +/- 0.003 < 0.005 0.040 +/- 0.005 < 0.012 0.025 +/- 0.003 < 0.007 1Q 2014 Mean +/- s.d.04-09-14 430 04-17-14 594 04-24-14 505 05-01-14 524 05-08-14 507 05-15-14 526 05-21-14 461 05-28-14 535 06-05-14 620 06-12-14 519 06-19-14 338 06-26-14 547 07-03-14 550 0.030 +/- 0.007 < 0.020 0.019 +/- 0.003 < 0.010 0.024 +/- 0.003 < 0.012 0.026 +/- 0.003 < 0.008 0.014 +/- 0.003 < 0.011 0.012 +/- 0.003 < 0.007 0.022 +/- 0.003 < 0.011 0.020 +/- 0.003 < 0.009 0.016 +/- 0.003 < 0.006 0.015 +/- 0.002 < 0.006 0.016 +/- 0.003 < 0.006 0.022 +/- 0.004 < 0.020 0.015 +/- 0.003 < 0.011 0.017 +/- 0.003 < 0.013 3Q 2014 Mean +/- s.d.10-09-14 493 10-16-14 544 10-23-14 517 10-30-14 513 11-06-14 564 11-13-14 539 11-20-14 528 11-26-14 442 12-04-14 620 12-10-14 444 12-18-14 590 12-25-14 529 12-31-14 438 0.022 +/- 0.006 < 0.013 0.025 +/- 0.003 < 0.013 0.018 +/- 0.003 < 0.009 0.013 +/- 0.003 < 0.011 0.027 +/- 0.003 < 0.007 0.017 +/- 0.003 < 0.011 0.017 +/- 0.003 < 0.008 0.023 +/- 0.003 < 0.008 0.030 +/- 0.004 < 0.013 0.028 +/- 0.003 < 0.006 0.030 +/- 0.004 < 0.013 0.038 +/- 0.003 < 0.005 0.016 +/- 0.003 < 0.009 0.027 +/- 0.003 <0.016 2Q 2014 Mean +/- s.d.0.018 +/- 0.004 < 0.020 4Q 2014 Mean +/- s.d.Cumulative Average 0.024 +/-0.007 <0.016 0.023 C-10 Table 2. Airborne particulates and charcoal canisters, analyses for gross beta and iodine-1 31.Location:
P-5 Units: pCi/m 3 Collection:
Continuous, weekly exchange.Date Volume Date Volume Collected (me) Gross Beta 1-131 Collected (ms) Gross Beta 1-131 Required LLD 0.0075 0.050 0.0075 0.050 01-08-14 01-15-14 01-22-14 01-30-14 02-06-14 02-13-14 02-20-14 02-27-14 03-05-14 03-13-14 03-19-14 03-27-14 04-03-14 446 547 527 613 511 551 509 503 420 208 420 596 510 0.025 +/- 0.003 0.034 +/- 0.003 0.030 +/- 0.003 0.022 +/- 0.003 0.031 +/- 0.003 0.029 +/- 0.003 0.034 +/- 0.003 0.028 +/- 0.003 0.043 +/- 0.004 0.040 +/- 0.007 0.019 +/- 0.004 0.023 +/- 0.003 0.025 +/- 0.003< 0.011< 0.006< 0.005< 0.009< 0.012< 0.005< 0.012< 0.009< 0.006< 0.018< 0.008< 0.011< 0.010 07-10-14 07-17-14 07-23-14 07-31-14 08-07-14 08-14-14 08-21-14 08-28-14 09-04-14 09-11-14 09-18-14 09-25-14 10-02-14 547 525 439 558 509 466 498 443 498 463 458 464 470 0.018 +/- 0.003 0.021 +/- 0.003 0.026 +/- 0.004 0.020 +/- 0.003 0.030 +/- 0.003 0.021 +/- 0.003 0.021 +/- 0.003 0.027 +/- 0.003 0.027 +/- 0.003 0.026 +/- 0.003 0.016 +/- 0.003 0.028 +/- 0.003 0.029 +/- 0.003< 0.010< 0.005< 0.006< 0.007< 0.007< 0.014< 0.010< 0.015< 0.008< 0.008< 0.005< 0.008< 0.008 1Q 2014 Mean +/- s.d.04-09-14 04-17-14 04-24-14 05-01-14 05-08-14 05-15-14 05-21-14 05-28-14 06-05-14 06-12-14 06-19-14 06-26-14 07-03-14 411 562 497 490 495 573 495 559 626 536 541 549 552 0.029 +/- 0.007 0.018 +/- 0.004 0.022 +/- 0.003 0.029 +/- 0.003 0.014 +/- 0.003 0.014 +/- 0.003 0.022 +/- 0.003 0.019 +/- 0.003 0.016 +/- 0.003 0.017 +/- 0.002 0.015 +/- 0.003 0.015 +/- 0.003 0.014 +/- 0.003 0.019 +/- 0.003< 0.018< 0.011< 0.012< 0.008< 0.012< 0.007< 0.010< 0.008< 0.006< 0.006< 0.006< 0.012< 0.011< 0.013 3Q 2014 Mean +/- s.d.10-09-14 10-16-14 10-23-14 10-30-14 11-06-14 11-13-14 11-20-14 11-26-14 12-04-14 12-10-14 12-18-14 12-25-14 432 464 445 425 590 584 594 493 680 508 648 584 0.024 +/- 0.005 0.032 +/- 0.004 0.021 +/- 0.003 0.015 +/- 0.003 0.031 +/- 0.004 0.020 +/- 0.003 0.020 +/- 0.003 0.024 +/- 0.003 0.032 +/- 0.003 0.028 +/- 0.003 0.036 +/- 0.003 0.038 +/- 0.003 0.017 +/- 0.003 0.024 +/- 0.003< 0.015< 0.015< 0.011< 0.013< 0.009< 0.010< 0.008< 0.007< 0.011< 0.005< 0.012< 0.005< 0.008< 0.014 12-31-14 493 2Q 2014 Mean +/- s.d.0.018 +/- 0.004< 0.013 4Q 2014 Mean +/- s.d.Cumulative Average 0.026 +/- 0.007< 0.015 0.024 C-11 Table 2. Airborne particulates and charcoal canisters, analyses for gross beta and iodine-131.
Location:
P-6 Units: pCi/m 3 Collection:
Continuous, weekly exchange.Date Volume Date Volume Collected (ma) Gross Beta 1-131 Collected (mW) Gross Beta 1-131 Required LLD 0.0075 0.050 0.0075 0.050 01-08-14 464 01-15-14 566 01-22-14 544 01-30-14 619 02-06-14 549 02-13-14 555 02-20-14 531 02-27-14 528 03-05-14 467 03-13-14 635 03-19-14 443 03-27-14 611 04-03-14 546 0.028 +/- 0.003 < 0.011 0.033 +/- 0.003 < 0.006 0.028 +/- 0.003 < 0.005 0.023 +/- 0.003 < 0.009 0.031 +/- 0.003 < 0.011 0.032 +/- 0.003 < 0.005 0.038 +/- 0.003 < 0.012 0.030 +/- 0.003 < 0.008 0.041 +/- 0.004 < 0.005 0.029 +/- 0.003 < 0.006 0.021 +/- 0.003 < 0.007 0.026 +/- 0.003 < 0.010 0.023 +/- 0.003 < 0.010 07-10-14 07-17-14 07-23-14 07-31-14 08-07-14 08-14-14 08-21-14 08-28-14 09-04-14 09-11-14 09-18-14 09-25-14 10-02-14 536 533 463 612 537 540 554 505 549 531 524 520 544 0.017 +/- 0.003 < 0.010 0.021 +/- 0.003 < 0.005 0.026 +/- 0.003 < 0.006 0.016 +/- 0.002 < 0.006 0.026 +/- 0.003 < 0.007 0.017 +/- 0.003 < 0.012 0.018 +/- 0.003 < 0.009 0.026 +/- 0.003 < 0.014 0.023 +/- 0.003 < 0.007 0.022 +/- 0.003 < 0.007 0.014 +/- 0.003 < 0.005 0.025 +/- 0.003 < 0.007 0.024 +/- 0.003 < 0.007 1Q 2014 Mean +/- s.d.04-09-14 444 04-17-14 607 04-24-14 533 05-01-14 404 05-08-14 521 05-15-14 546 05-21-14 482 05-28-14 547 06-05-14 615 06-12-14 533 06-19-14 526 06-26-14 558 07-03-14 531 0.029 +/- 0.006 < 0.012 0.020 +/- 0.003 < 0.010 0.026 +/- 0.003 < 0.011 0.025 +/- 0.003 < 0.008 0.019 +/- 0.004 < 0.014 0.013 +/- 0.003 < 0.006 0.024 +/- 0.003 < 0.011 0.022 +/- 0.003 < 0.008 0.016 +/- 0.003 < 0.006 0.017 +/- 0.003 < 0.006 0.017 +/- 0.003 < 0.006 0.015 +/- 0.003 < 0.013 0.014 +/- 0.003 < 0.011 0.019 +/- 0.003 < 0.014 3Q 2014 Mean +/- s.d. 0.021 +/- 0.004 < 0.014 10-09-14 307 10-16-14 531 10-23-14 528 10-30-14 495 11-06-14 455 11-13-14 532 11-20-14 594 11-26-14 502 12-04-14 677 12-10-14 509 12-18-14 655 12-25-14 579 12-31-14 518 0.041 +/- 0.005 < 0.020 0.018 +/- 0.003 < 0.010 0.012 +/- 0.003 < 0.011 0.023 +/- 0.003 < 0.007 0.018 +/- 0.003 < 0.013 0.022 +/- 0.003 < 0.008 0.027 +/- 0.003 < 0.007 0.034 +/- 0.003 < 0.011 0.030 +/- 0.003 < 0.005 0.037 +/- 0.003 < 0.012 0.039 +/- 0.003 < 0.004 0.020 +/- 0.003 < 0.008 0.026 +/- 0.003 < 0.013 4Q 2014 Mean +/- s.d. 0.027 +/- 0.009 < 0.020 2Q 2014 Mean +/- s.d.0.019 +/- 0.004 < 0.014 Cumulative Average 0.024 C-12 Table 2. Airborne particulates and charcoal canisters, analyses for gross beta and iodine-1 31.Location:
P-7 Units: pCi/m 3 Collection:
Continuous, weekly exchange.Date Volume Date Volume Collected (ma) Gross Beta 1-131 Collected (mW) Gross Beta 1-131 Required LLD 0.0075 0.050 0.0075 0.050 01-08-14 01-15-14 01-22-14 01-30-14 02-06-14 02-13-14 02-20-14 02-27-14 03-05-14 03-13-14 03-19-14 03-27-14 04-03-14 444 547 530 611 531 543 575 568 458 636 495 656 588 0.027 +/- 0.003 0.030 +/- 0.003 0.027 +/- 0.003 0.021 +/- 0.003 0.028 +/- 0.003 0.030 +/- 0.003 0.027 +/- 0.003 0.026 +/- 0.003 0.033 +/- 0.004 0.026 +/- 0.003 0.014 +/- 0.003 0.020 +/- 0.002 0.022 +/- 0.003< 0.011< 0.006< 0.005< 0.009< 0.011< 0.005< 0.011< 0.008< 0.005< 0.008< 0.007< 0.010< 0.009 07-10-14 07-17-14 07-23-14 07-31-14 08-07-14 08-14-14 08-21-14 08-28-14 09-04-14 09-11-14 09-18-14 09-25-14 10-02-14 576 540 505 645 557 573 562 531 565 549 533 546 561 0.019 +/- 0.003 < 0.010 0.022 +/- 0.003 < 0.005 0.023 +/- 0.003 < 0.005 0.018 +/- 0.002 < 0.006 0.030 +/- 0.003 < 0.007 0.019 +/- 0.003 < 0.011 0.019 +/- 0.003 < 0.009 0.020 +/- 0.003 < 0.013 0.026 +/- 0.003 < 0.007 0.022 +/- 0.003 < 0.007 0.015 +/- 0.003 < 0.005 0.025 +/- 0.003 < 0.007 0.028 +/- 0.003 < 0.007 1Q 2014 Mean +/- s.d.04-09-14 04-17-14 04-24-14 05-01-14 05-08-14 05-15-14 05-21-14 05-28-14 06-05-14 06-12-14 06-19-14 06-26-14 07-03-14 493 650 573 582 561 571 503 574 650 562 568 577 566 0.025 +/- 0.005 0.016 +/- 0.003 0.024 +/- 0.003 0.023 +/- 0.003 0.014 +/- 0.002 0.013 +/- 0.002 0.019 +/- 0.003 0.019 +/- 0.003 0.019 +/- 0.003 0.016 +/- 0.002 0.016 +/- 0.003 0.010 +/- 0.003 0.013 +/- 0.003 0.022 +/- 0.003< 0.011< 0.009< 0.011< 0.007< 0.010< 0.006< 0.010< 0.008< 0.006< 0.006< 0.005< 0.012< 0.011< 0.013 3Q 2014 Mean +/- s.d.10-09-14 10-16-14 10-23-14 10-30-14 11-06-14 11-13-14 11-20-14 11-26-14 12-04-14 12-10-14 12-18-14 12-25-14 12-31-14 536 547 548 527 584 554 544 465 666 468 620 534 462 0.022 +/- 0.004 < 0.013 0.027 +/- 0.003 < 0.012 0.020 +/- 0.003 < 0.009 0.013 +/- 0.003 < 0.011 0.027 +/- 0.003 < 0.007 0.023 +/- 0.003 < 0.010 0.020 +/- 0.003 < 0.008 0.030 +/- 0.003 < 0.008 0.035 +/- 0.004 < 0.012 0.030 +/- 0.003 < 0.006 0.040 +/- 0.004 < 0.013 0.048 +/- 0.003 < 0.005 0.021 +/- 0.003 < 0.009 0.027 +/- 0.003 < 0.015 2Q 2014 Mean +/- s.d.0.017 +/- 0.004< 0.013 4Q 2014 Mean +/- s.d.Cumulative Average 0.028 +/-0.009 <0.015 0.023 C-13 Table 2. Airborne particulates and charcoal canisters, analyses for gross beta and iodine-1 31.Location:
P-35 Units: pCi/mr 3 Collection:
Continuous, weekly exchange.Date Volume Date Volume Collected (m") Gross Beta 1-131 Collected (m") Gross Beta 1-131 Required LLD 0.0075 0.050 0.0075 0.050 01-08-14 01-15-14 01-22-14 01-30-14 02-06-14 02-13-14 02-20-14 02-27-14 03-05-14 03-13-14 03-19-14 03-27-14 04-03-14 460 558 543 632 543 560 547 530 457 228 468 621 548 0.027 +/- 0.003 0.039 +/- 0.003 0.027 +/- 0.003 0.021 +/- 0.003 0.030 +/- 0.003 0.031 +/- 0.003 0.035 +/- 0.003 0.031 +/- 0.003 0.039 +/- 0.004 0.033 +/- 0.006 0.019 +/- 0.003 0.024 +/- 0.003 0.023 +/- 0.003< 0.022< 0.009< 0.013< 0.007< 0.008< 0.011< 0.007< 0.011< 0.008< 0.017< 0.017< 0.009< 0.010 07-10-14 07-17-14 07-23-14 07-31-14 08-07-14 08-14-14 08-21-14 08-28-14 09-04-14 09-11-14 09-18-14 09-25-14 10-02-14 644 601 542 724 611 636 635 584 642 626 603 618 639 0.015 +/- 0.002 < 0.009 0.018 +/- 0.003 < 0.009 0.022 +/- 0.003 < 0.009 0.016 +/- 0.002 < 0.009 0.022 +/- 0.003 < 0.010 0.018 +/- 0.002 < 0.011 0.018 +/- 0.003 < 0.010 0.022 +/- 0.003 < 0.012 0.024 +/- 0.003 < 0.016 0.019 +/- 0.002 < 0.010 0.012 +/- 0.002 < 0.014 0.022 +/- 0.003 < 0.010 0.022 +/- 0.002 < 0.011 1Q 2014 Mean +/- s.d.04-09-14 04-17-14 04-24-14 05-01-14 05-08-14 05-15-14 05-21-14 05-28-14 06-05-14 06-12-14 06-19-14 06-26-14 07-03-14 459 615 531 551 538 593 538 560 650 573 574 548 605 0.029 +/- 0.006 0.017 +/- 0.003 0.025 +/- 0.003 0.029 +/- 0.003 0.012 +/- 0.003 0.014 +/- 0.003 0.022 +/- 0.003 0.019 +/- 0.003 0.017 +/- 0.003 0.015 +/- 0.002 0.015 +/- 0.003 0.013 +/- 0.003 0.013 +/- 0.003 0.019 +/- 0.002< 0.022< 0.006< 0.015< 0.023< 0.009< 0.014< 0.013< 0.016< 0.013< 0.009< 0.007< 0.012< 0.017< 0.010 3Q2014 Mean+/-s.d.10-09-14 10-16-14 10-23-14 10-30-14 11-06-14 11-13-14 11-20-14 11-26-14 12-04-14 12-10-14 12-18-14 12-25-14 12-31-14 612 622 629 602 621 616 589 508 696 505 658 583 507 0.019 +/- 0.003 < 0.016 0.024 +/- 0.003 < 0.009 0.016 +/- 0.002 < 0.005 0.011 +/-0.002 < 0.004 0.023 +/- 0.003 < 0.011 0.019 +/- 0.002 < 0.005 0.019 +/- 0.002 < 0.008 0.024 +/- 0.003 < 0.010 0.033 +/- 0.003 < 0.012 0.030 +/- 0.003 < 0.009 0.033 +/- 0.003 < 0.009 0.040 +/- 0.003 < 0.004 0.017 +/- 0.003 < 0.013 0.027 +/- 0.003 < 0.012 2Q 2014 Mean +/- s.d.0.018 +/- 0.005< 0.023 4Q 2014 Mean +/- s.d.Cumulative Average 0.024 +/- 0.008 <0.013 0.023 C-14 Table 3. Airborne particulates, analyses for gamma-emitting isotopes.Collection:
Quarterly Composite Units: pCi/m 3 Location PE-1 Quarter 1st Qtr. 2nd Qtr. 3rd Qtr. 4th Qtr. Req. LLD Lab Code PEAP- 1809 PEAP- 3783 PEAP- 5999 PEAP- 7466 Vol. (M 3) 6591 7198 7101 7477 Be-7 0.061 +/- 0.010 0.060 +/- 0.010 0.054 +/- 0.009 0.045 +/- 0.008 -Co-58 < 0.0004 < 0.0002 < 0.0004 < 0.0004 -Co-60 < 0.0002 < 0.0004 < 0.0004 < 0.0002 -Cs-1 34 < 0.0005 < 0.0004 < 0.0004 < 0.0005 0.037 Cs-1 37 < 0.0003 < 0.0003 < 0.0004 < 0.0004 0.045 Location PE-3 Lab Code PEAP- 1810 PEAP- 3785 PEAP- 6000 PEAP- 7467 Vol. (M 3) 6718 7443 7719 8376 Be-7 0.058 +/- 0.011 0.058 +/- 0.008 0.051 +/- 0.009 0.051 +/- 0.008 -Co-58 < 0.0004 < 0.0003 < 0.0003 < 0.0004 -Co-60 < 0.0002 < 0.0003 < 0.0003 < 0.0004 -Cs-1 34 < 0.0005 < 0.0004 < 0.0004 < 0.0003 0.037 Cs-137 < 0.0003 < 0.0003 < 0.0004 < 0.0003 0.045 Location PE-4 Lab Code PEAP- 1811 PEAP- 3786 PEAP- 6001 PEAP- 7468 Vol. (M 3) 6500 6555 6644 6761 Be-7 0.058 +/- 0.009 0.069 +/- 0.011 0.061 +/- 0.010 0.056 +/- 0.010 -Co-58 < 0.0003 < 0.0004 < 0.0003 < 0.0004 -Co-60 < 0.0002 < 0.0004 < 0.0004 < 0.0004 -Cs-134 < 0.0006 < 0.0004 < 0.0006 < 0.0005 0.037 Cs-1 37 < 0.0003 < 0.0003 < 0.0005 < 0.0003 0.045 Location PE-5 Lab Code PEAP- 1812 PEAP- 3787 PEAP- 6002 PEAP- 7469 Vol. (M 3) 6361 6887 6338 6940 Be-7 0.065 +/- 0.012 0.069 +/- 0.009 0.061 +/- 0.010 0.061 +/- 0.008 -Co-58 < 0.0004 < 0.0003 < 0.0005 < 0.0004 -Co-60 < 0.0002 < 0.0004 < 0.0002 < 0.0004 -Cs-134 < 0.0004 < 0.0005 < 0.0004 < 0.0003 0.037 Cs-137 < 0.0004 < 0.0006 < 0.0005 < 0.0003 0.045 C-15 Table 3. Airborne particulates, analyses for gamma-emitting isotopes.Collection:
Quarterly Composite Units: pCi/mr 3 Location PE-6 Quarter 1st Qtr. 2nd Qtr. 3rd Qtr. 4th Qtr. Req. LLD Lab Code PEAP- 1813 PEAP- 3788 PEAP- 6003 PEAP- 7471 Vol. (M 3) 7058 6845 6947 6993 Be-7 0.057 +/- 0.008 0.066 +/- 0.011 0.059 +/- 0.008 0.057 +/- 0.008 -Co-58 < 0.0004 < 0.0003 < 0.0001 < 0.0003 -Co-60 < 0.0003 < 0.0004 < 0.0004 < 0.0004 -Cs-1 34 < 0.0004 < 0.0005 < 0.0003 < 0.0005 0.037 Cs-137 < 0.0004 < 0.0003 < 0.0002 < 0.0004 0.045 Location PE-7 Lab Code PEAP- 1814 PEAP- 3789 PEAP- 6004 PEAP- 7472 Vol. (M 3) 7182 7431 7243 7055 Be-7 0.054 +/- 0.007 0.057 +/- 0.009 0.060 +/- 0.010 0.057 +/- 0.009 -Co-58 < 0.0003 < 0.0003 < 0.0005 < 0.0003 -Co-60 < 0.0003 < 0.0003 < 0.0004 < 0.0003 -Cs-1 34 < 0.0004 < 0.0005 < 0.0005 < 0.0004 0.037 Cs-1 37 < 0.0003 < 0.0004 < 0.0003 < 0.0003 0.045 Location PE-35 Lab Code PEAP- 1815 PEAP- 3790 PEAP- 6005 PEAP- 7473 Vol. (M 3) 6695 7338 8106 7747 Be-7 0.057 +/- 0.012 0.064 +/- 0.010 0.058 +/- 0.010 0.044 +/- 0.007 -Co-58 < 0.0009 < 0.0003 < 0.0002 < 0.0004 -Co-60 < 0.0007 < 0.0004 < 0.0004 < 0.0002 -Cs-1 34 < 0.0007 < 0.0005 < 0.0005 < 0.0003 0.037 Cs-1 37 < 0.0006 < 0.0003 < 0.0003 < 0.0004 0.045 C-16 Table 4. Lake water, analyses for gross beta and gamma emitting isotopes.Location:
P-28 Collection:
Monthly composites Units: pCi/L Lab Code Start Date End Date Gross beta Mn-54 Fe-59 Co-58 Co-60 Zn-65 Zr-95 Nb-95 Cs-1 34 Cs-1 37 Ba-140 La-1 40 Lab Code Start Date End Date Gross beta Mn-54 Fe-59 Co-58 Co-60 Zn-65 Zr-95 Nb-95 Cs-1 34 Cs-1 37 Ba-140 La-140 Lab Code Start Date End Date Gross beta Mn-54 Fe-59 Co-58 Co-60 Zn-65 Zr-95 Nb-95 Cs- 134 Cs- 137 Ba-140 La- 140 PELW- 354 12-23-13 01-30-14< 1.9< 3.2< 8.9< 3.4< 4.9< 8.2< 8.7< 6.9< 4.7* 4.0< 27.7< 6.6 PELW- 2396 04-24-14 05-27-14 1.5 +/- 0.4< 2.1< 5.2< 2.8< 2.0< 2.2< 5.3< 3.6< 2.4< 2.9< 19.0< 2.8 PELW- 5172 08-28-14 09-25-14 1.5 +/- 0.6< 1.2< 4.5< 2.3< 1.7< 4.1< 3.7< 3.3< 3.0< 3.6< 15.7< 3.3 PELW- 760 02-27-14 02-27-14 2.5 +/- 0.8< 2.6< 5.8< 2.8< 2.0< 1.5< 3.5< 3.0< 2.8< 1.9< 18.8< 3.1 PELW- 3105 05-27-14 06-30-14 3.2 +/- 1.1< 2.2< 2.3< 1.3< 2.3< 4.7< 3.8< 4.6< 3.9< 2.9< 13.5< 4.6 PELW- 6244 09-25-14 10-30-14 2.6 +/- 0.9< 2.2< 3.9< 3.0< 1.9< 6.0< 4.7< 5.0< 3.2* 2.4< 27.0< 4.3 PELW- 1210 02-27-14 03-27-14 2.3 +/- 0.8< 2.1< 4.4< 2.4< 1.5< 1.9< 5.2< 2.3< 2.2< 2.6< 16.3< 2.3 PELW- 3930 06-30-14 07:31-14 1.0 +/- 0.4< 2.1< 4.0< 1.6< 2.3< 2.5< 2.8< 1.5< 2.5< 1.5< 22.3< 5.1 PELW- 6811 10-30-14 11-26-14 2.6 +/- 0.8< 1.6< 4.8< 2.6< 1.2< 2.1< 2.5< 2.8< 2.6< 3.7< 18.5< 4.0 PELW- 1749 03-27-14 04-24-14 2.5 +/- 0.9< 1.9< 3.5< 1.8< 2.0< 2.1< 4.1< 2.5< 2.4< 2.5< 12.2< 4.1 PELW- 4561 07-31-14 08-28-14, 2.5 +/- 0.8< 2.5< 5.6< 2.2< 2.3< 4.8< 4.5< 2.4< 3.1< 2.8< 29.4< 6.5 PELW- 7253 11-26-14 12-29-14 1.6 +/- 0.8< 1.8< 5.4< 3.5< 2.0< 2.8< 6.0< 4.0< 3.0< 2.3< 20.5< 4.9 Req. LLD 3.0 11 22 1.1 22 22 22 11 13" 45 11 Req. LLD 3.0 11 22 11 11 22 22 11 11 13 45 11 Req. LLD 3.0 11 22 11 11 22 22 11 11 13 45 11 a Grab sample.C-17 Table 4. Lake water, analyses for gross beta and gamma emitting isotopes.Location:
P-34 Collection:
Monthly composites Units: pCi/L Lab Code Start Date End Date Gross beta Mn-54 Fe-59 Co-58 Co-60 Zn-65 Zr-95 Nb-95 Cs-1 34 Cs-I 37 Ba- 140 La-140 Lab Code Start Date End Date Gross beta Mn-54 Fe-59 Co-58 Co-60 Zn-65 Zr-95 Nb-95 Cs- 134 Cs-1 37 Ba-140 La-140 Lab Code Start Date End Date Gross beta Mn-54 Fe-59 Co-58 Co-60 Zn-65 Zr-95 Nb-95 Cs-134 Cs-1 37 Ba- 140 La- 140 PELW- 355 12-23-13 01-30-14 3.0 +/- 1.0 PELW- 761 01-30-14 02-27-14 2.3 +/- 0.8< 2.8< 3.8< 2.5< 2.5< 3.5< 4.2< 2.5< 2.3< 3.3< 13.3< 4.4 1.8 5.0 2.1 2.2 4.2 4.9 3.2 2.5 2.1 13.8 3.6 PELW- 2397 04-24-14 05-27-14 1.7 +/- 0.4< 2.9< 4.3< 1.5< 1.9< 3.4< 3.7< 1.7< 2.7< 2.6< 14.4< 3.7 PELW- 5173 08-28-14 09-25-14 1.9 +/- 0.6< 3.6< 5.4< 1.9< 1.9< 2.4< 4.1< 3.5< 3.9< 2.0< 17.4< 2.2 PELW- 3106 05-27-14 06-30-14 2.0 +/- 0.9< 2.2< 4.4< 2.0< 2.2< 5.0< 4.4< 2.6< 2.8< 3.1< 16.2< 3.6 PELW- 6245 09-25-14 10-30-14 2.4 +/- 0.8< 3.0< 5.0< 2.9< 1.5< 3.3< 4.5< 2.7< 2.3< 2.9< 29.6< 3.5 PELW- 1211 02-27-14 03-27-14< 1.0< 3.2< 3.1< 2.6< 1.4< 4.8< 5.0< 3.3< 3.1< 3.2< 10.2< 2.1 PELW- 3931 06-30-14 07-31-14 1.0 +/- 0.4< 2.1< 5.0< 1.6< 1.8< 2.8< 4.3< 3.5< 3.0< 2.9< 18.8< 2.8 PELW- 6812 10-30-14 11-26-14 2.3 +/- 0.7< 1.3< 4.9< 2.4< 1.1< 4.7< 3.5< 2.6< 2.5< 2.9< 21.0< 3.2 PELW- 1750 03-27-14 04-24-14 2.2 +/- 0.8< 2.3< 2.0< 1.9< 2.1< 2.5< 4.2< 2.4< 2.5< 2.2< 14.6< 1.5 PELW- 4562 07-31-14 08-28-14 2.1 +/- 0.7< 2.1< 7.0< 2.2< 2.7< 5.0< 5.2< 3.6< 3.0< 3.0< 32.2< 4.0 PELW- 7254 11-26-14 12-29-14 2.5 +/- 0.7< 1.6< 3.3< 2.0< 1.9< 3.7< 4.8< 2.7< 2.1< 1.7< 23.2< 4.2 Req. LLD 3.0 11 22 11 11 22 22 11 11 13 45 11 Req. LLD 3.0 11 22 11 11 22 22 11 11 13 45 11 Req. LLD 3.0 11 22 11 11 22 22 11 11 13 45 11 C-18 Table 4. Lake water, analyses for gross beta and gamma emitting isotopes.Location:
P-36 Collection:
Monthly composites Units: pCi/L Lab Code Start Date End Date Gross beta Mn-54 Fe-59 Co-58 Co-60 Zn-65 Zr-95 Nb-95 Cs-1 34 Cs- 137 Ba- 140 La- 140 Lab Code Start Date End Date Gross beta Mn-54 Fe-59 Co-58 Co-60 Zn-65 Zr-95 Nb-95 Cs-1 34 Cs-1 37 Ba- 140 La-140 Lab Code Start Date End Date Gross beta Mn-54 Fe-59 Co-58 Co-60 Zn-65 Zr-95 Nb-95 Cs-1 34 Cs-1 37 Ba- 140 La- 140 PELW- 356 12-23-13 01-30-14< 1.8< 2.3< 2.8< 2.8< 2.2< 3.2< 4.5< 2.3< 2.7< 3.5< 18.0< 2.1 PELW- 2398 04-24-14 05-27-14 1.3 +/- 0.4< 2.6< 2.9* 1.6< 1.9< 2.9< 5.0< 3.6< 2.5< 2.9* 19.4* 4.3 PELW- 5175 08-28-14 09-25-14 1.0 +/- 0.5< 2.6< 8.5< 2.8< 2.4< 4.3< 7.6< 3.5< 4.2< 2.7< 15.5< 2.9 PELW- 762 01-30-14 02-27-14 1.6 +/- 0.8* 1.5* 3.1* 2.1< 2.1* 5.1< 4.0* 3.0* 2.5* 2.4* 17.6* 3.8 PELW- 3107 05-27-14 06-30-14 2.2 +/- 1.0< 2.7< 4.0< 3.1< 2.1< 3.5< 5.2< 1.3< 2.8< 1.6< 16.0< 2.8 PELW- 6246 09-25-14 10-30-14 2.2 +/- 0.8< 2.7< 5.3< 1.4< 1.9< 2.0< 4.0< 2.9< 2.6< 2.9< 20.4< 7.5 PELW- 1212 02-27-14 03-27-14 2.0 +/- 0.7< 2.3< 3.7< 2.7< 1.9< 1.6< 4.9< 2.6< 2.6< 2.5< 13.5< 4.7 PELW- 3933 06-30-14 07-31-14 1.1 +/- 0.4< 2.4< 4.5< 1.3< 1.8< 3.0<4.1< 2.5< 1.9< 2.0< 33.8< 5.2 PELW- 6813 10-30-14 11-26-14 3.0 +/- 0.8< 2.2< 3.1< 1.3< 2.0< 5.2< 3.1< 3.0< 2.6< 2.6< 23.7< 4.9 PELW- 1751 03-27-14 04-24-14 1.8 +/- 0.8< 2.4< 2.0< 3.1< 1.3< 2.6< 4.1< 2.7< 2.7< 3.3< 16.1< 4.8 PELW- 4563 07-31-14 08-28-14 2.0 +/- 0.8< 2.4< 5.7< 2.2< 2.9< 2.6< 4.1< 2.1< 2.6< 1.9< 17.6< 4.2 PELW- 7255 11-26-14 12-29-14 2.2 +/- 0.8< 2.0< 3.7< 2.8< 1.3< 3.0< 2.9< 2.4< 2.3< 2.6< 15.6< 3.5 Req. LLD 3.0 11 22 11 11 22 22 11 13 45 11 Req. LLD 3.0 11 22 11 11 22 22 11 11 13 45 11 Req. LLD 3.0 11 22 11 11 22 22 11 11 13 45 11 C-19 Table 4. Lake water, analyses for gross beta and gamma emitting isotopes.Location:
P-59 Collection:
Monthly composites Units: pCi/L Lab Code Start Date End Date Gross beta Mn-54 Fe-59 Co-58 Co-60 Zn-65 Zr-95 Nb-95 Cs-1 34 Cs- 137 Ba- 140 La-140 Lab Code Start Date End Date Gross beta Mn-54 Fe-59 Co-58 Co-60 Zn-65 Zr-95 Nb-95 Cs-1 34 Cs-1 37 Ba-140 La-140 Lab Code Start Date End Date Gross beta Mn-54 Fe-59 Co-58 Co-60 Zn-65 Zr-95 Nb-95 Cs- 134 Cs-1 37 Ba-140 La-140 NS a 01-30-14 PELW- 2399 04-24-14 05-27-14 1.5 +/- 0.4< 3.2< 2.9< 2.3< 1.8< 4.5< 3.9< 3.4< 3.4< 2.8< 23.3< 4.4 PELW- 5176 08-28-14 09-25-14 1.0 +/- 0.5< 2.3< 5.9< 1.7< 2.8< 2.6< 4.1< 3.4< 2.4< 3.4< 13.5< 4.0 NS a 02-27-14 PELW- 3108 05-27-14 06-30-14 2.4 +/- 0.9< 2.6< 3.1< 1.5< 3.1< 2.0< 5.4< 2.4< 2.9< 2.8< 11.4< 3.2 PELW- 6247 09-25-14 10-30-14 3.4 +/- 0.8< 3.3< 8.7< 3.8< 5.8< 6.6< 7.8< 5.0< 5.2< 3.4< 25.2< 3.7 NS a 03-27-14 PELW- 3934 06-30-14 07-31-14 1.2 +/- 0.4< 1.7< 5.5< 1.8< 1.5< 2.6< 2.9< 2.5< 2.0< 1.5< 29.4< 6.0 PELW- 6814 10-30-14 11-26-14 2.6 +/- 0.7 PELW- 1752 04-24-14 2.6 +/- 0.8< 3.0< 2.8< 1.5< 1.4< 4.3< 3.6< 2.4< 3.1< 3.0< 11.3< 1.8 PELW- 4565 07-31-14 08-28-14 2.5 +/- 0.7< 2.2< 2.5< 1.5< 1.8< 3.2< 3.8< 3.5< 2.4< 2.9< 20.5< 4.3 PELW- 7256 11-26-14 12-29-14 1.6 +/- 0.7< 2.2< 5.1< 2.2< 1.4< 5.3< 3.4< 3.2< 3.1< 3.0< 25.2< 5.2 Req. LLD 3.0 11 22 11 22 22 11 11 13 45 11 Req. LLD 3.0 11 22 11 11 22 22 11 11 13 45 11 Req. LLD 3.0 11 22 11 11 22 22 11 11 13 45 11< 1.7< 3.7< 2.2< 1.6< 1.7< 3.9< 3.9< 2.4< 2.9< 20.9< 2.1 8 No sample available, shoreline inaccessible.
C-20 Table 4. Lake water, analyses for gross beta and gamma emitting isotopes.Location:
P-60 Collection:
Monthly composites Units: pCi/L Lab Code Start Date End Date Gross beta Mn-54 Fe-59 Co-58 Co-60 Zn-65 Zr-95 Nb-95 Cs-1 34 Cs-1 37 Ba-140 La-140 Lab Code Start Date End Date Gross beta Mn-54 Fe-59 Co-58 Co-60 Zn-65 Zr-95 Nb-95 Cs-1 34 Cs-137 Ba- 140 La-140 Lab Code Start Date End Date Gross beta Mn-54 Fe-59 Co-58 Co-60 Zn-65 Zr-95 Nb-95 Cs-1 34 Cs-1 37 Ba-140 La-140 NS a 01-30-14 NS a 02-27-14 NS a 03-27-14 PELW- 2400 04-24-14 05-27-14 1.5 +/- 0.5< 1.5< 8.0< 1.6< 3.0< 3.3< 4.1< 2.5< 3.7< 3.6< 19.4< 3.8 PELW- 5177 08-28-14 09-25-14 2.3 +/- 0.8< 2.5< 5.9< 2.1< 1.5< 4.3< 5.1< 3.6< 2.8< 2.3< 19.4< 2.7 PELW- 3109 05-27-14 06-30-14 2.9 +/- 1.0< 1.8< 3.7< 1.7< 2.4< 3.7< 3.9< 3.2< 3.1< 3.0< 21.0< 4.9 PELW- 6249 09-25-14 10-30-14 2.5 +/- 0.8< 2.1< 5.3< 2.2< 2.4< 3.0< 3.6< 3.2< 2.7< 2.7< 13.9< 3.0 PELW- 3935 06-30-14 07-31-14 2.2 +/- 0.5< 2.8< 3.9< 2.3< 1.6< 2.8< 2.9< 3.0< 3.0< 2.8< 33.7< 7.9 PELW- 6815 10-30-14 11-26-14 3.4 +/- 0.8< 2.6< 3.9< 2.5< 1.7< 2.5< 4.8< 3.4< 2.8< 2.4< 26.0< 6.0 PELW- 1753 04-24-14 2.2 +/- 0.8< 1.7< 3.9< 1.6< 2.3< 3.3< 4.6< 2.8< 2.6< 1.6< 18.8< 4.7 PELW- 4566 07-31-14 08-28-14 4.5 +/- 0.9< 2.5< 5.2< 2.4< 2.4< 3.0< 3.8< 3.1< 2.5< 2.6< 26.8< 5.2 PELW- 7258 11-26-14 12-29-14 3.6 +/- 0.8< 3.1< 3.3< 2.7< 2.8< 4.6< 2.7< 3.1< 2.7< 3.1< 21.4< 5.9 Req. LLD 3.0 11 22 11 11 22 22 11 13 45 11 Req. LLD 3.0 11 22 11 11 22 22 11 11 13 45 11 Req. LLD 3.0 11 22 11 11 22 22 11 11 13 45 11' No sample available, shoreline inaccessible.
C-21 Table 4. Lake Water, analysis for tritium.Collection:
Quarterly composites of monthly collections.
Units: pCi/L Required limit of detection:
1500 pCi/L Location P-28 Period 1st Qtr. 2nd Qtr. 3rd Qtr. 4th Qtr.Lab Code PELW- 1352 PELW- 3328 PELW- 5441 PELW- 7315 H-3 < 149 < 137 < 158 < 177 Location P-34 Period 1st Qtr. 2nd Qtr. 3rd Qtr. 4th Qtr.Lab Code PELW- 1353 PELW- 3329 PELW- 5442 PELW- 7316 H-3 < 149 < 137 < 158 < 177 Location P-36 Period 1st Qtr. 2nd Qtr. 3rd Qtr. 4th Qtr.Lab Code PELW- 1354 PELW- 3330 PELW- 5443 PELW- 7317 H-3 < 149 < 137 < 158 < 177 Location P-59 Period 1st Qtr. 2nd Qtr. 3rd Qtr. 4th Qtr.Lab Code NA a PELW- 3331 PELW- 5445 PELW- 7318 H-3 < 137 < 158 < 177 Location P-60 Period 1st Qtr. 2nd Qtr. 3rd Qtr. 4th Qtr.Lab Code NA a PELW- 3332 PELW- 5444 PELW- 7319 H-3 < 137 < 158 < 177 a No sample available, shoreline frozen.C-22 Table 5. Milk, analyses for iodine-1 31 and gamma-emitting isotopes.Collection:
Semimonthly during grazing season, monthly at other times.Collection Lab Concentration (pCiIL)Date Code 1-131 Cs-1 34 Cs-1 37 Ba-1 40 La-140 K-40 Required LLD P-1 8 01-06-14 02-03-14 03-03-14 04-07-14 04-21-14 05-05-14 05-19-14 06-03-14 06-16-14 07-07-14 07-22-14 08-04-14 08-18-14 09-02-14 09-15-14 10-06-14 10-20-14 11-03-14 12-01-14 (pCi/L)NDa NDa NDa PEMI- 1410 PEMI- 1633 PEMI- 1997 PEMI- 2190 PEMI- 2510 b PEMI- 2855 PEMI- 3247 PEMI- 3739 PEMI- 4030 PEMI- 4352 PEMI- 4639 PEMI- 4878 PEMI- 5379 PEMI- 5876 PEMI- 6275 PEMI- 6808 PEMI- 72 PEMI- 432 PEMI- 823 PEMI- 1411 PEMI- 1634 PEMI- 1998 PEMI- 2191 PEMI- 2511 PEMI- 2856 PEMI- 3248 PEMI- 3740 PEMI- 4031 PEMI- 4354 PEMI- 4640 PEMI- 4879 PEMI- 5380 PEMI- 5877 PEMI- 6276 PEMI- 6809 0.8 11 13 45 11 P-1 9< 0.4< 0.3< 0.2<0.3< 0.3<0.5< 0.4< 0.4< 0.3< 0.5< 0.4<0.3< 0.4< 0.3<0.5<0.3< 0.4<0.5<0.3< 0.4< 0.4< 0.2< 0.3< 0.3< 0.4< 0.2< 0.3< 0.4< 0.4< 0.3< 0.4<0.5<0.3< 0.3< 0.4<4.1<3.6<4.1< 5.8< 2.8< 2.9< 4.4<2.7< 3.8< 3.2< 3.6< 3.2<2.8< 3.2< 11.4< 3.7< 3.0< 2.9< 2.7< 4.2<4.2<3.6< 3.6< 3.3< 2.9< 4.6<2.9<4.3< 2.8< 3.4< 2.6< 3.0<2.8<2.9< 3.8< 4.4< 4.0<4.0< 7.2<2.7< 3.7<4.3<2.6< 3.9< 3.8< 3.6< 3.2< 3.8< 3.6< 4.2< 3.7<3.1< 3.3< 3.5< 4.2<4.3< 3.7< 4.9< 3.5< 2.7<4.5< 3.0<4.6< 3.6< 3.6< 2.2< 2.8<3.5<3.1<4.7< 20.5< 20.9< 31.7< 17.3< 57.4< 13.8< 26.1< 32.0< 16.8< 20.3< 21.4< 21.3< 17.3< 28.1< 17.0< 28.7< 16.5< 19.0< 16.6< 16.0< 22.5< 19.1< 18.0< 27.4< 17.1< 21.0< 25.1< 31.3< 31.7< 17.9< 16.5< 23.7< 24.5< 14.3< 23.1< 2.6< 1.9<5.5< 6.4< 13.1<2.7< 5.0<5.3< 3.6< 2.2<2.5< 3.3<3.7<3.1<2.1< 2.3< 3.6< 3.3< 3.5<2.7< 3.5< 3.3<2.3<3.6< 3.4< 3.5< 5.2< 8.3< 4.3< 1.9<2.8< 3.9< 3.8< 3.0< 5.4 1822 +/- 126 1840 +/- 125 1864 +/- 120 1632 +/- 176 1408 +/- 89 1887 +/- 112 1785 +/- 126 1772 +/- 97 1676 +/- 110 1860 +/- 124 1731 +/-124 1750 +/- 109 1658 +/- 113 1454 +/- 100 1493 +/- 111 1397 +/- 107 1376 +/- 110 1397 +/- 101 1232 +/- 91 1322 +/- 110 1224 +/- 107 1238 +/- 96 1107 +/- 105 1361 +/- 110 1376 +/- 93 1222 +/- 122 1247 +/- 88 1206 +/- 108 1255 +/- 112 1336 +/- 116 1272 +/- 82 1246 +/- 100 1350 +/- 101 1254 +/- 93 1300 +/- 105 01-05-14 02-03-14 03-03-14 04-07-14 04-21-14 05-05-14 05-19-14 06-03-14 06-16-14 07-07-14 07-22-14 08-04-14 08-18-14 09-02-14 09-15-14 10-06-14 10-20-14 11-03-14 12-01-14 a ND = No data, no milk available.
b MDA for Ba-140 and La-1 40 not reached due to delay in counting.C-23 Table 5. Milk, analyses for iodine-1 31 and gamma-emitting isotopes (continued).
Collection:
Semimonthly during grazing season, monthly at other times.Collection Lab Concentration (pCi/L)Date Code 1-131 Cs-1 34 Cs-1 37 Ba-1 40 La-1 40 K-40 Required LLD (pCi/L)0.8 11 13 45 11 P-41 01-06-14 02-03-14 03-03-14 04-07-14 04-21-14 05-06-14 05-19-14 06-03-14 06-16-14 07-07-14 07-22-14 08-05-14 08-18-14 09-02-14 09-15-14 10-06-14 10-20-14 11-03-14 12-01-14 NDa ND ND ND ND PEMI- 1999 PEMI- 2192 PEMI- 2512 PEMI- 2857 PEMI- 3249 PEMI- 3741 PEMI- 4032 PEMI- 4355 PEMI- 4641 PEMI- 4881 ND ND ND ND< 0.2<0.3< 0.4< 0.4< 0.2< 0.4< 0.4< 0.4< 0.3<0.3< 3.9<5.1< 3.0< 3.7< 3.7<2.7< 4.0<3.1< 4.4< 2.5< 3.7< 4.7< 2.7< 3.0< 3.2<3.3< 2.2< 3.7< 3.5< 3.5< 35.5< 15.0< 24.4< 17.4< 30.9< 26.4< 31.6< 30.8< 20.0< 17.4< 3.7<2.7< 3.8< 3.3< 6.2< 4.9< 5.5< 3.9< 2.2<3.6 1704 +/- 114 2009 +/- 142 1679 +/- 105 1490 +/- 100 1727 +/- 120 1535 +/- 88 1667 +/- 107 1863 +/- 117 1656 +/- 126 1479 +/- 90 P-51 01-05-14 02-03-14 03-03-14 04-07-14 04-21-14 05-05-14 05-19-14 06-03-14 06-16-14 07-07-14 07-22-14 08-04-14 08-18-14 09-02-14 09-15-14 10-06-14 10-20-14 11-03-14 12-01-14 PEMI- 73 PEMI- 433 PEMI- 824 PEMI- 1412 PEMI- 1635 PEMI- 2000 PEMI- 2193 PEMI- 2513 PEMI- 2858 PEMI- 3250 PEMI- 3743 PEMI- 4033 PEMI- 4356 PEMI- 4642 PEMI- 4882 PEMI- 5381 PEMI- 5878 PEMI- 6277 PEMI- 6810< 0.4< 0.4< 0.4< 0.2< 0.2< 0.2< 0.3<0.3<0.5< 0.4< 0.3< 0.3< 0.5<0.3< 0.3< 0.3< 0.4< 0.5< 0.4<2.7< 3.2< 2.7< 3.7< 3.3< 3.2<3.1< 3.5<4.1<4.0< 3.0< 3.6< 3.0< 3.4< 2.4< 2.8<3.1<3.1<3.1<3.1<3.3< 2.9< 4.2< 3.3< 3.3< 3.9< 3.9< 3.9< 2.4<3.1< 3.4< 3.6<2.7< 2.8< 3.0< 4.4<4.1< 3.8< 19.4< 13.1< 16.4< 21.0< 19.7< 24.5< 20.7< 27.8< 28.1< 33.5< 29.0< 12.7< 29.8< 16.6< 17.0< 17.1< 37.2< 18.8< 18.0< 2.0< 4.2< 2.4< 3.5<2.9< 3.8< 3.8< 3.7< 1.8< 4.2<7.1<2.7< 4.9< 3.3<2.7< 3.0<6.2<3.1<4.3 1397 +/- 94 1428 +/- 105 1365 +/- 91 1298 +/- 115 1380 +/- 120 1334 +/- 97 1305 +/- 97 1366 +/- 114 1383 +/- 123 1296 +/- 102 1238 +/- 75 1345 +/- 100 1442 +/- 108 1361 +/- 108 1347 +/- 80 1289 +/- 98 1351 +/-105 1202 +/- 103 1370 +/- 97 a ND = No data, no milk available.
C-24 Table 7. Food Products, analyses for gamma emitting isotopes.Collection:
Monthly Location:
P-2 Units: pCi/kg wet Lab Code Date Collected Sample Type Be-7 K-40 Co-58 Co-60 1-131 Cs- 134 Cs-1 37 Lab Code Date Collected Sample Type Be-7 K-40 Co-58 Co-60 1-131 Cs-1 34 Cs- 137 PEVE- 3838 07-28-14 Mustard 378 +/- 129 4006 +/- 321< 11.7< 6.9< 24.9< 8.6< 10.3 PEVE- 4401 08-21-14 Turnips 627 +/- 91 5161 +/- 267< 7.8< 8.1< 18.3< 6.2< 7.8 PEVE- 5038 09-18-14 Collard Greens 325 +/- 87 3676 +/- 262< 5.3< 7.4< 16.5< 6.5< 8.3 PEVE- 5417 10-07-14 Collard Greens 389 +/- 119 3461 +/- 272< 8.0< 5.0< 25.0< 10.0< 6.0 2796 +/-86 247 10.8 10.4 19.6 7.4 7.8 PEVE- 3839 07-28-14 Collard Greens PEVE- 4402 08-21-14 Swiss Chard 686 +/- 135 5829 +/- 366< 9.8< 12.0< 26.2< 9.7< 13.4 PEVE- 3840 07-28-14 Turnips 457 +/- 85 2802 +/- 213< 4.2< 5.7< 17.2< 6.2< 7.5 PEVE- 4403 08-21-14 Mustard PEVE- 4400 08-21-14 Collard Greens 188 +/- 81 3423 +/- 256< 5.5< 6.9< 26.1< 7.7< 8.6 PEVE- 5037 09-18-14 Swiss Chard 614 +/- 134 5533 +/- 371< 11.4< 8.3< 21.0< 9.5< 12.5 PEVE- 5416 10-07-14 Mustard Greens 267 +/-3491 +/-Req. LLD 45 45 60 75 196 6.5 4.0 21.8 6.6 7.8 Req. LLD 45 45 60 Lab Code Date Collected Sample Type Be-7 K-40 Co-58 Co-60 1-131 Cs-1 34 Cs-1 37 PEVE- 5039 09-18-14 Mustard Greens 799 +/- 155 4307 +/- 317< 8.0< 4.9< 40.1< 12.1< 11.5 PEVE- 5415 10-07-14 Turnip Greens 669 +/-5571 +/-141 357 9.7 10.4 33.3 12.3 9.4 838 +/-5243 +/-134 370 9.7 11.2 26.9 10.1 11.3 Req. LLD 45 45 60 Lab Code Date Collected Sample Type Req. LLD Be-7 K-40 Co-58 Co-60 1-131 Cs-1 34 Cs-1 37 45 45 60 C-25 Table 7. Food Products, analyses for gamma emitting isotopes.Collection:
Monthly Location:
P-16 Units: pCi/kg wet Lab Code Date Collected Sample Type Be-7 K-40 Co-58 Co-60 1-131 Cs-1 34 Cs- 137 Lab Code Date Collected Sample Type Be-7 K-40 Co-58 Co-60 1-131 Cs- 134 Cs-1 37 Lab Code Date Collected Sample Type Be-7 K-40 Co-58 Co-60 1-131 Cs-1 34 Cs-1 37 Lab Code Date Collected Sample Type Be-7 K-40 Co-58 Co-60 1-131 Cs-134 Cs-137 PEVE- 3841 07-28-14 Collard Greens 178 +/- 85 4195 +/- 311< 6.7< 9.4< 21.9< 6.9< 6.5 PEVE- 4404 08-21-14 Swiss Chard< 79 2594 +/- 213< 7.2< 4.8< 18.8< 7.2< 6.6 PEVE- 5040 09-18-14 Swiss Chard 390 +/-3509 +/-il1 260 7.5 8.5 16.0 7.1 9.7 PEVE- 3842 07-28-14 Mustard PEVE- 3843 07-28-14 Turnips 374 +/- 103 3631 +/- 274< 9.9< 8.4< 16.8< 8.3< 9.2 PEVE- 4406 08-21-14 Mustard 283 +/-4670 +/-110 345 9.9 9.5 25.7 10.7 10.3 PEVE- 3844 07-28-14 Swiss Chard Req. LLD 45 45 60 566 +/-3680 +/-125 299 12.9 9.3 25.5 10.5 13.3 PEVE- 4405 08-21-14 Collard Greens< 136 3645 +/- 311< 7.1< 6.8< 32.8< 10.1< 11.2 PEVE- 5041 09-18-14 Mustard Greens 419 +/- 105 5345 +/- 317< 10.1< 10.0< 25.3< 9.0< 8.4 PEVE- 5420 10-07-14 Collard Greens 159 +/- 84 4276 +/- 293< 5.2< 9.6< 18.2< 9.5< 10.1 340 +/-2773 +/-95 214 8.8 8.3 15.5 7.4 6.1 359 +/-4172 +/-PEVE- 4407 08-21-14 Turnips PEVE- 5042 09-18-14 Collard Greens 117 +/-3588 +/-57 198 6.7 4.9 12.8 5.6 5.2 PEVE- 5418 10-07-14 Swiss Chard 288 +/- 117 4889 +/- 333< 8.8< 5.9< 15.6< 11.7< 10.5 Req. LLD 45 45 60 109 278 6.3 9.6 18.9 9.5 10.4 Req. LLD 45 45 60 PEVE- 5419 10-07-14 Mustard Greens 361 +/-5100 +/-91 268 5.5 9.5 21.0 8.8 8.5 Req. LLD 45 45 60 C-26 Table 7. Food Products, analyses for gamma emitting isotopes.Collection:
Monthly Location:
P-18 Units: pCi/kg wet Lab Code Date Collected Sample Type Be-7.K-40 Co-58 Co-60 1-131 Cs-1 34 Cs-1 37 PEVE- 3845 07-28-14 Mustard 334 +/- 117 2964 +/- 246< 5.9< 4.9< 17.6< 7.5< 6.3 PEVE- 3846 07-28-14 Turnips 266 +/- 90 2582 +/- 236< 5.8< 5.0< 20.3< 7.8< 8.8 PEVE- 4408 08-21-14 Turnips PEVE- 4409 08-21-14 Collard Greens 275 +/-4251 +/-85 295 6.4 5.3 17.9 6.7 5.7 240 +/-4288 +/-129 376 10.6 10.3 40.9 11.8 10.3 Req. LLD 45 45 60 C-27 Table 7. Food Products, analyses for gamma emitting isotopes.Collection:
Monthly Location:
P-20 Units: pCi/kg wet Lab Code Date Collected Sample Type Be-7 K-40 Co-58 Co-60 1-131 Cs-134 Cs- 137 Lab Code Date Collected Sample Type Be-7 K-40 Co-58 Co-60 1-131 Cs-1 34 Cs-1 37 Lab Code Date Collected Sample Type PEVE- 3848 07-28-14 Collard Greens< 115 4059 +/- 322< 10.3< 7.4< 16.8< 8.8< 10.7 PEVE- 4410 08-21-14 Collard Greens<130 4234 +/- 341< 9.6< 8.6< 26.5< 12.2< 7.6 PEVE- 5043 09-18-14 Swiss Chard PEVE- 3849 07-28-14 Mustard 120 +/-2792 +/-69 244 9.8 7.4 16.9 6.5 8.3 Be-7 K-40 Co-58 Co-60 1-131 Cs-1 34 Cs- 137 588 +/-6643 +/-138 395 11.5 5.4 21.7 10.3 12.3 PEVE- 4411 08-21-14 Turnip Greens< 109 4604 +/- 297< 10.7< 9.4< 35.4< 9.6< 9.7 PEVE- 5044 09-18-14 Collard Greens 222 +/- 99 4778 +/- 300< 8.0< 9.4< 22.7< 8.2< 5.1 PEVE- 5422 10-07-14 Collard Greens 316 +/- 101 4631 +/- 287< 8.6< 8.3< 20.2< 8.6< 9.0 PEVE- 3850 07-28-14 Turnips 319 +/- 99 4719 +/- 315< 5.5< 10.6< 22.5< 8.5< 6.5 PEVE- 4412 08-21-14 Mustard 219 +/- 68 3820 +/- 234< 8.6< 5.4< 24.5< 8.0< 4.8 PEVE- 5045 09-18-14 Mustard Greens 360 +/-3774 +/-PEVE- 4413 08-21-14.Swiss Chard 370 +/- 86 5327 +/- 296< 8.2< 6.6< 22.8< 7.2< 5.1 PEVE- 5046 09-18-14 Turnip Greens 371 +/- 111 4712 +/- 327.< 9.5< 13.8< 32.2< 9.1< 8.9 Req. LLD 45 45 60 Req. LLD 134 285 9.7 7.9 21.5 6.9 10.6 PEVE- 3851 07-28-14 Swiss Chard Req. LLD 45 45 60 302 +/-5244 +/-117 329 5.3 9.7 29.9 9.1 7.7 45 45 60 Lab Code Date Collected Sample Type PEVE- 5421 10-07-14 Swiss Chard PEVE- 5424 10-07-14 Mustard Greens Be-7 K-40 Co-58 Co-60 1-131 Cs- 134 Cs-137 467 +/-6233 +/-115 389 8.1 10.7 21.8 10.3 10.0 362 +/-5871 +/-103 331 8.9 8.1 21.3 8.4 7.9 Req. LLD 45 45 60 C-28 Table 7. Food Products, analyses for gamma emitting isotopes.Collection:
Monthly Location:
P-37 Units: pCi/kg wet Lab Code Date Collected Sample Type Be-7 K-40 Co-58 Co-60 1-131 Cs-1 34 Cs-1 37 Lab Code Date Collected Sample Type PEVE- 3442 07-15-14 Collard Greens 5091 +/-139 423 14.2 10.6 23.5 13.6 17.1 PEVE- 4417 08-21-14 Turnip Greens PEVE- 3443 07-15-14 Mustard Greens 177 +/- 81 4938 +/- 318< 7.4< 9.9< 16.2< 8.7< 11.2 PEVE- 4418 08-21-14 Collard Greens< 135 4835 +/- 368< 9.3< 14.1< 42.1< 10.8< 11.7 PEVE- 5425 10-07-14 Collard Greens 318 +/-2747 +/-103 232 8.1 5.9 26.2 8.1 8.8 312 +/-3877 +/-122 280 6.5 6.5 28.6 9.5 9.0 PEVE- 4414 08-21-14 Swiss Chard PEVE- 4415 08-21-14 Mustard Req. LLD 45 45 60 Be-7 K-40 Co-58 Co-60 1-131 Cs-1 34 Cs-1 37 170 +/-3331 +/-73 249 7.2 6.6 24.6 6.5 7.7 PEVE- 5048 09-18-14 Swiss Chard 471 +/- 101 3777 +/- 231< 4.6< 3.7< 19.8< 7.7< 8.7 PEVE- 5049 09-18-14 Turnip Greens 274 +/-4472 +/-84 236 7.6 4.8 17.1 6.9 7.6 Req. LLD 45 45 60 Lab Code Date Collected Sample Type Be-7 K-40 Co-58 Co-60 1-131 Cs-134 Cs- 137 PEVE- 5050 09-18-14 Collard Greens< 78 4339 +/- 136< 4.0< 4.7< 21.4< 6.9< 6.4 4732 +110 314 8.9 5.2 35.7 9.6 10.3 PEVE- 5426 10-07-14 Mustard Greens 362 +/- 101 6181 +/- 349< 8.2< 9.2< 23.8< 9.9< 9.7 PEVE- 5427 10-07-14 Swiss Chard 594 +/- 126 4084 +/- 315< 11.2< 6.6< 29.4< 10.1< 8.2 Req. LLD 45 45 60 C-29 Table 7. Food Products, analyses for gamma emitting isotopes.Collection:
Monthly Location:
P-70 Units: pCi/kg wet Lab Code Date Collected Sample Type Be-7 K-40 Co-58 Co-60 1-131 Cs-1 34 Cs- 137 Lab Code Date Collected Sample Type Be-7 K-40 Co-58 Co-60 1-131 Cs- 134 Cs- 137 Lab Code Date Collected Sample Type Be-7 K-40 Co-58 Co-60 1-131 Cs-1 34 Cs-1 37 Lab Code Date Collected Sample Type Be-7 K-40 Co-58 Co-60 1-131 Cs-1 34 Cs-137 PEVE- 3853 07-28-14 Mustard 366 +/- 102 2821 +/- 229< 5.0< 6.3< 18.8< 6.8< 8.8 PEVE- 4420 08-21-14 Turnip Greens 527 +/- 153 4525 +/- 331< 10.6< 9.2,< 34.7< 10.6< 7.2 PEVE- 5052 09-18-14 Collard Greens PEVE- 3854 07-28-14 Turnips 462 +/- 101 3695 +/- 260< 5.7< 9.2< 18.1< 6.8< 5.5 PEVE- 4421 08-21-14 Mustard 536 +/- 136 3775 +/- 317< 10.0< 8.2< 35.3< 10.7< 10.2 PEVE- 5053 09-18-14 Mustard Greens 775 +/- 160 5217 +/- 390< 5.9< 11.5< 32.6< 10.3< 7.9 PEVE- 5430 10-07-14 Swiss Chard 487 +/- 111 5974 +/- 317< 7.3< 7.2< 18.1< 10.0< 6.7 PEVE- 3855 07-28-14 Swiss Chard 415 +/-3019 +/-161 273 10.1 8.2 24.0 9.9 5.2 PEVE- 4422 08-21-14 Swiss Chard 513 +/-5214 +/-137 383 11.0 9.4 27.0 11.2 11.9 PEVE- 4419 08-21-14 Collard Greens< 82 3972 +/- 297< 8.9< 8.6< 19.8< 8.7< 7.1 PEVE- 5051 09-18-14 Swiss Chard 655 +/- 111 6523 +/- 352< 4.8< 7.2< 31.6< 8.0< 9.4 PEVE- 5428 10-07-14 Collard Greens 154 +/- 70 3347 +/- 239< 5.1< 6.6< 16.1< 8.2< 9.7 Req. LLD 45.45 60 Req. LLD 45 45 60 PEVE- 5054 09-18-14 Turnip Greens 3339 +/-88 247 7.5 5.8 16.3 6.1 6.4 638 +/-4655 +/-147 354 8.3 12.4 33.1 11.8 8.0 Req. LLD 45 45 60 PEVE- 5429 10-07-14 Mustard Greens PEVE- 5431 10-07-14 Turnip Greens 505 +/-5907 +/-101 292 9.5 5.7 20.2 8.3 6.2 380 +/-4690 +/-110 323 10.6 8.6 23.5 9.9 10.0 Req. LLD 45 45 60 C-30 Table 9. Fish, analyses for gamma emitting isotopes.Collection:
Annually Units: pCi/kg wet Location P-25 Lab Code Date Collected Sample Type PEF- 4906 09-16-14 Smallmouth Bass K-40 Mn-54 Fe-59 Co-58 Co-60 Zn-65 Cs- 134 Cs-1 37 1754 + 339< 11.4< 52.3< 18.5< 14.0< 16.8< 16.2< 16.2 PEF- 4907 09-16-14 White Perch 630 +/- 274< 21.2< 115.1< 33.3< 22.2< 34.3< 26.5< 23.5 PEF- 4908 09-16-14 Walleye 1533 +/- 314< 16.3< 48.5< 17.0< 13.8< 41.1< 19.2< 15.1 Redhorse Sucker PEF- 4909 09-16-14 Req. LLD 1957 +/- 323< 14.1< 36.3< 13.9< 17.9< 36.7< 18.5< 17.7 94 195 97 97 195 97 112 Location P-25 Lab Code Date Collected Sample Type PEF- 4910 09-16-14 PEF- 4911 09-16-14 K-40 Mn-54 Fe-59 Co-58 Co-60 Zn-65 Cs-1 34 Cs-1 37 Gizzard Shad 2012 +/- 347< 17.5< 55.0< 20.2< 9.3< 18.2< 17.4< 18.3 Channel Catfish 1442 +/- 303< 9.9< 37.4< 15.7< 13.7< 10.1< 14.3< 13.0 PEF- 5409 10-02-14 White Perch 887 +/- 284< 19.6< 55.9< 20.5< 23.9< 39.3< 18.1< 11.7 PEF- 5410 10-02-14 Gizzard Shad Req. LLD 1979 +/-335 11.5 16.7 17.0 7.6 17.3 16.1 16.8 94 195 97 97 195 97 112 Location P-25 Lab Code Date Collected Sample Type K-40 Mn-54 Fe-59 Co-58 Co-60 Zn-65 Cs-134 Cs-1 37 PEF- 5411 10-02-14 Walleye 1677 +/- 314< 8.9< 80.9< 25.9< 13.4< 27.3< 15.9< 17.8 PEF- 5621 10-02-14 Smallmouth Bass 1505 +/- 281< 21.0< 44.4< 16.0< 13.5< 18.9* 15.9< 18.0 Redhorse Sucker 2138 +/- 353< 16.3< 51.3< 24.5< 16.5< 37.8< 15.0< 10.2 PEF- 5622 10-02-14 Req. LLD 94 195 97 97 195 97 112 C-31 Location P-32 Location P-32 Lab Code Date Collected Sample Type K-40 Mn-54 Fe-59 Co-58 Co-60 Zn-65 Cs- 134 Cs- 137 PEF- 4912 09-16-14 White Perch 1104 +/- 317< 18.4< 55.6< 20.0< 8.9< 30.8< 17.5< 25.4 PEF- 4913 09-16-14 Walleye 801 +/- 463< 22.7< 117.2< 50.7< 9.5< 44.8< 36.8< 35.6 PEF- 4914 09-16-14 PEF- 4915 09-16-14 Req. LLD Redhorse Sucker 1401 +/- 296< 19.5< 58.8< 27.8< 11.3< 29.6< 18.3< 20.6 Channel Catfish 1115 +/- 307< 15.8< 63.8< 18.4< 8.5< 31.3< 17.6< 14.8 94 195 97 97 195 97 112 Location P-32 Lab Code Date Collected Sample Type K-40 Mn-54 Fe-59 Co-58 Co-60 Zn-65 Cs-1 34 Cs-1 37 PEF- 4916 09-16-14 Gizzard Shad 1527 +/- 303< 13.3< 21.2< 22.0< 13.0< 26.5< 15.8< 14.7 PEF- 5412 10-02-14 Steelhead 2284 +/- 375< 17.5< 46.6< 23.8< 4.5< 28.9< 16.8< 15.4 PEF- 5413 10-02-14 White Bass 943 +/- 272< 12.2< 40.8< 21.7< 3.9< 28.2< 13.8< 15.2 PEF- 5414 10-02-14 Req. LLD Walleye 2100 +/- 343< 18.9< 58.3< 26.5< 19.9< 24.3< 18.8< 14.4 94 195 97 97 195 97 112 Location Lab Code Date Collected PEF- 5623 10-02-14 PEF- 5624 10-02-14 P-32 PEF- 5625 10-02-14 Req. LLD Sample Type Smallmouth Bass White Perch Channel Catfish K-40 Mn-54 Fe-59 Co-58 Co-60 Zn-65 Cs-1 34 Cs-1 37 728 +/- 263< 11.2< 69.4< 20.8< 12.3< 24.2< 17.8< 16.0 866 +/- 293< 13.8< 65.3< 17.4< 12.1< 35.3< 17.3< 11.0 2161 +/- 374< 19.3< 32.7< 21.4< 10.9< 19.6< 16.7< 15.3 94 195 97 97 195 97 112 C-32 Table 11. Sediments, analyses for gamma emitting isotopes.Collection:
Semiannually Units: pCi/kg dry Location P-25 Lab Code PEBS- 4917 Date Collected 09-15-14 Req. LLD K-40 10765 +/- 564 -Co-58 < 17.6 50 Co-60 < 11.7 40 Cs-134 < 17.2 112 Cs-137 56.5 + 27.0 135 Location P-26 Lab Code Date Collected Req. LLD K-40 Co-58 50 Co-60 40 Cs-I134 112 Cs-137 135 Location P-27 Lab Code Date Collected Req. LLD K-40 Co-58 50 Co-60 40 Cs-134 112 Cs-137 135 Location P-32 Lab Code PEBS- 4918 Date Collected 09-15-14 Req. LLD K-40 13532 +/- 666 Co-58 < 21.8 50 Co-60 < 13.2 40 Cs-1 34 < 16.7 112 Cs-137 80.4 +/- 24.6 135 C-33 Table 11. Sediments, analyses for gamma emitting isotopes.Collection:
Semiannually Units: pCi/kg dry Location P-64 Lab Code PEBS- 3745 PEBS- 4858 Date Collected 07-22-14 09-11-14 Req. LLD K-40 6125 +/- 281 7020 +/- 396 -Co-58 < 8.0 < 13.6 50 Co-60 < 5.7 < 11.1 40 Cs-134 < 6.4 < 9.2 112 Cs-1 37 < 10.1 < 7.4 135 Location P-65 Lab Code PEBS- 3746 Date Collected 07-22-14 Req. LLD K-40 6194 +/- 364 Co-58 < 10.4 50 Co-60 < 8.8 40 Cs-134 < 11.6 112 Cs-137 < 9.1 135 Location P-66 Lab Code PEBS- 4860 PEBS- 5068 Date Collected 09-15-14 09-15-14 Req. LLD K-40 7242 +/- 459 9441 +/- 482 Co-58 < 15.8 < 16.2 50 Co-60 < 6.4 < 6.2 40 Cs-1 34 < 13.2 < 10.1 112 Cs-1 37 < 15.1 < 15.3 135 C-34 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Appendix D Corrections to Previous Annual Environmental and Effluent Release Reports ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT APPENDIX D Corrections to previous Annual Environmental and Effluent Release Reports: None D-1 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Appendix E Abnormal releases ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT APPENDIX E Abnormal Releases In November 2011, radioactivity was detected in the Nuclear Closed Cooling (NCC) system.The source of this activity is the Primary Coolant. There is some leakage from the NCC system to Service Water and from there to the environment.
The activity released from NCC has been included in the total radioactivity released.
Feed and bleed evolutions have occurred throughout the year to reduce the radioactive concentration in NCC and thus reduced the activity released to the environment.
Quarter 1 Quarter 2 Quarter 3 Quarter 4 Annual A. Fission and Activation Products (0)Na-24 <LLD <LLD 1.97E-04 <LLD 1.97E-04 Cr-51 <LLD <LLD 3.96E-04 4.32E-05 4.39E-04 Mn-54 3.34E-07 <LLD 1.50E-04 1.03E-04 2.53E-04 Mn-56 <LLD <LLD 6.28E-05 <LLD 6.28E-05 Co-58 <LLD <LLD 6.96E-05 5.54E-05 1.25E-04 Fe-59 <LLD <LLD 6.35E-05 1.90E-06 6.54E-05 Co-60 6.68E-04 7.44E-05 6.56E-04 5.40E-04 1.94E-03 Zn-65 <LLD <LLD 2.90E-05 9.79E-06 3.88E-05 Zn-69m <LLD <LLD 2.83E-05 <LLD 2.83E-05 Sr-91 <LLD <LLD 1.08E-05 <LLD 1.08E-05 Y-91 rn <LLD <LLD 1.59E-05 <LLD 1.59E-05 Sr-92 <LLD <LLD 1.20E-05 <LLD 1.20E-05 Nb-95 <LLD <LLD 9.74E-06 2.70E-06 1.24E-05 Zr-95 <LLD <LLD 4.26E-06 7.41 E-07 5.OOE-06 Tc-99m <LLD <LLD 3.91 E-06 <LLD 3.91 E-06 Ag-110m <LLD <LLD <LLD 2.46E-07 2.46E-07 1-133 <LLD <LLD 8.39E-07 <LLD 8.39E-07 Cs-134 1.25E-06 2.19E-06 <LLD <LLD 3.43E-06 Cs-137 2.84E-06 1.09E-05 2.47E-07 <LLD 1.40E-05 Au-1 99 <LLD <LLD 6.55E-05 <LLD 6.55E-05 E-1 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT B. Tritium (Ci) 1.87E-02 2.95E-02 1.54E-02 3.04E-03 6.66E-02 C. Noble Gases (Ci)Ar-41 <LLD <LLD 1.76E-06 <LLD 1.76E-06 Xe-133 <LLD <LLD 4.21 E-07 <LLD 4.21E-07 Xe-1 35 <LLD <LLD 3.35E-06 <LLD 3.35E-06 D. Gross Alpha (Ci) 1.03E-05 <LLD <LLD <LLD 1.03E-05 E-2 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Appendix F ODCM Non-Compliances ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT APPENDIX F ODCM Non-Compliances The ODCM requires an operable Service Water Flow Monitor. However this monitor was out of service from 11/14/14 to the end of the year. The delay in returning the monitor to service is due to age of the monitor (cannot obtain spare parts) and need to procure a new one.A shoreline sediment sample is required twice per year. However a sample was not obtained in the first half of the year. This issue was captured in the PNPP corrective action program.F-1 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Appendix G ODCM Changes ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT APPENDIX G ODCM Changes There were no changes to the ODCM during this reporting period.G-1 ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT Appendix H Changes to Process Control Program ANNUAL ENVIRONMENTAL AND EFFLUENT RELEASE REPORT APPENDIX H Changes to the Process Control Program There were no changes to the Process Control Program.H-1 REGULATORY CORRESPONDENCE REVIEW FORM NOP-LP-4007-01 Rev. 03 Page 1 of 1 (1) LETTER NUMBER: (2) LETTER
SUBJECT:
Submittal of the Perry 2014 Annual Environmental and Effluent Release L-15-143 Report (AEERR)(3) SUBMITTAL DUE: (4) PREPARER 4130/15 Name: J. Burnett PHONE NO.:5158 (5) POSTING REQUIRED (6) LICENSING BASIS DOCUMENT (7) OATH OR AFFIRMATION REQUIRED BY 10CFR19.11 CHANGE REQUIRED: E]YES ED NO 0 YES 0 NO []YES NO (8) PREPARER COMMENTS, SPECIAL INSTRUCTIONS:
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Name & Organization Commitment Enclosure Signature Date No Comments_ _ _ _ _ _ _ _ Ownership Verification Comments Provided Preparer J. Burnett, PYCH N/A N/A N/A N/A Peer Reviewer NA NA 1E K. Gehring-Ohrablo N/A N/Supervisor .N/A N/A C. Elliot, RP Manager (Acting) NJIA IJ A El T. Brown, Director PI oP a- ("- / ,/- / (/2-3 I/6 E D. Hamilton, DSO ,5 i/-- Cv' El N. Conicella, PYRC Manager / , .4.,, _ _ El~d~e~ ~L____ 2'_ El_ _ _ _ _ _ _ _ _ _ _ _ _ El El __ _ _ _ _ _ _ _El El_ _El El___ ___ ___ _ _El E3__ _ _ _ _El .El El El (10) RECOMMENDATION FOR SIGNATURE
____ ____________
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-The cognizant Manager determines whether the correspondence has received an adequate review and is therefore recommended for final signature and release, signs and dates where appropriate, and indicates whether comments are provided.
Additional reviews for signature recommendation may be obtained at management discretion.
BLOCK 11 REVIEWER COMMENTS -NO RESPONSE REQUIRED -As an alternative to using the REGULATORY DOCUMENTATION COMMENT FORM (Form NOP-LP-4007-03) reviewers may use this space to provide brief comments that do not require response from preparer.Extensive comments or comments requiring documented response must be provided on Form NOP-LP-4007-03.
REGULATORY CORRESPONDENCE CHECKLIST NOP-LP-4007-02 Rev. 02 Letter Number/
Subject:
L-15-143 Page 1 of 2 The reviewers of this correspondence signify the review of the items on the checklist by placing initials in the boxes below. As necessary, explain deviations, exceptions and non-applicable items in the Comments sections provided.A. Peer Review: No. Item Checked Initials 1. Correct organizations are listed on the review and routing forms, including organizations providing statements of fact.2. References to Codes and Standards are accurate and in sufficient detail.3. Subject line of an NRC cover letter references the NRC TAC number, if applicable.
- 4. The letter number has been entered on the letter and subsequent pages. ?__)5. Format and presentation are consistent with NORM-LP-4003 and any deviations justified.
I. I 6. Pages containing information pursuant to 10 CFR 2.390 are appropriately marked. KA 7. Oath or affirmation (if required)
-unsworn declaration is present. s, )lA 8. Dates are correct and consistent throughout the submittal.
Y,;qp-9. Grammar, spelling and editorial presentation have been verified to be correct.10. All applicable parts of the submittal are present (e.g. letter, enclosures, attachments, affidavits).
I.I 11. If Regulatory Commitments are included in NRC correspondence, the regulatory commitments are re-stated on an attachment (Regulatory Commitment List) to the submittal and identified for ownership on the Regulatory Correspondence Review Form (NOP-LP-4007-01).
If no regulatory commitments are included in NRC correspondence, a statement to that effect is provided in the correspondence.
For non-NRC correspondence, no statement regarding regulatory commitments is necessary.
__1 _12. The letter content is factually complete, is presented logically and supports conclusions reached.13. Enclosures and attachments are appropriately identified and contain all the necessary information to support conclusion of the submittal without the need to obtain other reference material.14. If action is requested of the NRC, the requested action date has been included with appropriate justification.
- 15. If the letter is in response to NRC requests, there is a clear tie between each question/request and the associated response, and each question/request is completely and clearly answered in the response.16. References listed have been reviewed, are available, and support the information contained in the correspondence.
- 17. Statements of fact have been verified to be accurate.18. Actions stated as being complete have been verified to be complete.19. Submittal does not contain information that has a material effect on information previously submitted to the NRC in response to a Notice of Violation or other enforcement action (e.g., Davis-Besse head event) or may significantly affect the NRC's understanding of plant activities.
If it does, expedited communication paths with the NRC have bgDa-teterMined, Review Performed By (Print Name and Sign): eM, Date: 4.z1 1 Comments:
C,ýýo 1AUVCLq01 rL-V:eLý-
0C="-ýq 1 X'S REGULATORY CORRESPONDENCE CHECKLIST NOP-LP-4007-02 Rev. 02 Page 2 of 2 Letter Number/
Subject:
L-15-143 B. Cognizant Manager Review (Final Submittal Review Prior to Signature Authority):
No. Item Checked Initial 1. Comments obtained during the review cycle have been resolved and incorporated within the applicable sections of the submittal.
The submittal remains factual and complete.2. Review signatures, or equivalent, have been obtained on Correspondence Review Forms (NOP-LP-4007-01).
- 3. The correspondence has been reviewed for regulatory commitments, licensing positions, prudency, appropriate wording, and potential regulatory impact.4 If the letter is in response to NRC questions or requests, there is a clear and complete respons o I each question or request and all questions jaye be" satisfactorily addressed.
-',.Review Performed By (Print Name and Date:.Comments: C. Responsible Organization Review (Administrative Support Follow-up):
No. Item Checked initials 1. Date is on the letter and the letter has been put on the appropriate company letterhead.
- 2. Submittal cover letter is signed correctly.
- 3. Oath or Affirmation (if required)
-unsworn declaration is present. If a notarized statement is requested by the signature authority, the statement page is signed and notarized.
- 4. When appropriate, initial notification and copy of submittal has been provided to the NRC via electronic
.mail.5. Submittal has been mailed, or provided electronically (in accordance with NRC guidance on electronic submittals) to all appropriate recipients, with appropriate enclosures, attachments, etc.6. Internal FENOC distribution is complete.7. Regulatory Commitments have been documented in accordance with FENOC commitment management procedures.
- 8. Additional FENOC actions have been documented, as necessary, in appropriate activity tracking systems.9. Correspondence documentation package is complete, and ready for future referral.Review Performed By (Print Name and )har 6,101' & ate: ,-4 "I Comments:
F