ML20095K060
| ML20095K060 | |
| Person / Time | |
|---|---|
| Site: | Farley  |
| Issue date: | 12/31/1991 |
| From: | Woodard J SOUTHERN NUCLEAR OPERATING CO. |
| To: | NRC OFFICE OF INFORMATION RESOURCES MANAGEMENT (IRM) |
| References | |
| NUDOCS 9205040296 | |
| Download: ML20095K060 (72) | |
Text
{{#Wiki_filter:. Southem Wecar Operatog Conpany Post Oftce Bc41295 Gimungham Alabarna 35201 Teiephone 205 668 5080 L 3 o. w ooo ,,, Southern Nudear Operating Company [$y"No7 April 30. 1992 'h'# 5 "'06**C'"C ""* Docket Nos. 50-348 50-364 U. S. Nuclear Regulatory Commission ATTN: Document Control Desk Washington, DC 20555 Joseph M. Farley Nuclear Plant Annual Environmental Operatina Reportladioleaical Geistlemen: The attached " Annual Environmental Operating Report, Part B: Radiological" for the calendar year 1991, is transmitted in accordance with the Joseph M. Farley Nuclear Plant Unit I and Unit 2 Technical Specifications Section 6.9.1.6. If you have any questions, please advise. Respectfully submitted,
,-h rnk. ssk N,D3 Woodard JDW/DMH Attachment cc: U. S. Nuclear Requlatory Commission Mr. S. D. Ebneter Mr. S. T. Hoffman Mr. G. F. Maxwell State of Alabama Director, Division of Radiation Control State of Georaia Director, Environmental Protection Division I
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SOUTHERN NUCLEAR OPERATING COMPANY. ANNUAL ENVIRONM' INTAL OPERATING REPORT PART Bf RADIOLOGICAL
-JOSEPH M. FARLEY NUCLEAR PLANT UNIT NO. 1 i
LICENSE NO. NPF-2 AND ,
. UNIT N0. 2
-LICENSE NO. NPF-8 PERIOD ENDING DECEMBER 31, 1991 ,
9 a I .
I l. ANNUAL ENVIROt@aRAL OPEFATING REPORT PART B: RADIOLOGICAL '
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TABLE Of CONTDUS ---- Section Title Page I Introduction 1 II Radiological Sanpling and Analysis 2 III Results and Discussion 5 IV Land Use Census and Interlaboratory Comparison 8 Program V Data Trends and Conclusions 8 i
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PADIOLOGICAL DNIRCtMWTAL OPERATItG REPORT LIST OF FIGURES
' Figure Title 1- Indicator Sampling Locations for Airborne , Environmental Radioactivity. at the Farley Nuclear Plant 2- Community (Indicator II) Sampling Locations for Direct Radiation in the Farley Nuclear Plant Area 3 Control Sampling Locations for Airborne Environmental Radioactivity in the Farley Nuclear Plant Area 4 Indicator and Control Sampling Locations for .
Waterborne Environmental Radioact.vity in the i Farley Nuclear Plant Area i 11
'ENV Annual-Report /2
7.. If t 1 I
-. r RADIOLOGICAL DNIRONMENTAL OPERATI!G REPORT LIST OF TABLES Tahle Title 1 Outline-of Operational Radiological Environmental Monitoring Program for Farley Nuclear Plant During'1991
'2 Required Detection Capabilities for Environmental Sample Analysis for Farley Nuclear Plant ;
3 Reporting Levels for Radioactivity Concentrations
.in Environmental Samples
-4 Sampling and Analyr.is Deviations During 1991 1991-01 Airborne: Particulates - Operational Radioactivity Summary 1991 Airborne: . Io:line - Operational Radioactivity Sumuary 1991 External Radiation - Operational Radioactivity Summary
- 1991-04 Milk - Operational Radioactivity Summary 1991-05 . Vegetation: _ Forage - Operational Radioactivity Summary 1991-06 Soil - Operational Radioactivity Summary 1991-07 Waterborne: Surface Water - Operational Radioactivity Summary 1991-08~ Waterborne: Ground Water - Operational Radioactivity Summary 1991-09~ Sedirnent: River - Operational Radioactivity Sumary l 1991-10 Fish: River (Game) - Operational Radioactivity Summary l: 1991-11 Fish: River (Bottom Feeding) - Operational Radioactivity Summary lii
. DN Annual Report /2 o
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RADIOIOGICAL DNIRONMDirAL OPERATI!G REPORT LIST OF ATTACHMENTS
Attachment:
Title l- Land Use Survey for Radiological Environmental Mcaitoring Program, Joseph M. Farley Nuclear Plant June 7, 1991 ' 2 Plots of Selected Environmental Data iv. ENV Annual Report /2 u.,,. , , # _ , +. -. _____ -I
- 4 OPERATICNAL RADIOIEICAL ENVIIOr. ENTAL PROGRAM JOSEPH M. FARLEY NUCLEAR PIAlff LNITS 1 AND 2 I. Introduction The Joseph M. Farley Nuclear Plant, owned by Alabama Power Company (APCo) and operated by Southern Nuclear Operating Company (SNC),
located in Houston County, Alabama is approximately fifteen miles east of Dothan, Alabama on the west bank of the Chattahoochee River. Unit 1, a Westinghouse Electric Corporation Pressurized Water Reactor (PWR) with a reted power output of 860 megawatts electrical (MWe) achieved initial criticality on August 9, 1977. The unit was declared "comercial" on December 1,1977. Unit No. 2, also a 860 MWe Westinghouse PWR, achieved initial criticality on May 8,1981 and was declared "comercial" on July 30, 1981. Unit II concluded its seventh refueling outage on January 6, 1991. Unit I was shutdown for its tenth refueling outage from March 8, 1991 through May 19, 1991. The Farley Nuclear Plant Environmental Monitoring Program is designed to detect the effects, if any, of plant operation on environmental radiation levels. The sample collection and analysis schedule was implemented in 1977, and modified on July 1, 1980, by l adding 14 TLD stations. The program was further modified in April l 1982, by Amendment No. 26 to the Unit I Technical Specifications. l The program was changed a third time in 1989, with the addition of two more control TLDs and has continued through 1991 without further change. Indicator sampling stations are located, where practical, at locations where detection of the radiological effects of the plant's. operation is thought to be most likely, where the samples collected should provide a significant indication of potential dose to man, and where an adequate comparison of predicted radiological levels might be made with measured levels. l The control stations are placed at locations where radiological levels are not expected to be significantly influenced by plant operation, i.e., at background locations. For some airborne radioactivity samples, community stations are located at the l principal population centers between the indicator and the control L stations (3-8 miles). Community stations could be used, if desired, as additional control stations, and alternatively, as indicator stations for the nearest population centers in the event of a major airborne release from the plant. 1
l 1 II. Radiological Sampling and Analysis To assess the environental impact of plant operation the Farley Nuclear Plant Environmental Monitoring Program monitors airborne, waterbene, ingection and direct radiation pathways in the area surrounding the plant site. Table 1 details the sample types, collection and analysis frequency and locations of indicator, community and control stations. For each sample type and location, one sample was collected and analyzed to meet Technical Specification requirements for Units I and II. While no longer required by Technical Specifications, in situ soil monitoring was continued in 1991. The samples were collected by Southern Nuclear's technical stuff except for the in situ scil measurements, which were collected by staff members oTthe University of Georgia (UCA), Center for Applied Isotope Studies. All sample analyses were contracted to UGA, except TLD's, which are read at the plant. The minimum detectable concentration (MDC), specified for the various samples and their respective analyses are given in Table 2. The reporting levels for radioactivity concentrations in environmeatal samples are provided in Table 3. Sampling and analysis deviations during 1990 are listed in Table 4. A. Airborne Particulates and Iodine All airborne particulate and iodine monitoring stations shown in Figures 1 and 3 were equipped with Roots vacuum pumps which 3 continuously at a flow rate of approximately 0.04 m /ain operatep/ (1.5 ft min). Th( particulates were collected on Gelman Metricel Svm filters. In series with, but downstream of the particulate filters, F&J 50 mm (or equivalent) activated charcoal cartridges were used for collection of iodine. The Roots system has the sample collector mounted outside of the cabinet horizontally to the ground with a Singer gas meter measuring the cumulative air flow. The gas meters were calibrated against a certified flow meter. Both the particulate filters and charcoal cartridges were collected weekly and sent to UGA for radioactivity analysis. Gross beta radioactivity measurements were performed on each air particulate filter using a Ter.nelec low background alpha-beta counting system. The filters from each station, composited at the end of each quarter, were analyzed for gamma emitters using a fifteen percent relative efficiency low background germanium lithium (Ge(Li)) detector and a Canberra 4J96 channel computer-based multichannel analyzer (MCA). All air monitoring station locations shown in Figures 1 and 3 have the capability of monitoring airborne iodine. Weekly routine samples were analyzed for I-131 by UGA using a Canberra 1024 channel MCA and two 1" x 3" NaI detectors and matched photomultiplier tabes. 2
l B. External Radiation For the continuous meaurement of environmental gamma radiation, natural Lithium Fluoride (Mr) (TLD-700) chips, manuf actured by Harshaw-riltrol Chemical Conpany, were used. TLD packets, each containing four annealed Lir chips, were sealed in opaque mylat to produce a packet that was light-tight, weather-proof, and which had a low p ss attenuation for radiation (approximately 50mg/cm ). On the plant site, all TLD packets were kept in a lead safe with 2-inch walls except for those receiving field exposure or those in the process of being exchanged. At each external radiation monitoring station (shown in rigures 1-3), two TLD packets, one changed and read quarterly and one changed and r W annually, were exposed side-by-side on metal stakes at a height of one meter above the ground. For the . computation of the net field doses, a log of all exposure periods was rWntained for each TLD packet. C. Milk The milk sample location ib as indicated on Figure 3. All milk samples, collected bi-weekly, were analyzed by tGN for 1-131 and gamma emitters. As a preservative for shipment,1 ml of 25 weight percent merthiolate (Thimerasol) solution was added to each one gallon sample. he I-131 concentration in each sample was determined by collection on anion exchange resin, elution with sodium hypoch.orite, followed by organic extraction and counting, by reta-gamma coincidence, the resultant toluene-iodira solution in a low level liquid scintillation counter. Stable iodine carrier was added to each sample for determination of the radiochemical yield. One liter of each sample was placed in a marinelli beaket and analyzed for gamma emitters using a 15 percent relative efficiency low background Ge(Li) detector and a Canberra 496 channel computer-based MCA. D. Vegetation: Forage Monthly, forage was collected from indicator gras . plots located near the air monitoring stations at the plant site [ perimeter in the SSE and N sectors, or alternate plots if needed, and from a control grass plot located near the air monitoring station in Dothan, Alabama. After drying and pulverizing, the samples were analyzed by LGA for gamma emitters using a 15 percent relative efficiency low background Ge(Li) detector and a Canberra 4096 channel computer-based MCA. 3
l l , E. Soil Annual in situ gamma-ray spectroscopy measurements were made by tXA using a ID percent relative efficiency high purity germanium A toctor and gamma-ray spectroscopy system specially designed for field use. Measurements were taken at the six indicator locations and at the three community and two control (background) locations listed in Table 1. A 1024 channel Canberra MCA interfaced to a llewlett-Packard 9025A calculator was used for data storage and analysis,
- r. Surface (River) Water Samples of water from the Chattahoochee River, upstream and downstream of the ,>lant site at the locations shown in rigute 4 were collected on a semi-continuous basis with Instrumentation Specialties company (ISCO) samplers. Monthly composites were sent to UCA for radioactivity analysis. Two liter aliquots from each monthly composite were placed in traus lined with plastic film and evaporated to dryness at 100'C. We residue (on r ustic film) was folded to fit a petri-dish and analyzed 2cr .ana emitters using a 15 percent relative ef ficiency Ge(Li) low background detector and a Canberra 4096 channel computer-based MCA.
At the end of each quarter, for each sampling location, the balance of the three monthly composites were combined to give a quarterly composite sample. Approximately 50 ml from each quarterly composite sample was distilled and a 25 ml aliquot taken for tritium analysis using a large volume (100 ml) Hewlett-Packard 200 low background liquid scintillation counter. G. Ground (Well) Water In the Parley Plant area there are no true indicaur sources of groundwater. A well which serves Georgia Pacific Paper Company as a source of potable water, located on the east bank of the Chattahoochee River about four miles south-southeast of the plant, was sampled quarterly as an indicator station. A deep well which supplies water to the Whatley residence located about 1.2 miles southwest of the plant was sampled quarterly as a control (background) station. Samples from both were sen to UGA for radioactivity analysis. An aliquot from each sample was taken for tritium analysis. After distillation, 25 ml samples were analyzed using a large volume (100 ml) low background liquid scintillation counter. From the remainder of each sample, a two liter aliquot 'aas taken and evaporated to dryness at 100'C in a tray lined with plastic film. The residue (on plastic film) was folded to fit a petri dish m d analyzed for gamma emitters using a 15 percent relative efficiency Ge(Li) detector and a Canberra 4096 channel computer-based MCa. 4
II. Fish (River) Semi-annually, two types of finh, game and bottom feeding, were collected from the Chattahoochee River at the locations shown in rigure 4, and ser.t to E for gamma-ray spectroscopy analysis. All fish samplet sent to UCA conslated of fish filletc that had been split with Alabama Division of Radiation Control. These fish samples were coarsely chopped at e and were analyzed for gamma emitters using a 15 percent relative efficiency low background Ge(Li) detector and 4096 channel Canberra computer-based MCA.
- 1. Sediment (River)
Semi-annually, sediment samples were collected from the Chattahoochee River at the locations shown in rigure 4. Approximately one kilogram of each sample was sent to UCA where it was tied, mixed, and analyzed for gamma emitters using a 15 percent relative efficiency low background Ge(Li) detector and a Canberra 4095 channel computer-based MCA. One set of semi-annual sediment sah.ple was split with Alabama Division of Radiation Control. III. Results and Discussion No known atmospheric nuclear tests were conducted during 1991. 7he definitions of " lower limit of detec M on" (LLD) and " minimum detectable concentration" (MDC) have not changed since last reported (1990 Annual Environmental Operating Report). Attachment 2 , Plots of Selected Envircnmental Data, has been added to this year's report as an enhancement to trending. In general, the mean annual concentrations of frequently identified isotopes were chosen to be plotted. In cases where many naturally occurring isotopes were identified, those chosen to be plotted were from differing decay chains. Significant uptrends in the data were as follows: (1) Atmospheric Tests, Peoples Republic of China: September 17, 1977 March 14, 1978 December 14, 1978 october 15, 1980 (2) Chernobyl Disaster, USSR, April 1986
A. Altborne Particulates and Iodines Analysis results of airborne particulate filters and charcoal cartridges are shown in Tables 1991-01 and 1991-02, and Attachment 2, pages 1-5. he 1991 results are below pre-operational levels and consistent with previous years. Cesium 134, Cesium 137, and Iodine 131 were not detected and there are no significant differences in indicator, comunity and control measurements. D. External Radiation he results of the aternal radiation measurements are shown in Table 1991-03 and Attachment 2 pasje 6. The 1991 results are at or below pre-operational levels and consistent with previous years. There are no significant differences in indicator, community and control measurements. C. Milk The milk analysis results are shown in Table 1991-04 and Attachment 3, pages 7-9. Lewis Dairy was used as the control location. There were no indicator samples during 1991. We 1991 results are consistent with those of previous years, and Potassium-40 was the only isotope detected in milk samples. D. Vegetation Forage analysis results are shown in Table 1991-05 and Attachment 2, pages 10-14. he 1991 results are below pre-operational levels and consistent with the downward trends of recent years with the following exceptions. The August 1991 control sample contained 13 pci/kg Cesium 137 activity,
- barely above the MDC of 12 pCi/kg. The mean annual Cesium 117 control sample was higher due to the December cc,ntrol samp;o containing 137 pCIAg Cesium 137 activity. The most likely cause of the elevated activity in the December sample was the lack of sufficient fresh green forage'at the control location due to cold weather and lack of rain. The sample consisted of grass and vegetation from the forage plot which had survived the dry weather and the cold. Cesium 137 has been shown to be present in the soil throughout tne area since the pre-operational period. Consultation with University of Georgia, Center for Applied Isotopes Studies supervision, confirmed that such "old" vegetation, having had more ti.ne to concentrate Cesium 137 from the soil, is more likely to indicate Cesium 137 activity than fresh green growth. The
, control forage plot has been tilled, fertilized and reseeded with a mixture of rye and bahia grass and is being watered more frequently during dry weather. Subsequent samples have been adequate to meet analysis requirements. 6
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E. Soil he in situ soil analysis results are shown in Tablo 1991-06 and Tn Attachment 2, pages 15 and 16. We only man-made isotope found was Cesium 137 which has been present since the pre-operational period. Cesium 137 measurements for 1991 continue the downward trend of recent years with no significant difference in measurements taken at indicator, control and community locations. F. Waterborne (Surface Water) he surface water analysi: tesults are shown in Table 1991-07 and in Attachment 2, pages 17-19. The tritium activity measured in two of four indicator samples was below pre-operational levels and consistent with a general downward trend observed since 1986, tio measurable act tvity from man-mado isotopes was detected in control sagles.
-G. Waterborne (Ground Water)
The grrund water analysis results are shown in Table 1991-08 and in Attachment 2, pages 20-22. tio measurable activity from man-made isotopes was detected in ground water samples in 1991. II. River Sedinent The river sediment analysis results are shown in Table 1991-09, and in Attachment 2, pages 23->26. While activity from a variety of naturally occurring isotopes was measured, no man-made isotopes were detected. I. Game Fish (River) The analysis results of edible portions of Chattahoochee River game fish are shown in Table 1991-10 and in Attachment 2, page
- 27. Cesium 137 activity was detected in one of two indicator sampics and one of two control samples. Detected activity was below pre-operational levels and consistent with established trends.
J. Bottom-Feeding Fish (River) Analysis results of edible portions of Chattahoochee River bottomfeeding fish are shown in Table 1991-11 and in Attachment 2, page 28. tio measurable activity from man-made isotopes was detected in control or indicator samples, and FDC values are less than those for the pre-operational period. 7
IV. Land Use Census and Interlaboratory Comparison Program A. Land Use Census The rekalts of the June, 1991, Land Use C?nsus are given in Attachment 1 to this report. D. Interlaboratory Cmparison Program During 1991, the University of Georgia Center for Appli*xl Isotope Studies (UGA) was a participant in the EPA crosscheck Program. We UGA EPA Program code designation is EA. V. Data Trends and Conclusion Review of data trends from the pr, w,pe, 'ie:u'. neriod through 1991 indicates t%t environmental radi. .im 1 mei red in all the pathways man' tored in 1991 remaint ' v. ;w1: .u6 /Jels and vere at or below pre-operational levels. N f c ephi .o test conducted by the Peop e's Republic of China in vets ,a 1983, and the Chernobyl M saster in April 1986, produced measurable increases in background radiation, but the effects diss Pted within two to three years following each event. he gentral downward trend in environmental radiation levels observed since 1986 continue in 1991. Therefore, data obtained during 1991 demonstrated that continued operation of Parley Nuclear Plant has not harmed or caused any irreversible damage to the environment. 8
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TABIE 1 OUTLINE OF OPEPATICHAL RADIOLOGICAL Ehv1PfnMDMAL - MCNITORI!G PROGFAM EVR FARLEY NUCLEAR PLANT DURING 1991 Types of Samples Type and Fregtecy and Sampling of Sampling Locations and Collection Frequency Analysis (Distances Given in Miles) AIRBORNE Continuous operation of sampler with Particulate sampler Particulates sample collection being performed Analyze for gross Leta once per 7 days. radioactivity > 24 hours following filter change. Indicator Stations: Perform gamma isotcpic analysis on esch sample North Perimeter (N-0.8) when gross beta activity South Perimeter (SSE-1.0) is >10 times the yearly Plant Entrance (WSN-0.9) mean of centrol samples. River Intake Structure (ESE-0.8) Perform gagna isotopic analysis on crrposite (by location) sample at i Conmanity Stations: least once per 92 days. Columbia, AL. (N-5) , Great Southern Paper Co. (SSE-3) ' Ashford, AL. (TGN-8) Control Stations: Blakely, GA. (NE-15) Dothan, AL. (W-18) Neals Landing, FL. (SSE-18) Continuous sa=pler operation Padiciodine canister Iodine with charcoal canister Analyze at least once Indicator Stations: collection performed once per 7 days. per 7 days for I-131. North Perimeter (;+--0.8) South Perimeter (SSE-1.0) Plant Entrance - (WSN-0.9) River Intake Structure (ESE-0.8) Table 1 Page 1 of 5 Annual ErW Report /4
TABLE 1 (con'd) Types of Samples Type and Fregaency - and. Sampling and of Sampling Locations Analy,is Collection Frequency ! (Distances Given in Miles) Community Stations: Great Southern Paper Co. (SSE-3) Control Stations: i Blakely, CA. (NE-lS) Dothan, AL. (W-18) Neals Landing, FL. (SSE-18) Annual in situ Ge(Li) gan:na-ray C w a Isotgic Soil spectroscopy measurements. Annually Indicator Stations: Seven Stations along the plant perimeter (NE-1.0, E-0.8, SSE-1.0, SSW-1.0, W~:#r-0.9, IN4-0.8 and N-0.8) Community Stations: Columbia, AL. (N-5) (reat Southern Paper Co.'.SSE-3) Ashford, AL. (WSW-8) Control Stations: Blakely, GA. (FE-lS) Dothan, AL. (W-18) At least once per 92 days Ceana dose DIRECT RADIATION Readout at least once per 92 days Table 1 Page 2 of 5 Annual EIN Report /4
TABLE 1 (cono d) . Types.of samples. Type and Frequency Sampling and . of Sampling Locations and Collection Fregaency Analysis (Distances Given in Miles) Indicator I Stations: Sixteen stations, one in each meteorological sector along the plant perimeter (r+-0.8, r@iE-0.9, !E-1.0, ME-0.9, E-0.8, ESE-0.8, SE-1.1, SSE-1.0, S-1.0, S W 1.0, % 0.9, WSN-0.9, W-0.8, RM-0.8, PM-1.1, and 1 M-0.9) . Indicator II (Community) Stations: l Eighteen stations: At least one in each meteorological sector at a distance of 3-8 miles (trE-4, IE-4, DE-4, E-5, ESE-5, SE-5, SSE-3, S-5, i 5%4, %1.2, %5, WSW-4, W%8, W-4, MM-4, IM-4,1:M-4, and N-5). Control Stations: Blakely, GA. (NE-15) Neals Landing, FL. (SSE-18) Dothan, AL. (W-18) Dothan, AL. (W-15) Webb, AL. (RM-ll) Haleburg, AL. (N-12) 'WATEFK;FIE Composite taken with propor- Monthly ganma isotcpic Surface Water analysis of each coeposite tional semi-continuous sampler, having a minimum sampling fre- sample. Tritium analysis Indicator Station: of each composite sample quency not exceeding two hours collected over a period 5 31 days. at least once per 92 days. Great Southern Paper Co., (3 miles dosastream of plant discharge, River Mile-40) Table 1 Page 3 of 5 Annual D N Report /4
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i TABLE 1 (con'd) -
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Types'.of Samples-and . . Sampling Type and Frequency - Sampling Locations and of (Distances Given'in Miles)- Collection Frequency Analysis-Control Station: Upstream of ' Andrews 'Inck and Dam (-3 miles upstream of plant intake, River Mile-47)
! Ground Water. Grab sample taken at'least . c.=amma isotopic and tritium.
L once per 92 days. analyses of each sample-i' ~ Indicator Statirris: once per quarter. . _ i
; Great Southern Paper Co.,.Well (SSE-4)
Control Station:. l- . Whatley Residence, Well (SW-1.2) e
- River Sedinent Grab sample taken at least Gamma isotopic analysis p
once per 184 days. of each saaple twice per year. Indicator. Station: Downstream of plant. discharge ' i 3-at Smith's Bend (River Mile - 41) 3: Control Station: i 4 Upstream of plant discharge 4 at Andrews Lock & Dam Reservoir' . (River Mile - 47) i-J i Table 1
- Annual DN Report /4 Page 4 of 5 i
TABLE 1 (con'd) - Types of Samples and Sa:cyling Type and Frequency - Sampling Locations and of (Distances Given in Miles) Collection Frequency Analysis IfGESTION Milk Contrcl Staton: Lewis Dairy At least once per 16 days Gamma isotopic and I-131 Avon, AL. (WSW-14) analysis of each bi-weekly sample when animals are en pasture. Fish Indicator Station: One sample each of the following Gamma isotopic analysis species at least once per each on edible portions once seasco (March 15 - May 15 and per season. September 15 - No,.
- r 15)
- 1. Game Fish
- 2. Bottom Feeding Fish Dcranstream of plant discharge in vicinity of Smith's Bend (River Mile - 41)
Control Station: Upstream of plant discharge j in Andrews Lock & Dam Reservoir (Piver Mile - 47) Forage Grab sample cut frca green Garmn isotopic analysis forage at least once per 31 (which includes I-131) days. of each monthly sa=ple. Indicator Station: North Perimeter (N-0.8) South Perimeter (SSE-1.0) Control Station: Dothan, AL. (W-18) Table 1 Annual ENV Report /4 Page 5 of 5
s. TABLE 2 REQUIRED DETECTIGi CAPABILITIES FOR EINIHONMErTIAL SAMPLE MaLY FOR FARLEY NUCLEAR PIRir VALUES FOR THE MINIMUM Dt:1u;1ABLE CGJCENIRATIG1(P'DC)* *
- l Airborne Particulate Fish Milk Food Products Sediment Water or Gap (pCi/kg. wet) (pCi/kg. dry)
Analysis (gCi/1) (pCi/m ) (pCi/k g. wet) (pCi/1) Gross beta 4 0.01 la ta ra ra i 2000 ra la la la fa H-3 Mn-54 15 NA 130 NA ra fa Fe-59 30 M 260 ra la ra co-58, 60 15 ra 130 ra fa ra 2n-65 30 ra 260 ra NA ra Zr-95 30 ra ta ta ra ta Nb-95 15 ra ta ta ra la 0.07 ra 1 60 NA I-131 1* 15 0.05 130 15 60 250 Cs-134 18 0.06 150 18 80 180 Cs-137 Ba-140 60 ra ta 60 ra la La-140 15 NA ra 15 ra ra Table 2 Page 1 of 2 1
i TABLE 2 (con'd)
*ne MDC is the smallest concentration of radioactive material in a sample that will be detceted with 95% probability with 5% probability of falsely concluding that a blank observation represents a "real" signal.
For a particular measurement system (which may include radiochemical separation): MDC = 4.66 S, E V 2.22 Y exp (-A6t) Where MDC is the "a priori" lower limit of detection as defined above (as picoeurie per unit mass or volume). , l S is the standard deviation of the background counting rate or oIthecountingrateofablanksampleasappropriate(ascounts per minute). l p . l E is the counting efficiency (as counts per transformation). V is the sample size (in units of mass or volume). 2.22 is the number of transformations per minute per picoeurie. Y is the fractional radiochemicel yield (when applicable). A is the radioactive decay constant for the particular ' radionuclide, at is the elapsed time between sample collection (or end of the sample collection period) and time of counting (for environmental samples, not plant effluent samples). he value of S, used in the calculation of the MDC for a detection
- system shall be based on the actual observed variance of the background L
o counting rate or of the counting rate of the blank samples (as appropriate) rather than on an unverified theoretically predit..td
- variance. In calculating the MDC for a radionuclide determined by l- gama-ray spectroscopy, the background shall include the typical
! contributions of.other radionuclides normally present in the samples (e.g ,1 Potassium-40 in milk samples). Typical values of E, V, Y and at shall;be used in the. calculations. ! " W e MDC's for Tritium, Gross beta, and Radioiodine were obtained using L blank background (a priori), whereas, for gamma-ray spectroscopy L- _ actual sample backgrounds were used (a posteriori).
'MDC for drinking water.
Table 2 Page 2 of 2
TABLE 3 - REPORTING LEVELS FOR RADICACTIVITY CINCDrIRATIWS IN DNIlOMENIAL SAMPLES Airborne Particulate Water or Gap Fish' Milk Food Products Analysis (pCi/1) (pCi/m ) (pCi/kg. wet) (pCi/1) _pCi_/kg. ( wet) H-3 2 x'10** ra la la la -Mn-54 1 x'10'~ ra 3 x 10' ra la Fe 4 x'10* ra 1 x 10' ra la co-58 1 x 10' NA 3 x 10' ra la Co-60 3 x 10 2 ra 1 x 10' ra ta Zn-65 3 x 10 2 ra 2 x 10' ra ta 2-/td>-95 4 x 10* ra ta ra fa 2 1-131 2 x 10' 9 x 10-* Fa 3 x 10' 1 x 10 Cs-134 3 x 10* 1 x 10* 1 x 10' 6 x 10* 1 x 10' Cs-137 '5 x 10* 2 x 10* 2 x 10' 7 x 10* 2 x 10' Ba/La-140 2 x 10* ra ta 3 x 10 2 ra
*For drinking water samples.
Annual DN Report /4(7) Table 3 Page 1 of 1
l TABLE 4
. . SAMPLI!G AND A% LYSIS DEVIATIONS IURItu 1991 Component Time Period Reason for Deviation / Comments Air Monitoring Station 1/2/91 - 1/0/91 Low sample volume; adjusted sampla 1601 flowrate.
Air Monitoring Station 1/2/91 - 1/8/91 Low sample volume; adjusted sample 0501 flowrate. Air Monitoring Station 1/2/91 - 1/8/91 Im sample volume; adjusted sample 0701 flowrate. Air Monitoring Station 1/2/91 - 1/8/91 Low sample volume; adjusted sample 0215 flowrate. Air Monitoring Station 1/8/91 - 1/15/91 Low sample volume; adjusted sample 0701 flowrate. Air Monitoring Station 1/15/91 - 1/22/91 Low sample volume due to loss of 0701 electrical power. Power restored 1/25/91. Air Monitoring Station 1/15/91 - 1/22/91 Low sample volume; adjusted sample 0703 flowrate. Air Monitoring Station 1/22/91 - 1/29/91 Low sample volume due to dust loading 1601 on particulate filter. Air Monitoring Station 1/22/91 - 1/29/91 Low sample volume due to dust loading 0501 on particulate filter. Air Monitoring Station 1/22/91 - 1/29/91 Low sample volume due to dust loading 0701 on particulate filter. Air Monitoring Station 1/22/91 - 1/29/91 Low sample volume due to mechanical 0703 failure; monitor repaired 1/30/91. Air Monitoring Station 1/22/91 - 1/29/91 Low sample volume due to dust loading 0215 on particulate filter. Air Monitoring Station 1/29/91 - 2/5/91 Low sample volume due to dust loading 0701 on particulate filter. Air Monitoring Station 2/5/91 - 2/12/91 Low sample volume due to dust loading 0501 on particulate filter. Air Monitoring Station 2/5/91 - 2/12/91 Low sample volume due to dust loading 0703 on particulate filter. Air Monitoring Station 2/12/91 - 2/19/91 Low sample volume due to dust loading 0501 on particulate filter. Table 4 1 fnnual EIN Report /3 Page 1 of 5 I
Component Time Period Reosor. for Deviation / Comments Air Monitoring Station 2/12/91 - 2/19/91 tow sample volume due to dust loading 0703 on particulate filter. Air Monitoring Station 2/19/91 - 2/26/91 Low sample volume due to dust loading
-0501 on particulate filter.
. Air Monitoring Station 2/19/91 - 2/26/91 Low sample volume due to dust loading 0701 on particulate filter.
Air Monitoring Station 2/19/91 - 2/26/91 Low sample volume due to dust loading 0703 on particulate filter. ! Air Monitoring Station 2/26/91 - 3/5/91 Low sample volume due to dust loading 0501 on particulate filter. Air Monitoring Station 2/26/91 - 3/5/91 Low sample volume due to electrical 0701 failure of pump motor' motor repaired 3/7/91. Air Monitoring Station 2/26/91 - 3/5/91 Low sample volume due to mechanical 0703 failure of pump; pump repal. ! 3/8/91. Air Monitoring Station 3/5/91 - 3/12/91 Low sample volume due to dust loading 0501 on particulate filter. Air Monitoring Station 3/5/91 - 3/12/91 Low sample volume due to dust loading 0701 on particulate filter. Air Monitoring Station. 3/5/91 - 3/12/91 Low sample volume due to shortened-
'0703 collection period caused by pump failure.-
Air Monitoring Station 3/5/91 - 3/12/91 Low sample volume due to faulty 0718 totalizer. Totalizer replaced 3/19/91.
-Air Monitoring Station 3/12/91 - 3/19/91 '
low sample volume due to dust loading - 0501 on particulate filter. Air Monitoring Station 3/12/91 - 3/19/91 Low sample volume due to dust loading 0701 on particulate filter. Air Monitoring Station 3/12/91 - 3/19/91 Low sample volume due to faulty 0718 totalizer; totalizer replaced 3/19/91. Air Monitoring Station 3/19/91 - 3/26/91 Low sample volume; adjusted sample flowrate. 0501
~' Air Monitoring Station 3/19/91 - 3/26 /91 Low sample volume; adjusted sample 0701J flowrate.
l L Table 4 Annual DN Report /3 Page 2 of 5 l
Component Tiro Nried Rioson for DevictiorVComments I Air Monitoring Station 3/19/91 - 3/26/91 Sample station inoperable due to 1101 electrical failure; pump motor replaced 3/29/91. Air Monitoring Station 3/19/91 - 3/26/91 Low angle volume due to faulty 1108 totalizer; totalizer replaced 3/29/91. Air Monitoring Station 3/26/91 - 4/2/91 Low samplo volume; adjusted sample flowrate. 0501 l Air Monitoring Station 3/26/91 - 4/2/91 No sample; pump motor improperly 1101 installed; repaired 4/5/91. Air Mon.:oring Station 4/2/91 - 4/9/91 Low sample volume; sample flow 0501 obstructed; work request initiated. Air Monitorin'g Station 4/2/91 - 4/9/91 Low sample volume; increased sample 0718 flowrate. Air Monitoring Station 4/2/91 - 4/9/91 Low sample volume; increased nample 0215 flowrate.
- Air Monitoring Station 4/16/91 - 4/23/91 Low sample volume; work request 0501 outstanding. Repaired (new pump installed) 5-8-91.
Air Monitoring Station 5/1/91 - 5/14/91 Low sample volume due to mechanical 1605- failure of totalizer. - Air Monitoring Station 5/7/91 - 5/14/91 Particulate sample missing; reason 0501 unknown. Air Monitoring Station 5/14/91 - 5/21/91 No sample due to mechanical failure 1605.
~
of totalizer; totalizer replaced 5/23/91. Air Monitoring Station 5/21/91 - 5/28/91 Low sample volume due to faulty 0701 totalizer; work request initiated. Air Monitoring Station 5/21/91 - 5/28/91 Package containing particulate 1108 filter accidently fell to ground and was destroyed by lawn mower. In Situ soil Sample- 5/28/91 Measurement not taken due to 0201 temporarily barricaded road. Air Monitoring Station 5/28/91 - 6/4/91 No sample due to mechanical failure of 0701 totalizer; totalizer replaced 6/4/ &
- Air Monitoring Station 6/4/91 - 6/12/91 Low sample volume; poor sample flow; 0701 work request initiated.
Air Monitoring Station 6/12/91 - 6/18/91 Low sample volume due to poor sample 0701. flow and six-day collection period. (schedule changed due to NRC Inspection) Table 4 Annual DW Report /3 Page 3 of 5 ,
Component Time Pariod R2tson for Deviation /Coments Air Monitoring' Station 6/12/91 - 6/18/91 Low sample volune; adjusted sample 0703 flowrate. Air Monitoring Station 6/12/91 - 6/18/91 Low sample volume; adjusted sample 0215 flowrate. Air Monitoring Station 6/18/91 - 6/25/91 Low sample volume due to dust loading 0703 on particulate filter. Air Monitoring Station 6/18/91 - 6/25/91 Low sample volume due to blown 0218 fuse; replaced fuse. Air Monitoring Station 7/16/91 - 7/23/91 Monitoring station inoperable due to 0215. nechanical failure; repaired 7/25/91. Air Monitoring Station 7/23/91 - 7/30/91 Low sample volume; adjusted sample 0215 flowrate.
' Air Monitoring Station 7/23/91 - 7M 0/91 Monitoring station inoperable due to 1218 electrical failure; repaired 8/2/91.
Air Monitoring StaticA1 7/30/91 - 8/6/91 Monitoring station inoperable due to
-1218 electrical failure; repaired 8/9/91.
Air Monitoring Station 8/6/91 - 8/13/91 Low sample volume; adjusted sample 1218. flowrate. Air Monitoring Station 11/13/91 - 8/20/91 Monitoring station shutdown 8/18/91 and 0701 moved to permit removal of dead tree for safety; monitoring station returned to service 8/24/91. Air Monitoring Station 8/13/91 - 8/20/91 Low sample volume due to blown fuse; 1101 replaced fuse. Air Monitoring Station- 8/20/91 - 8/27/91 Low sample volume; monitoring station 0701: returned to service 8/24/91. Air Monitoring Station 8/20/91 - 8/27/91- Monitoring station inoperable due to 1101- blown fuse; replaced fuse. Air Monitoring Station 9/17/91 - 9/24/91 Low sample volume; adjusted sample 1218 flowrate. ; Air Monitoring Station 9/24/91 - 10/1/91 -Particulate filter missing; reason 1218 unknown. cAir Monitoring Station 10/29/91 - 11/5/91 Monitoring station inoperable due to
'0703- broken drive bc1t; belt replaced 11/8/91, i
Table 4 Annual DN Report /3 Page 4 of 5 , _ _ . - . _ _ _ . _ . _ . . . . _ -- _ . ~ - . . _ . . _ . _ . . , , , ,.
Conponent Time Period R22 son for Deviction/Conments Air Monitoring Station 10/29/91 - 11/5/91 . Monitoring station inoperable due to 1218 blown fuse; replaced fuse. Air Monitoring Station 11/12/91 - 11/19/91 Low sample volume due to dust loading 1601 on particulate filter. , Air Monitoring Station 11/12/91 - 11/19/91 Low sanple volume; adjusted sample 0701 flowrate. Air Monitoring Station 11/12/91 - 11/19/91 Low sample volume; adjusted sample ' 0718 flowrate. Air Menitoring Station 11/12/91 - 11/19/91 Monitoring station inoperable due to mechanical failure of totalizer; 0215 replaced totalizer 11/21/91.
. Air Monitoring Station 11/2/91 - 11/19/91 Monitoring station inoperable due to 1218 fuser-replaced fuse.
i Air Monitoring Station 11/19/91 - 11/25/91 Monitoring station inoperable due to mechanical failure of totalizer; 1
-0701 totalizer replaced 11/30/91.--
. Air Monitoring Station 12/3/91 - 12/10/91 Monitoring station inop .able due to 1218 blown fuse; replaced fuse.
Air Monitoring Station 12/10/91 - 12/17/91 Monitoring station inoperable due to 1218- blown fuse; replaced fuse, initiated-work request to investigate repeat occurrence; work request completed- , 12/19/91. Air Monitoring Station 12/17/91 - 12/23/91 Monitoring station inoperable due to 0701 tripped breaker; reset breaker. 1 l' l l Table 4 , Annual DN Report /3 Page 5 of 5
p l l 7AltLE 1991-01 AIRW)KKE: TARTlcU!ATES Of f. RATIONAL RAD 10AC11VITY SUMKARY
.)
JOSKfH N. FARLIT NICLEAR TLAhT '
. LICENSE N05. KPF+2 AMI NTF 8 IKfETON Col'hiY Al.AMMA
SUMMARY
RElf1RT FROH 010191 TO -123191 (A) ;
'MTDlDMOR 11TPE AND i- 1 All INDICATOR I INDICATOR IICATK$ 1 COMMist1Y I CONTROL !
TATIMY I M AL i 1 'lCATIONS I WITil fil0EST AhTJAL MMN IIEATIONS I lEAT10N ! SAMTLfD llNMBERS OF 1 N9HINAL- IFF.AN (C/D) l - - - ---+ - --- - - - ---+-l MM N (C/D) i MEAN (C/D) -
'"litt or IANn1YS15 i K C(B) Il W F(C) i KAME I Mr.AN (C/10 i RAW:E (C) i RANGE (C) !
hi.ASITEKEh7)lTERFORMED I I I DISTA U i RAR:E (C) I i
!_ 1 1 1AND DIPSCTION .I 1 l l
AIR PARTICU-10ROSS 5241 .001 _ 1 .00H208/209) I N H TERIN. l .010( 52/ 52)! .00M157/157) 1 .010(156/158)- , LATES, .IBETA I f( OD2- 0.033) II,0 MI. SSE l( 0.002- 0.03311( Oml- 0.031)l( - 0.00% 0.035) .
' (PCl/ M'.83) 1- 1- 1 I I I I I I I I I i 1 4 IEE 7 401 ,010 : I . 077( 16/ 16) IMil ITRIN. 1 .030( 4/ 4)I .023( 11/ 12) i .031(12/12)
I i f( 0.016 0.046) 11.0 M1, SSE l( 0.023- 0.0%)l t 0.013- 0.035)i( 0.016- 0.046)- 1 I I ! I J l 105-134 401 J101 l < KC - ( 0/ 16) I i l KC ( 0/ 12) 1 < Kt ( 0/ 12)
-1 1 1 'l i 1 I l
-1 l- -l l I I 1 r
- CS-137 401 M1 1 < KC ( 0/ 16) I i. I ( KC ( 0/12) 1 < KC ( 0/_12) l~ l .1 1 I I i i l i i i l I i 131- 401 #1 l ' < MDC ( . 0/ 16) l I i < KC ( 0/ 12) I < M*C ( 0/ 12) f I- 1 I .1 I I
- 1. t' I I I I I i 1 l- l l 1 .i
.l. I I I I i 1 1 1 1 1 1 1 l l l 1 I I I I I l .I I I I i l i l- 1 i i i l i i i i i i l- 1. I 1 l l l
~ T 'l ~ L1 1 i 1 !
l I i 1 I 1 l I != 1 1 i i I ,1- l- 'l I i l I l- 1 I ! I I ,
- l. I 1 I I i 1 l- I l- l' I I J
'l- 1 I I I i l 4 l' I -1 I l- 1
! -l l' 1 1 1 1 1: 1 i l i i 1
- 1. I l -. l- 1 J l 1 i i I l- 1 i l I ! ~1 I .t - 1 I I I I I I l' Y
(A) No N'mroutine Anomalous Nieutemt. nit brortd Durir1 This teriod, i /
,(B) Mean Minimum Detectable Concentration Calcufstnl Fer Table 2 of This Reget. Table 1991-01 (C) M6an anti Range of Husber of Maatervpnts Wth Detratable Activity Only. Page 1 of 1
'(D) Total Numter of Measurements T A en.
u hf
1AB12 19102. l' AIFP.ORNFi 10DlKE - OPERAtl0NAL l@!OACflVITY E!IMM8,Rf L j -- e
, =, JOSEl'Il W. FAPLEY hTIIAR P! ANT i -- 1.1CIKSE NA NPF-2 AO NTF-8 llo'# TON COUhTY ALA!'.INA E!*NSY PEfWf FM 010191 TO-123191 (A)
MEDllN OR ~ ITYTEAO 1 f ALL IOICATOR i lOlOTOR l#ATION I 00KWKitY I CONTROL FATir4Af IT07AL i I LOCATIONS 1 Wlfil E10FEST AEX MEAN I [ EAT 10):S IIICATION SAMPLID INUMBERS OF I R MINAL 1MEAN(C/D) 1 ~ ~ ~ -- --- -- -- -- - ----I MEAN (C/D) i KEAN (0/D)
- (ttN17 0F 'IANALY515 I OC(B) tRur*(c) I cxE I MEAN tc/ro i KA rt (c) i p>JcE (c)
' EAStTEMENT)lfERPOEMD) i I i DICIAICE I RAN3E (C) ! I L i I 1 1A W DilTCTION I I I AIR 10 DINE il(ti1NE 4221 .047 1 < Mhc i 0/211) 1 I ~i~ikU 0/ 9) I < OC ~ ( 0/1%)
(!T1/M"3) 1 1 1 I i l 1 l i i i i i 1
-l 1 1 I i 1 l 1 -I l' I I I I
- l l i l I I I l' l -l I l- l
,1 l I I I I I ,
I I I i l i 1 l i I I I I I i i 1 I i ! ! I i 1 I i 1 1 1 1 1 1 I i l i i t i i 1 I I I I I I i i r
-l i i 1 I I I J l ! ( I l i ,
i i 1 1 I F l l ' I l i i l I i 1 1 1 I i 1 , l- ;l l i l I i i ! l 1 l l 1 1 1 I I I I I i 1; I I I I I l- : : -) 1 l 1 1 1 I I I I i 1. l- 1- 1 I I I I
'l 1 1- l 1 1 1 :.
'l i I i l i 1 l- 1 i 1 1 I i l' l- l 1 -l I i 1 - 1. I l- 1 i 1 l I I I ! l i
.I I i l 1 i i 1 1 I I I I I l- -I
- ! -1 I I l 1- - l~ : (- 'l i 1 I
( i- t I l- i l i
- (A) !b Nonreutine Anomalous M4anuttecnts Ergotted traing This feriod.
-(B) Hean Minimut Detect.able Concentration Calculaicd Per Twtc 2 er inis Re:o.t. Table 1991-02
- (C) Mean and Range of thi&r of Meanietents With Dete: table Activity Only, Page 1 of 1 (D) Total Nu h r of Measurements faten, h
, ~ - - -...,,_.._.--.._.m_. -
..-,.-,--,-1,-
_ -. ~ - _ . 7APLE 19?l-03 EXTERNAL FADI ATION - (tDAT10NAL RAD 10AC11VITY SUMRY JOSEPli M. TAtlIY 10JCLIAR fl.Ah7
'1,10ENCE VIS, NPF-2 AND l#F 8 fl00SM C0!WTY AlA!:AFA FiMRY REP 0kT fint 310191 TO 123191 (A) -
ME01tN OR ITYTE AO - i I ALL INDICATOR I INhlCATOR !&AT]ON 1 C(MNITY l CONTROL FATINAY ITOTAL l l l/rAtl0NS I WITil lilGHECT rAhtAL EAN 1 IN ATIONS I llCATION
- SAMPlID IN'J)t# M Of I D INA1. lMEAN (CID) l - -- ------ ---- ---- -------- I MFAN (C/D) 1 MEAW h (UNIT OF- IAKAltsiS I MX(B) IRAIG(C) l KAME I MFAN (C/D) 1 FA EE (C) i FA CE (C)
QEASUREMENT)lTEkFORMED l I l DIF1A!CE 1 -RAN"E (C) I i
-l i l IAO DIRECTION I i I TLD-QUARTERICR(C3 ff01 10.C00 1 18.363( 64/ 04) 1EASTTERIM. I 24.652( 4/- 4)I 16.068( 72/ 72) i 16.1(E 24/ 24)
~<WRAb) IGAMMA I l( ll , M- 31.78) 10.8N!. E I( 20. M- 31.78)l( 9.33- 31.16)l( 10.83- 23.*14) i I I I I i l 1 i l I i 1 1 TLD-A W1AL IGROSS 401 10.000 1 53.160( 16/ 16) lEAt7 ff.klN. I 78.620( 1/ 1)I 43.630( l Al 18) 1 46.328( 6/ 6)
M AD) :10AMH4 I It 37.62- 7AAh 10.8 Fl. E I f( 35.87- 60.37)l( 37.87- Z 92) i I i 1' i 1 1 TLD ANNUAL-EIGROCS 401 10.(00 1 73.7 % ( 16/ 16) - IEAST TFklM. I 101.110( li l)I 64.275( 18/ 18) I ' 61.M3( 6/ M
- (MPAD) ICAWA l 1( $5.61- 101.11) 11.0 Ml. NE I 1( 52.91- 76.41)l( 42.67- 85.M)
,. I i 1 -I i i !
-. 1 i ! I i 1 I l l I i 1 1 I I i l I 1 1 I l l i i i i i l I i i 1 i l I
'l i I I I I i l i i i l i 1 1 1 .I I I I i 1 'I ! l I I i 1 i i i i l l I I l I- 1 I I I i 1 1 I t i I 'l 1 I I I I i l I l- l 1 1 1 I i l i i 1 1 l- 1 I I l 'l
- 1. l 1 1 1 I I I I l- 1 i i i i I i l i I i 1: 1 I I I i l l 1 l l 1 I i
-1: I I i 1 1 I l I I i i l I i 1 1 I I I I l !. I I I I i 1- 1 1 l' I I i
-l I i i 1 -1 1
_- { - : 1:- l t l- l 1 1 i -i 1 1 l ! ) = (A) }b'Nanioutine Anomalo9s Measurcunts Rarorted Dm ing This frriod. Table 199' . l -(B) Mean Minimum Detectable Concertration. (C) Hean and Range of Namter of Measurrents With Detectable Activity Only. Page 1 of 1-(D) Total kater of.Heaturements Taken.
-(E) Sum of Four Quarters for Comparative Turpc:ces m
r -: n d . IAhlI 1991 04 ) m , MllJ - OffkATIONAI EAN0 ACTIVITY SinAla -l i XCEril M, I AFlEY NTlIAR TIAkT LICENFE 105. NPF-2 Am NIF-8 Il09STON CD'J NTY Al.AMMA SiW#Y REPOPT l'MN 010191 TO 123191 (A) EDilH OR ITYPEIJO I lALLINDICATOR 8 101CATOR IfrATION I C4Mi!NITY I C0hTROL PATilWAY ITUTAl. I i 14 CAT 10NS , WIT 11 IIICRETT AKAL MFAN IIICATIONS I llrAT10N SAMPLED INMERS OF i )KHlhAL LEAN (C/D) l -- -- ----------- + ~ ~ - 1 EAN (C/ D ) i EAN (C/D)-
- (1417 OF IANALYSIS I MJC(B) IRAEE(C) l NAE I EAN (C/D) 1 FAEE (C) i RAEE (C)
EAKl%EEhillTERF0 FED I l i DISTAT E I RAEE (C)~ l I l AO DIRITTION I
=1 I I 1 1 MILX 110 DINE 27' .25S I I I I l < KC ( 0/ 27)
(TCl/L) i' I I I I i i l i i i 1 1 1 IPA-140 271 46.518 1 i i l I < OC ( O! 27) i 1 I l '. 1 1 1 1 , 1 i l i 1 l I i 105-134 271 13.074 I t i I f ( OC ( - 0/ 27) l l 1 ! 1 I f I : i l 1 I I I I i 105-137 271 12,481 l ~ l i I I( KC ( 0/ 27) l I I i 1 ! I_ ; 1 i- 1 I I I l ! IK 40 271 98.666-f i I i i 1429.259( 27/ 27)- i 1 1 1 1 1 It 1260,00 1620.00) I l= 1 1 1 I ILA-149 271 . 9.148 i l i i I ( KC ( 0/ 27) ', i l i l i i I ; i i 1- 1 I I I l_ 1 1 1 I I i 1 1 ! ! I I I i 1 I I I I I 7
.1 1 I .1 1 1 1. !
l- 'l 1 I i i i ! I I 'l .I I I I
- 1. i. I I .I I !
I i i l 1 1 I I I i l. I i i 1 -1 1 I I i l i i ! -l i I i i i l i i l i
- 1. 1. I I I I I ,
1 i i 1 i l I i i l 1 i l I i 1 l- 1 I I i
-; ~l
.l l 1 1- 1
.; ' :I .1 1 l _I i 1 ! 'l I l l I i I (A) No Ibntoutine Anosalous Measutetents Fe; cried DurJN This Petiod.
- (B) Mean Minimum Detectable Concentration Calculated rer Table 2 of this Femtt.
(C) Mean and Range of Ndtber of Mestereunts Jith I>tectable Activity Doly,
. -(D) Total Nur,bar of Mearurteents Taken.
'Tdle 1991-M Page 3 of I ;
.w.- . a - . .,- a-. . - -- .~ - -- . - - . . - . ~ - . - , - . - . ~ - - - _ x.-...-.-~.. , .
. ..- -_ , . - . - - - . . - - - - . - - ~ _ - _ . _ _ - - _
TAfilt 1991-05 VIEETATIOKi 'FDFAZ . Ori1AT10NAL FAD 10ACTRiff BIMMARY !
, , EElli W. FF1.tY NielfAR ?!.'NT
!.lCENSE HOS.-NPF 2 AtD NIf-B ikfrTON CWfY AlAt.AMA j Sl* ARY PEftRT FR N 010191 TO 123191 (A)
. MEDIUM OR ;ITYPE A0 1A!.L l O!CATOR I IIPirATOR lEAfiON i C(NWINiif I CONTROL l TAff!WAY ITUTA!, -1 i / FAT 10lM i KIT 8 Ifirmr.ST ANWAL WEAN I !/lCAT10NS 1l0 CATION l SAMP!J:D JNtHEERS OF 1 IDMIKAi, IKEAN (C/D) 1 -~ --- -------- ----- --- I NE AN (C/ D) l MEAN (C/D)
(UNIT OF lAKALY51S I KC(B) lRANf2(C) iKM i MEAK (C!D) l FA CE (C) l RAtCE (Ci 2 EiEEMEhT)lFERf0RMP 1 I l DISTAtri i FATE (C) 1 I I i l iA O DIRfrTION 1 1 I i 1 FORAGE (E) LAC-228 51-52.2r0 I 65.000( 4/ 4) 110R7a TERIN. I 67.6M( 3/ 3)I i 115.000 ( 1/ 1) (PC1/KG4*ET)I i it 57.00- 77.00) 10.8 Pl. N l( 59.0 - 77.0)I i i 1 'l i i 1 i IBE-7. 361 101.111 1 743.416( 24/ 2 0 I?JJTilTfSIM. I 737.909( 11/ 1111 1 770.363( 11/ 12) l 1 l( 138.00- If R 0n) 11.0 MI. SN 1( 1!d.0 16Ni.0)l l( IPS.CO- 1MO.00) . I i i l I I I 1B1-214 71 28.285 1 61,500( 4/ 4) IS0!Till PEFlM. I 67.333( 3/ 3)I 1 52.000( 2/ 3) _I' I- l( 38.00- 106.00) 11,0 N!. 5 2 1( 3B.O - 106.0)I i( 44.00- (0 00) i I i- 1 1 1 1 105-134' 351=15.942 i < KC -( C/ 24) 1 1 1 1 ( K)C ( 0/ 11) l L 1 I 1 1 1 1 1 l
-l 1 i i i i i
]
105-137 36i 14.083: I < MLC ( 0/ 24) 1 I I i 75.000( 2/ 12) , l' i. 1 I. I I I( 13.00-- 137.00) ^ l I i i 1 1 5
'11-131 351 16.17] I < OC ( 0/ 24) i I i 1 < KC ( 0/ 11) 1- 1 l l 1 1 1 I I I I I i i IK-40 361 109.111 1 4112.500( 24/ 24) IIDRTH TERIM. ! 4403.846( 13/ 13)I i 5125.0M( 12/12) 1 I f( 2130.004 6010.00) 10.8 M1. N l( 2130.0 -(010.0)I 1( 3400.00- 6830.00) ,
I I I i l i ! ; II'B-214 41 21,250 1 30.000( 3/ 3) IORTil f FRIM. 1. 30.0%( 2/ 2)I 1 53.000( 1/ 1) ; 1 I .I( 19.00- 41.00) 10.8 MI. N 1( 19.0 - 41.0)1 1. ; f i i i l i i 1P8212 T41 16.000 1 34.000( 2/ 3) INDRTP ITRIM, f 42.000( 1/ 1)I I bl.000( 1/ 1) 1 i 1( 26.00a 42.00) 10.R Mi, N l l !
~
l .I I I I I i ' l I _l' -l 'l i I I I l- 1 1 1 1 1 1 1 ! I i I
.I I 1 1 I i 1
=l. 1 I -1 i i i I i- l- I 1 I i 1 l- 1 ( l i I I I I i i i 1~ l- -1 I i l i l -g - .;- ;-- ;- j -; ;
[ 1 -If l~ l i l I l dA) 1b lbarettine Anomalous Menutements Reivatted During Thje feriod. (B) Mean Minimum Detectable Concentrition' Cakulated Per Tahle 2 of Titis !cuat. Table 1991-05 (C) Mean and Fange of liumber of Mosurerents With lietectable Activity Only. Page 1 of 1 (D) Blal Number of MeaGrements Taken.-
- f(E) Mean Wet / Dry Ratio for 1991 was 5.80n (f) Subeitute location Due to Unavailibity of forage During Snee Sample Periods.
,. , , . _ _ - - _ _ , _ _ _ . _. _c - _.... .____ _ _._ _ _ _ . _ . . - - _ _ . . . _, . . _ _ _ _ _ _
_x _
TAFLE b -06 Soll - OPERATIONAL LACETIVITY S!NMARY JCFfli H. l AEI.Ff Et' LEAR PLANT LICENEB N'C NPF-2 AO hTF 8 ID'rTON COPTY N M AMA S WyAFY W ORT } ROM 0)049) TO 123191 (A. MEDIUM OE ITYfE AND I lALL INDICATOR I INDICATOR LOCAT]ON 1 00MO NITY I C0hTROL FATEWAY ITOTAL i l ItrATICE I WITl! ElrliEST ANN'3h MEAN I ItrAT10E IItCATION SAMPLED INi'MBERS OF i NCHINAL IMFAN (C/D) 1 - -- - -- - - - --- - --- --- -- -- - - -~ 1 E AN (C/ D) l MEAN (C/D) ' iNM i EAN (C/D) 1 E T A (C) i RA 0E (C) NNIT OF IANALYSIS I MT(B) IEAEE(C) EA.<UREMEh'T)lf ERFCRED 1. I 1 D157ANCE I RANCE (C) I 1 1 I I I AO DIECTION I I s . _ . _ $ SOIL IAC-228 111 303.T9 1 12 % .000( 5! 5) IStX'Ill TERIM. ! 1420.0 m( 1/ 1)I 1091.000( 3/ 3) I 1970.000( 3/ 3) ^ (IN SITU) 1 1 l( 114').00- 1420.00) 11.0 M1. SSE 1 It 873.00- 1390.00)l( 1190.00- 2980.00) (PCl/TG DRY)] I I ! I i 1 l i 1 i i I i IP!-212 81 792.875 I 881.250( 4/ 4) ISOUTl!PERIM. I1210.000( 1/ 1)I 1270.000( 1/ 1) I 20'0.000( 1/ 3) I i 1( 702.00- 1210.00) 11.0 MI. SSE I
- I I i I I i I i list -214 111 168 363 1 1025.200( 5/ 5) IWEST PERIM. ! ID9.0m! 1/ 1)I 918.000( 3/ 3) I 1669.0f.6( 3/ 3) 1 I l( 717.00- 1730.00) 10,9 Mt. W9W I 1( 757.00- 1150.00)l( 799.00- 2270.00) l I i 1 1 I I ICS-137 111 40.363 1 151.000( 5/ 5' IWES' PEklM. I 279.000( 1/ 1)I 159.333( 3/ 3) i 122.333( 3/ 3)
I i f( 70.( 4 279.00) 10.8 MI. WNW I 1( 78.00- 242.00)!( 75.00- N .00) l I I I I I I IK-40 111 480.545 1 5218.000( 6! 6) lEAST PERIM. Il4900.0m( 1/ 1)I 107R.333( J/ 3' .' 2225.000( 2/ 2) I i l( E78.00-1410.0) 10.B MI. E i l( 835.00- 1450.0 'l( 1120.00- 3330.00) 1 1 1 I I I I ITB-214 111 274.090 ! a32.000( 5/ 5) IES1 TEKlM. I 1700.000( 1/ 1)I R96.333( 31 3) I 1783.333( 3/ 3) l t 1( 773.00- 1700.00) 10.9 M1. EW l l( Phl.00- 955.00)ll 1110 00- 2200.00) I i i l i I i IFB-212 111 278.727 1 782.600( 5/ 5) 1004T!! TERlH. I T6.000( 1/ 1)I 174 f46( 3/ 3) I 1308.000( 3/ 3) 1 1 1( 575.00- 906 m) 11.0 Hl. SRW I 1( 587.00- 93A.00)l( PO4. 1930.00) i l i I I I i IRA-226 111230.000 i i i l i 1310.000( 1/ 1) I i ! I I I I I I I I I I I ITL-208 lit 106.131 1 405.800( 5/ 5) IHORTH ffRIM. I 519.000( 1/ 111 347.6fA( 3/ 3) ! 714.fA6( 3/ 3) i I l( 315.00- M9.00) 10.8 Mt. N I 1( 231.00- 410.00)lt 428.00- lim.00) I I I I I I i i I i i l i l 1 I i l 1 I I I I I I I I i 1 I I t i I I , I i i I I I i l I I I I I I i 1 1 1 I I I i l i I I I I I t i I I I i 1 I I i i I I
! ! I I I (A) No Ncmroutine Arralom Measurer +n% bwlM for M This fertrA.
(B) Hean Minien Detactable Concer.ttatmn C,1rulatM fe: Trble 2 of This h;ert. Table 1991-06 (C) Moan and Fange of Nutter of Measurements With Detectable Activity Daly. Page 1 of 1 (D) Total Number of Measurerents Taken
TABLE 1991 07 hATEFFDFKE: S:3FAC8 WATER - OPERATIO!M RAn10 ACTIVITY
SUMMARY
FCEPH M. FARLEY h1' LEAR PLAKT LICENSE N% NTF-2 AND Nff-8 II0030N COUNTY ALARAMA SUMMAAY FFrORI EROM 010141 TO 123191 (A) MEDIUM OR ITYFF.AND 1 I ALL !!DICATOR I IN'JICATOR IKATION i C M MUN11Y l CONTROL FATl!WAY ITMAL 1 1 1/1 CAT 10NS I 91Tli lilCEW ANNUAL MEAN 1 lE AT10NS I IICATION SAMPT{D IN'JMPERS Of i N11NAL IMEAN (C/D) l -- -- -- - -- - ---- - - -- - - - - --- - - - I MflN ( C / C ) i MEAN (C/D) (liNIT OF 1 ANALYSIS I KC(B) IkANGE(C) I NAME I MEAN (C/0) i RATE (C) i RAWE (C) MEASUREMEKf)lTERF0D(FD I I I DISTANCE I RAEE (C) i I i 1 I LAND DIRFl' TION I I I SURFACE ITRITILH Bl 100.0% i 122.000( 2/ 4) IGREAT SOUTERNI 122.000( 2! 2)I i < KC ; 0/ 4) WATER (RIVER)I i 1( 117.00- 127.CO) IFAPER CO. l( 117.0 - 127.0)I I (PCl/1.) l I i 1RIV. M1. 40 1 i I I i i I i l I licA-140 231 17.434 1 < K10 ( 0/ 11) i I I I < M'C ( 0/ 12) i l i i i l i I I l 1 i i i 1C5-134 231 4.478 l < KC ( 0/ 11) I I i 1 < KC ( 0/ 12) l I I I 1 1 I i 1 I I I I i 105-137 231 g.347 1 < MC ( 0/ 11) i I I i < KC ( 0/ 12) i I I I I I i l i i l I I i 1C0-58 241 3.875 1 < KC ( 0/ 12) 1 I I 1 < KC ( 0/ 12) i I I I i i 1 I i l l I I I 100-60 241 3.83) I < KL ( 0/ 12) 1 I I i < KC ( 0/ 12) i I I I I i l i 1 i i l IFE-59 24l 8. lf;6 1( MDC ( 0/ 12) i I i 1 < KC ( 0/ 12) l I I I I I I i I i I 1 I i ILA-140 241 3.375 1 ( KC ( 0/ 12) 1 I i 1 < KC ( 0/ 12) i I I ! I I I I I I i l i I IF33-54. 241 3.916 i < MDC ( 0/ 12) I i I i < KC ( 0/ 12) i i 1 I i 1 I i i i l i l l INB-95 24l 3.958 i < KX' ( 0! 12) 1 I I I < MDC ( 0/ 12) i I I I I I I i l i i l i 1
.lZN-65 241 8.416 1 < MC ( 0/ 12) i I I i < K)C ( O! 12) 1 I I I I I I l l 1 i i l i 12R-95 241 6.875 i( MDC ( 0 / 1. ) l I I I < MtC ( 0/ 12) i I I I I I I l
(A) No Nonroutine Anor,alous Measurements Femrted During This Period. (B) Mean Minirm Detectable Concontration CalculattJ Ter Table 2 of This R9; ort. (C) Hean and Range of Navier of Mesuom.ts With DetectaWe Activity Only. Table 1991-07 Page 1 of 1 (D) Total NaMr of Measurer.ettr: Takn.
TABLE.- 1991-08 UATERPORNE: CR000 WATFX - (CERATIONAL RADIDACTIVITY Sit #ARY-c;- , .
.10CEril M.- TARLEY h"JCLEAR PLANT
_ LICENSE J. hTF-2.AND hTF-8 BOUSTON C0t'NTY ALAPMA
SUMMARY
REPORT FRt* 010191 TO 123151 (A)
- .H WlUM OR _ITYPE AND .l- I ALL"101CATOR I 1CICATOR LOCI.fl0N I CCNHUNITY l C0hTROL t PATINAY ItotAL I liLOCATIONS 1 WITH !!!GHES1 ANNUAL EAN- l LOCATIONS 1(KATION SANTLED= -lWUMBERS OF l NOMINAL ; LEAN (C/D) l----- - -------------- ----------i HEAN (C/D) i HEAN (C/D)
(11 NIT OFT l ANALYS!S: !! KC(B) lFANGE(C)- I NAE I MEAN (C/D) 1 RANCE (C) i RANG 3 (C)
? MEASUREMENT)lPERFORXED 1: 'I I DISTANCE I RAVIE (C) i I I' -- 1. 1 -LAND DIRECTION I 1 'l CROUND L1100lNET 31 .245 1 < KC ( 0/ 4) -1 I I i < KC ( 0/ 4$
UATER(ELL) 1 I I I i i i (PC1/L) :l 1 l- 1 l l l l' 1- -i i l I i ITRITIUM 81 100,000 - I < KC ( 0/ () l I I I < OC ( 0/ 4) , 7 1 l i l I i i
!! l. I I I I I IBA-140 81 17.500 1 < KC ( 0/ 4) l I I i < HDC ( 0/ 4) 1- 1 1 1 1 1 i l- 1 i 'l I i l 10S-134 di 4.625 I( HDC ( 0/ 4) l I I i < KC ( 0/ 4) 1- 1 I I -l I l l- l' I I ! I I 10S-137 "81 4.250 i < MDC ( 0/ 4) i I I I < 00 ( 0/ 4) -
I. ,1 1 I I 'l I-l~ -I 1: I i I !
-100-58 81- 3.875 1 < KC - ( 0/ 4) l I I i < HDC ( 0/ 4)
- 1. I- 1 i i I i 1 I I i i 'I
- 81 -4.125 I ( OC ( - 0/ 4) i < KnC ( 0/ 4)
'100-60 i I I I' I :l 1 i I I i l i 1 -l l I IFE-59 81' 8 500 I-< HDC ( 0/ O I I I I < HDC ( 0/ 4) 1 -l- 1. I i i 1 l- .I I I I i 1
-(LA-140- 81 3.875 :1 < MDC '( O! 4) 1 I- 1 i < MDC ( Or 4)-
1: I I I I I 'l i .1 ; 1 I i i 1
= lMN-54; 81. 4.125 l < KC .( 0/ :41 .I 1 1 l < 00 ( 0/. 4) 1.-- 1 l' I I I I LI: 'l I- i I I I
.INB-95 .81 4.375 I .( HDC- ( 0/ - 4 ) - 1 1 I' I < MDC ( O! 4)
! [i : l- 1 l i I I l- -l 1. I I i ! IZN 81 8,750 -I.< HDC -( 0/ 4) 'I i i I < HDC ( 0/ 4)-
'l.
If ll l 1 I I l- l' -1 i I 1 i IZR95- ' 81 -7.250 t ( KC - ' U 4) -I i i I < MDC - ( 0/ 4) , l l- 1 l- 1 I i 0 l 1- I l- 1 i
~(A)'No Nontoutine Anomalous Heazartments Reported Durino This Period.
- 1(B) Hean Minirum Detectable Concentration Calculated Per Table 2 of This Report. Table 1991-08 L '(C) Hean and Range of Number of Measuremente With Detectable Activity Only.- Page 1 of 1
- (D) Total Naber of Heasurements Taken.
--. , _ = . . . _ _ . _ . . - . . _ . _ . _ . . . , _ - . , __ _._ ~.
TAltLE 1991-09' SEDIMMf: ELVER - OPERATIONAL KAD10 ACTIVITY F M ARY i KCErl! M. FARLEY hiCLFAR Pl.AVf IICENCE lEC. hTF-2130 Nff-8 ITUSTON CO'!NTY 111.BAMA S M ARY REPOPT FROM 010'91' TO 123191 (A) EDllM OR ITYPE AD 1 1 All INDICATDR I INDICATOR LOCATION I CCWWIY l C0hTROL FATEWAY iTCrfAL i I [KATIONS I WITli lilGREST ANNUAL MEAN I IE ATIONS I l(CATION SAMPLED IKUMisERS OF i NOMIEAL iMEAN (C/D) l - -- - - - - - - - - - ---- --- - -- - - -- -- - - - - i EAN ( C/ D ) i EAN (C/D) (UNIT OF IANAl,YSIS l WC(B) iRAV1E(C) i NAWE I EAN (C/D) i PAVIE (C) l FAVIE (C) MEASUPEMEh7)lFEkFORED I I I 0! STANCE I U T;E (C) 1 I I I i 1AND DIRECTION I I I SEDIMEhi IAC-228 41 139.500 1 2819.000( 2/ 2) IFMITirS BEND i 2899.000( 2/ 2)I i 1675.000( 2/ 2) (RIVER) 1 1 1( 75R 00- 5040.00> 1RIV. M;. 41 l( 7b8.0 - W O.6)1 l( 1530.00- 1820.00) (TCl/FG-0RY)l i I I I I 1 1 1 I I I I I 1B1 212 41 640.250 I 3279.500( 2/ 2) ISHITil'S FFE I 3779. W H 2< 2H I 2025.000( 2/ 2) l l 1( 87).00- % 60.00) IPlV. MI. 41 1( 893.0 WO OM 1( 1910.00- 2)(0.00) i l 1 I i 1 1 IBI-214 46 BR.750 1 12.03.500( 2/ 2) ISMITitS'S BEND 1 1203.500( 2/ 2)I I 902.000( 2/ 2) i i 1( 347.00- 2060,00) lRIV. MI. 41 i( 347.0 - 20m.0)1 f( 815.00- 909.00) i I i ! I I i 1C5-134 41 44.(00 1 < KC ( O! 2) 1 I I l < H30 ( 0/ 2) i I I I i 1 I I i l i l I i 10S-137 41 51.500 i < MnC ( 0/ 2) i I i 1 ( KC ( 0/ 2) i I I I I i i l i I I I I I II-40 41 223. 2 1 2225.030( 2/ 2) ISMITil'S BEND 1 2225.0n0( 2/ 2)I I 3130.000( 2/ 2) 1 I 1( 1 8 0.00- 2570.00) 1RIV. MI. 41 1( 18F0.0 - 7570.0)I l( 2630.00- 3630.00) I 1 1 1 1 I I IFB 214 41 43.500 1 1263.000( 2! 2) trMITirs SEND 1 1263.000( ?' 2)I 1 969.000( 2/ 2) I I l( $16.00- 2210.00) IRIV. MI. 41 f( 316,0 - 2210.0)I l( 918.00- 1020.00) I 1 1 I I I I IPis-212 41 86.500 1 2212.500( 2/ 2) ISMITirS BEND I 2212.50)( Zi 211 1 1205.000( 2/ 2) I ! l( M5 00- 3930.00) IP!V. Fi. 4) l( 4%.0 - 3Plu)I l( 1010.00- 1340 5.) l 1 1 1 1 ! I IRA-226 41 010.000 1 1511.000( 2! 2) 1.~d!TirS EDID 1 1511.0 tot 2i 2)! l 935.000( 2/ .' ) l I It 372,00- 2650J0) lRIV. HI. 41 1( 372.0 - N O.0!! 1( 720.00- 1150.00) i I i l I i i ITL-208 41 48.250 1 1024 500( 2/ 2' ISMITirS FEND 1 1021.W M ?! 2)I I 5RO.000( 2/ 2) i i 1( 259.00- 1710.n0) IRIV. Ml. 4: l( 27 0 - 7 0.0)I l( 541.00- 619.00) i i i i I i i l i 1 ! l I I I I I i i I I i 1 ! ! 1 I I I I I i 1 I I i l I i I i l I i i I I I i l I i l i ! l I I I I I I I (A) No Nontoutine Ancmalous Heaturennts Pepntted During This Period.
@ Me u Minirco Detectable Concentration Calcul & d Trr Table 2 of This Fe; ort. Table 1991-09 (C) Hean and Ranae of N W r 01 Mcasorerents With l'etectable Activity Only. Page 1 of 1 (D) Total Number of Measuremnts Tann.
TABLE 19?l 10 l.' FISH: ELVER! GAME N1PERATIONAL EAD10 ACTIVITY 'S!W M Y
-,_ ,_ XCEffi M. FARLEY NUCLEAR Pl>NTI LICENSE 105. hTF-2 AND NFF 8110USTON COUhTY AMBAMA SlHMARY RFPORT FRCH 010191 TO 123191 (A)
' MEDilH OR ITYPE AND :I lALL INDICATOR' 1 INDICATOR LOCATION -I COMMUNITY- l C0!(TROL
-FATHWAY ITOTAL 1 1 LOCAT10NS I ' WITH RIGEST ANNUAL MF.AN i IEATIONS I LOCATION
= SAMTIID INUMBERS OF i !OHINAL IMFJsN (C/lo I ------ - - - - ---- ------- --- ---- - -- - I EAN (C/ D ) i MEAN (C/D) c !(UNIT OF = IANALYSIS I KC(B) 1 RANGE (C) 1 NAME l -- EAN (C/D) l RANGE 'C) I RANGE (C)
E ASUREMEhi)lFERFORMED 1 i .I DISTANCE I RANGE (C) 1 I I I- I LAND DIRECTION I I I FISB(CAME ) 105-134 4727.250-1<MDC -( 0/ 2) l- 1 I i < KC ( 01 - 2) (FCl/KG) i 1 i 1- 1 I I UET TISSUE I l- 1 I- 1 i 1
-1 I i i l I I
-tCS-137 41 25.500~! 36.000( 1/ 2) ITNiTB'S BFN]-l 36.000( 1/ 111 1~ 24.000( 1/ 2) i I I IRIV. MI. 41 I I I I I .I i i l l 100-58 41-25.000 1( KC ( 0/ 2)
- 1 I I I( HLC ( 0/ 2) 1 -1 I I I I I l! I i- 1 I I i 100-00 fi 31.250 i < KC ( 0/ 2) 1 I i 1, KC ( 0/ 2) i I I I I f i 1 l 1. .i I I I L IFE41 41 67.250 1 < Mlle ( 0/ 2) ! I i i < KC ( 0/ 2) l I i l I i i
~l- .I I I I I I (X 41179.500 1 2815.000( 2/ 2) ISMITH'S BEND i 2815.09. ;/ 2)I i 3650,000( 2/ 2) l- l l( 2VA00- 2940.00) IRIV. MI. 41 l( 2690.0 - z940.0)I 1( 3370.00- 3930.00) 1 l 1 I- 1 I I INN-54 41. 2'.500 :1 < MDC ( 0/ 2) I i i i < MDC - ( 0/ 2)
- 1. I I l i I I I I I I i l i IZW-65 41.64.500 i < KC ( 0/ 2) l I i 1 < KC ( 0/ 2) l- 1 I I I I I
-1 I I I i l- I l- 1 1 1.- l 1 1 I I I I i 1
'l -l I- 1- I l l l l l I I I I l
-1: I i 1. 1 1 I l l 1 1 I I i 1 l i l I i I i l l I I I i i 1 -l i I i I l El I l l l 1 I
.- l ' 1 1 1 1 I -1 1 1 I i ! 1 1. i
- -l I l' I I I i l I l -1 1 1 1 1 l
-(A) No Emroutine Arealons Measurermnts Ferorted Datit:0 This Period.
.(B) Mean Minimum Detectable Concentratiren calcolated fer Table 2 of This Regrt. Table 1991-10 (C) Mean and Range of Number of Measurements With Detectable Activity Only. Page 1 of 1 (D) Total Number of Measurements Taken.
TA?iE 1991-11 flS!!: FlVER (Pt1TTON lEEDING)-0rERAT10K4L RADIDACTIVITY TWMARY JOSErli M. fARLEY NUClfAR PLAhi LICENFE NDS. NPE-2 AND NPF-8 Il09STON COUhTY A!JUMA SI M ARY FEr0FT FFOM 010191 TO 123191 (A) MEDitH OR ITYPE A O 1 l ALL INDICATOR I INDir"r0R llEATION I CMMUNITY l C0hTR01. FATEWAY iT0fAL i i IEATIONS 1 FITH nlGHF.ST ANNUAL MU N I LOCATION 3 I IK ATION SAMPLED INUMBERS Of i NOMINAL IMEAN (C/D) l-------- ---------------- ----- I MEAN (C/D) l MEAN (C/0) (UNIT OF lANALYSIS I HDC(B) IRANUE(C) i NAME I MEAN (C/D) 1 RANCE (C) l FA10E (C) i(FASUREMEhT)lfERFORMED 1 1 1 DISTANTE I RANGE (C) 1 I I I I LAND DilGCTiON I I I FISS (BUfTOMICS-134 41 27.750 1 < KC ( 0/ 2) I i 1 i < KC ( 0/ 2) FEEDING) l I I I I I I i 1 1 I I (PCl/KG) 1 I FFT TISSUE I I i i i i i ICS-137 41 26.000 1 < KC ( 0/ 2) i I i 1 < MDC ( 0/ 2) l I I I l l l l l l i I I I 100-58 41 '.S.500 1 < KC ( 0/ 2) l I I i < KC ( O' 2) i I I I I I i I I i i i I i 100-60 41 29.250 i < MDC ( 0/ 2) l I I i < M'C ( 0/ 2) I i 1 1 1 1 1 1 1 I i i l i IFE-59 41 64.750 1 < KC ( O! 2) i I I I < OC ( 0/ 2) i I i i l I I I I I i ! i i IK 40 41 163.250 l 27?0.D.10( 2/ 2) ICM]Til'S FEND I 27 % 000( 2/ 2)I I 3095.000( 2/ 2) i i 1( 2450.00- 3110.00) IRIV. Mt. 41 l( 2450.0 - 3110.0;l l( 2190.00- 3203.00) I I i I i i i IMN-54 41 24.000 1<F ' O! 2) i I I I < KC ( 0/ 2) I i i i i I i i i l I I I I IZN-65 41 60.500 1 < KC ( 0/ 2) i I i i < MDC ( 0/ 2) 1 I I 1 1 I I I i l I i i i i i I I i I I I i l i i i l i l l I i I l 1 1 1 1 I i l I I i I I i i
! l l 1 i i i i l i I i i l i I I I i i i l i t i I i 1 i i l I I I i 1 1 I i 1 1 I I I I I I I I I I I I I I I I I I I I I I
( A) No Nontoutine Anomalem Measutomants fvportni DunnJ This Period. (B) Mnan Minimum Detectable Concentratica Calculatul Enr Table 2 of This Pemrl . g g 1991 y (C) Hean and Range of Nmber of Heasarerente With Det ectable Activity Only. (D) Total Number of Measurements Taken.
ATTACHMDR 1 \ . LAND USE SURVEY FOR RADIOLOGICAL DWIRONMENTAL MONI'IORING PROGPM JOSEPH M. FARLEY NUCLEAR PLAIR JUNE 7, 1991 This Land Usc Survey was performed to meet the requirements of the Farley Units 1 and 2 Technical Specifications, Section 3.12.2 and 4.12.2. A. Houston County, Alabama Lamar Nichols, Houston County Livestock Agent, was contacted for the purpose of reviewing known locations of milk animals in theMr. county. He knew of no individually owned milk cows in the county. Thomas Dean of Gordon, AL, still has milk goats at his residence located in sector 08, 6 miles from ne. A house-to-house canvas of Alabama residents in a five-mile radius of the plant was conducted along Highways 95 and 52, Houston County Roads 42, 33, 75 and the interconnecting light-duty roads. No milk animals were located. Individuals interviewed were: Mr. John Griffin, Mrs. Terry Martin, Mrs. Adair Gilbert, and Mrs. Sandra Long. Simultaneous with the milk animal survey, the nearest resident in each meteorological sector was identified. There were no new residents found closer to the site bcundary than those identified in the ODCM. B. Early County, Georgia Mr. Micky Fouracres, Early County Extension Agent, was contacted to determine if any milk animals were currently present in the county. He knew of no milk animals in Early County. A house-to-house canvas of residents in the area across the Chattahoochee River east of Farley Nuclear Plant revealed no milk animals within 5 miles of the plant site. The census of Georgia residents was conducted along Highways 62 and 370, Early County Roads 219, 239, 140 and the interconnecting light-duty roads. Individuals interviewed were Mr. Frank Loveless, Mrs. Martha Jean Knighton and Mrs. Eunice Harper. Simultaneous with the milk animal survey, the nearest resident in each meteorological sector was identified. No new residences were found closer to the site beundary than those previously identified in the ODCM. C. Results and Conclusions The results of the Land Use Survey are shown in Table 1 of Attachment 1. The survey located milk goats 6 miles from FNP; however, no action is required for animals located outside a 5 mile radius. Therefore, based on the survey results, no change in the present milk sampling program is required. I Attachment 1 Annual ENV Report /6 Page 1 of 2
- ~ - _ - - _ - _ - - _ .
TABLE 1 or ATTACHMENT 1 JOSEPH A FARLEY NUCLEAR PLANT LAND USE SURVEY JUNE 7, 1991 (DISTANCE MILES 'IO NEAREST) RADIAL SEC'IORS (22.5 DEGREES) PISIDENI' MILK ANIMAL North Northeast (01) 2.5 >5 Northeast (02) 2.4 >5 East Northeast (03) 2.4 >5 East (04) 2.8 >5 East Southeast (05) 2.8 >5 Southeast-(06) 3.4 >5 _ South Southeast'(07) >5 >5 Sotith (08) 4.3 >5
- South Southwest (09) 2.9 >5 i Southwest (10) 1.2 >5 West Southwest (11) 2.4 >5 West _(12) 1.3 >5
-West Northwest (13) 2.1 >5 Northwest (14) 1.5 >5 North Northwest (15) 2.0 >5 North (16)- '2.6 >5 i
Attachment 1 Annual EIN Report /6 Page 2 of 2
~
J. M. Faricy~ Annual Environmental Operating Report sooear pian Mean Annual Air Gross Beta X
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-X- CS-137 Control -EE- I-131 Control - X CS-137 MDC - Or I-131 MDC
' Attachment 2' Page 8 of 28
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J. M. Farley xoacar Annual Environmental Operating Report Plant Mean Annual Milk Concentration M __-._g _ - . _ _ _ - _ _, 1E+04 _ _ -t
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-X- K-40 Control -f I.A-140 Control A- K-40 MDC Ci LA-140 MDC l i Attachment 2 Page 9 of 28
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-X- Indicator -E- Control -W- MDC L ---
" Attachment 2 Page 11 of 26
b' d E J. M. Farley - - - - wooear . A2mual Environmental Operating Reaort: Plant
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