ML20042E919
| ML20042E919 | |
| Person / Time | |
|---|---|
| Site: | Farley  |
| Issue date: | 12/31/1989 |
| From: | Hairston W ALABAMA POWER CO. |
| To: | NRC OFFICE OF INFORMATION RESOURCES MANAGEMENT (IRM) |
| References | |
| NUDOCS 9005040103 | |
| Download: ML20042E919 (44) | |
Text
{{#Wiki_filter:-. , - q Alabam2 Power Company 40 inverntss Cinttr Parkway Post Office Box 1295 Birmingham. Alabama 35201 Telephone 205 P,68 5581 W. G. Hairston,111 Senior Vice President Nuclear Operations AlabamaPower the southern electrc system April 30,1990 , 4 Docket Nos. 50-348 50-364 l U. S. Nuclear. Regulatory Commission ATTN: Document Control Desk Washington, D.C. 20555 : Joseph M. Farley Nuclear Plant 1 Annual Environmental Operating Report 5 Radiolcaical Gentlemen: The attached " Annual Environmental Operating Report, Part B: Radiological"- for calendar year 1989, is transmitted in accordance with the Joseph M. Farley fluclear Plant Unit 1 and Unit 2 Technical Specifications Sections 6.9.1.6 and s 6.9.1.7. If you have any questions, please advise. ' Respectfully submitted, I l p.
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cc: U. S. Nuclear Reaulatory Commission Mr. S. D. Ebneter Mr. G. F. Maxwell Mr. S. T. Hoffman State of Alabama Director, Division of Radiation Control l State of Georaia Director, Environmental Protection Division l [d 9005040103 891231 - t ADOCK0500g8 DR
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z: h r h ALABAMA POWER COMPANY ANNUAL DNIRONMDEAL OPERATING REPORT PART B: RADIOLOGICAL , JOSEPH M. FARLEY NUCLEAR PLANT , UNIT NO. 1 LICENSE NO. NPF-2 AND UNIT No. 2 LICENSE NO. NPF-8' ; PERIOD ENDING DECEMBER 31, 1989
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CONTROL SAMPLING LOCATIONS FOR AIRBORNE ENVIRONMENTAL RADI0 ACTIVITY IN THE FARLEY NUCLEAR PLANT AREA. FIGURE 3.12 3 11
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4 f t~i> i _ g} t E & DAM ! to Mitt $ [ rarity"$llAAPLANI , r tARivc00Nrr A1Hf0R0 % h - 5 GORDON j HOUS!0N COUNTY ALABAMA INDICATOR STAil0NS CONTROL STAil0NS E $URfAct ANDGROUNDWAftR $URfAct WAftR. FISH AND $tDIMtNT X FISH AND StDIMtNT GROUND WATER INDICATOR AND CONTROL SAMPLING LOCATIONS FOR WATERBORNE ENVIRONMENTAL RADI0 ACTIVITY . IN THE FARLEY NUCLEAR PLANT AREA FIGURE 3.12 4 12 '-
- 1
o L TABLE 1 . SCOPE OF OPERATIONAL PADXOI/Xi! CAL DNIRONMENTAL MCNI'IORING PROGRAM AT THE FARLEY NUCLEaJt PLAfC DURING 1989 Principal Type of Number of Sanpling Stations Pathway Sanoles _ IndTeator Consnunity Control Airborne Particulates 4 3 3 Airborne Iodine 4 1 3 External Radiation 16 18 6 Airborne i Milk - - 1 i Forage' 2 - 1 Soil' 6 3 2 River Water 1 - 1 Groundwater 1 - 1 Waterborne River Fish 1 - 1 River Sediment 1 - 1
- rotage sampling in lieu of vegetable and fruit. Vegetable and fruit sampling-discontinued witFimplementation of Unit 1 Technical Specification Upgrade (Amendment No. 26, issued March 1, 1982).
b Annual In Situ Gama Measurements continued by choice of licensee during 1989. 13 Annual FNV Report /3
l
'DBLE 2 i
OUILINE OF OPf2ATICNPL RADIOUJGICAL DNIBCNEfDL MONITORING PROGRAM EOR FARLEY NUCLEAR PLANT DURING 1989 Types of Samples b and Sampling Sampling Locations Type and Frequency and of (Distances Given in Miles) Collection Frequency Analysis ! AIRBORNE Particulates Continuous operation of sampler with Particulate sampler sample collection being performed as required by dust loading, but at least Analyze for gross beta once per 7 days. radioactivity > 24 hours Indicator Stations: following filter change. Perform <f==ma isotopic North Perimeter (N-0.8) analysis on each sample South Perimeter (SSE-1.0) when gross beta activity Plant Entrance (WSW-0.9) is >10 times the yearly River Intake Structure (ESE-0.8) mean of control samples. Perform ry==mm isotopic E rn===w11ty Stations: analysis on composite (by location) sample at Columbia, AL. (N-5) least once per 92 days. Great Southern Paper Co. (SSE-3) Ashford, AL. (WSW-8) Control Stations: Blakely, Ga. (NE-15) Dothan, AL (W-18) Neals Landing, FL. (SSE-18) Iodine continuous sampler operation Radiciodine canister with charcoal canister Analyze at least once Indicator Stations: collection performed once per 7 days for I-131. per 7 days. North Perimeter (N-0.8) South Perimeter (SSE-1.0) Plant Entrance - (WSW)-0.9 River Intake Structure (ESE-0.8) Annual ENV Report /4 Page 1 of 5
TABLE 2 (con'd) i Types of Samples and Sampling Type and Frequency Sampling Locations and of j (Distances Given in Miles) Collection Frequency Analysis reummwlity Stations: Great Southern Paper Co. (SSE-3) Control Stations: Blakely, GA. (NE-15) Dothan, AL. (W-18) Neals Landing, FL. (SSE-18) Soil Annual in situ Ge(Li) gamma-ray c.ammaa Isotopic spectroscopy measurements. Annually Indicator Stations: Six Stations along the plant perimeter (NE-1.0, E-0.8,
" SSE-1.0, SSN-1.0, WSW-0.9, and Ntw-0.8)
Consunity Stations: Columbia, AL. (N-5) Great Southern Paper Co.(SSE-3) Ashford, AL. (WSW-8) Control Stations: Blakely, Ga. (NF-15) Dothan, Al. (W-18) DIRECT RADIATION At least once per 92 days c.a=== dose Headout at least once per 92 days Annual ENV Report /4 Page 2 of 5
'IRBLE 2 (con'd)
Types of Samples and Sampling Sampling Iocations Type and Frequency and of (Distances Given in Miles) Collection Frequency Analysis Indicator I Stations: Sixteen stations, one in each meteorological sector along the plant perimeter (N-0.8, I@iE-0.9, NE-1.0, DIE-0.9, E-0.8, ESE-0.8, SE-1.1, SSE-1.0, S-1.0, SSN-1.0, SW-0.9, WSW-0.9, W-0.8, NNN-0.8, NN-1.1, and leaW-0.9) . Indicator II (cne-wiity) Stations: Eighteen stations, one in each meteorological
- sector at a distance of 4-5 miles (leiE-4, NE-4, D3E-4, E-5, ESE-5, SE-5, SSE-3, S-5, SSW-4, SW-5, WSW-4, W-4, NNW-4, NF-4, felW-4, and N-5). Additional stations located at WSW-8 and SW-1.2.
g Control Stations: Blakely, Ga. (NE-15) Neals Landing, Fl. (SSE-18) Dothan, AL. (W-18) Dothan, AL. (W-15) Webb, AL (W-11) Haleburg, AL (N-16) mTERBORNE Surface Water Composite taken with propor- Monthly gamma isotopic tional semi-continuous sampler, analysis of each composite Indicator Station: having a minim m sampling fre- sample. Tritita analysis quency not exceeding two hours of each composite sample collected over a period $ 31 days. at least once per 92 days. Great Southern Paper Co., (3 miles below plant discharge, River Mile-40) Annual DIV Report /4 Page 3 of 5 1
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D BLE 2 (con'd) Types of Samples and Sampling Sampling Locations Type and Frequency and of (Distances Given in Miles) Collection Frequency Analysis Control Station: Upstream of Andrews Lock and Dam (-3 miles above plant intake, River Mile-47) Ground Water Grab sample taken at least r - isotopic and tritium once per 92 days. analyses of each sample Indicator Station: once per quarter. Great Southern Paper Co., Well (SSE-4) Control Station: Whatley Residence, Well (SW-1.2) River Sediment Grab sample taken at least r - isotopic analysis once per 184 days. of each sample twice per year. Indicator Station: M.mstream of plant discharge at Smith's Bend (River Mile - 41) Control Station: Upstream of plant discharge at Andrews Lock & Dan Reservoir . (River Mile - 47) Annual DIV Report /4 Page 4 of 5
DBLE 2 (con'd) Types of Samples and Sampling Type and Frequency Sampling Locations and of (Distances Given in Miles) Collection Frequency Analysis Ilta.di10N Milk 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 on pasture. Fish Indicator Station: One sample of the following c - isotopic analysis species at least once per 184 on edible portions once days: 1. Game Fish per 184 days.
- 2. Botton Feeding Fish Downstream of plant discharge e in vicinity of Smith's send (River Mile - 41)
Control Station: Upstream of plant discharge in Andrews Lock & Dan Reservoir (River Mile - 47) Forage Grab sample cut from green Gasuna isotopic analysis forage at least once per 31 which includes I-131 days. analyses of each monthly Indicator Station: sample. North Perimeter (N-0.8) South Perimeter (SS&-l.0) Control Station: Dothan, AL. (W-18) Annual ENV Report /4 Page 5 of 5
TABLE 3 ut.lu.nCE CAPABILITIES EIR DNIBCNENIAL SAMPLE ANALYSIS EUR FARIEf 20 CLEAR PIJNr VALUES EDR 'IHE MINIFKM DETECTABLE CCNCDFIRATICN(FOC)* ** Airborne Particulate Water or Gap Fish Milk Food Products Sediment Analysis (pCi/1) (pCi/m ) (pCi/kg. wet) (pCi/1) (pCi/kg. wet) (pCi/kg. dry) Gross beta 4 1 x 10-2 g , , , H-3 2000 m m m m m Mn-54 15 m 130 m m m Fe-59 30 m 260 m m m co-58, 60 15 m 130 m m m In-65 30 m 260 m a m Zr-95 30 m m m m m Nb-95
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15 m m m a m I-131 1* 7 x 10-* m m m m Cs-134 15 5 x 10-* 130 15 60 150 Cs-137 18 6 x 10-* 150 18 60 180 Ba-140 60' E R 60 m m La-140 15 m m 15 m m Page 1 of 2 J
TABLE 3 (con'd) I
'The MDC is the smallest concentration of radioactive material in a sample that will be detected with 95% probability with 5% probability '
of falsely concluding that a blank observation represents a "real" signal. ror a particular measurement system (which may include radiochemical separation): MDC = 4.66 S, ' E V 2.22 Y exp (-Aot) Where MDC is the "a priori" lower limit of detection as defined above (as picoeurie per unit mass or volume). S is the standard deviation of the background counting rate or ! oIthecountingrateofablanksampleasappropriate(ascounts , per minute). E is the cout. ting 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 radiochemical yield (when applicable). , A is the radioactive decay constant for the particular l radionuclide. At is the elapsed time between sample collection (or end of the sanple collection period) and time of counting (for environmental samples, not plant effluent samples). The 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 counting rate or of the counting rate of the blank samples (as appropriate) rather than on an unverified theoretically predicted i variance. In calculating the MDC for a radionuclide determined by gama-ray spectroscopy, the background shall include the typical l contributions of other radionuclides normally present in the samples (e.g., Potassium-40 in milk samples). Typical values of C, V, Y and at i shall be used in the calculations. l She MDC's for Tritium, Gross beta, and Radioiodine were obtained using , blank background (a priori), whereas, for gama-ray spectroscopy
- actual sample backgrounds were used (a posteriori).
*MDC for drinking water.
E i l l 20 Page 2 of 2
M LE 4 REPORTING LEVELS FOR RADIOPCTIVITY CONCENIRATICNS IN DIVIROPMENIAL SAMPLES Reporting Levels Airborne Particulate Water or Gay Fish Milk Food Products Analysis (pCi/1) (pCi/m ) (pCi/1tg. wet) (pCi/1) (pCi/kg.' wet) H-3 2 x 10** m m m m Mn-54 1 x 10' m 3 x 10' m n 2 Fe-59 4 x 10 m 1 x 10' m m co-58 1 x 10' m 3 x 10* m m co--60 3 x 10' m 1 x 10* m m 2 S Zn-65 3 x 10 m 2 x 10' m m Zr/Nb-95 4 x 10* NA m m M I-131 2 0.9 m 3 1 x 10' Cs-134 30 10 1 x 10' 60 1 x 10' Cs-137 50 20 2 x 10' 70 2 x 10' Ba/La-140 2 x 10* NA m 3 x 10 2 ,
"For drinking water samples.
Arnual ENV Report /4(7)
TABLE 5 SAMPLING AND ANALYSIS DEVIATIONS DURING 1989 Conponent Time Period Reason for Deviation /Coments Air Monitoring Station 1/12/89-2/2/89 Samples missing due to electrical 0701 cables being severed during road construction. Power restored 2/3/89. Air Monitoring Station 1/26/89-2/2/89 Samples missing due to oil leakage 1108 from pump. Pump, motor pulley and fan I belt replaced on 1/3/89. 1 Air Monitoring Station 2/2/89-2/8/89 Low air volume due to filter being : 0215 loaded with dirt. Air Monitoring Station 2/2/89-2/8/89 Low air volume due to low flow, riow 0701 rate adjusted to 90 scfh. l Air Monitoring Station 2/8/89-2/16/89 Low ait volume due to excessive dirt 0703 loading the filter. Air Monitoring Station 2/16/89-2/23/89 Low air volume due to lowered air 0501 flow. Flow rate adjusted to 90 scfh. l Air Monitoring Station 2/23/89-3/2/89 Low air volume due to loss of power. 0703 Transformer replaced on 2/27/89. ; Air Monitoring Station 3/9/89-3/16/89 Low air flow due to a defective air 0501 totalizer. Totalizer replaced on 3/17/89. - Air Monitoring Station 3/30/89-4/6/89 Samples missing due to a blown fuse. 1101 ruse replaced 4/6/89. Air Monitoring Station 4/13/89-5/20/89 Sample missing due to a broken 1605 muffler. Muffler replaced 5/20/89. Air Monitoring Station 5/18/89-11/14/89 Samples missing due to the power 1601 cables being cut during road work. Power restored on 11/13/89. Air Monitoring Station 6/13/89-6/20/89 Low air volume due to a blown fuse. 0703 ruse replaced 6/20/89. . Air Monitoring Station 6/13/89-6/20/89 Low volume due to a blown fuse. 1101 ruse replaced 6/20/89. # TLD 1601 2nd Quarter, 1989 TLD missing. TLD fell from the stand and was damaged by mower. Annual ENV Report /12 22 Page 1 of 2 1
l TABLE 5 (con'd) ; Component Time Period Reason for Deviation / Comments Air Monitoring Stati m 7/3/89-7/11/89 Low air volume due to a broken fan , 0701 belt. ran belt and motor pulley , replaced on 7/22/89. . Air Monitoring Station 7/3/89-7/11/89 Samples missing due to a broken fan 1605 belt, ran belt replaced on 7/11/89. ' Air Monitoring Station 8/1/89-8/8/89 Low air volume due to a failed motor. ' 0215 Motor replaced on 8/11/89. Air Monitoring Station 8/8/89-8/15/89 Low air volume due to the new motor 0215 being wired backwards. Motor rewired 8/12/89. Air Monitoring Station 8/22/89-8/29/89~ . Low air volume due to a blown fuse. I 1101 ruse replaced R/29/89. Air Monitoring Station 9/19/89-9/26/89 Sanples missing due to a loose fan 0501 belt. ran belt replaced on 9/27/89. ' Air Monitoring Station 9/26/89-10/3/89 Samples missing due to a blow fuse. 0701 ruse replaced 10/3/89. Air Monitoring Station 10/3/89-10/10/89 Samples missing due to a failed punp. ; 0501 Pump replaced on 10/11/89. - Air Monitoring Station 10/10/89-10/17/89 Samples missing due to oil leakage from
- 1818 pump. Pump replaced 11/12/89.
Air Monitoring Station 10/24/89-10/31/89 Low air volume due to failed pump. 0718 Pump replaced 10/26/89. I Air Monitoring Station 12/5/89-12/12/89 Sanples missing due to work being 1108 performed at substation. Power to air monitor was turned off. Air Monitoring Station 12/5/89-12/12/89 Low air volume due to broken fan motor. 1601 ran motor replaced 12/10/89. Annual ENV Report /12 23 Page 2 of 2
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ATTACHMENT 1 l LAND USE SURVEY FOR RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM > JOSEPH M. FARLEY NUCLEAR PLANT JUNE 6-9, 1989- : Wis Land Use 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 the county. He knew of no individual milk cows in the county. He did give information concerning milk goats owned by Mr. Thomas Dean of Gordon, AL. The residence is located in sector 08, 6 miles from FNP. 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. Walter Whatley, Mrs. Jerry Carpenter, Mrs. Ezzie Respress, and Amanda Ryals. Simultaneous with the milk animal- survey, the nearest resident in each meteorological sector was identified. A new residence was found in Sector 14; however, it is located less than 100 yards from the present closest residence in that sector. There is no , difference in mileage from the plant to these residences. We new residents were William and Amanda Ryals. 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 individual milk animals nor dairies in Early County. A house-to-house canvas of residents in the area across the Chattahoochee River east of Farley Nuclear Plant revealed several goats in Sectors 5, ESE & 6, SE. he. goats were not being milked. There were no milk cows located. 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. Tony Knighton, Mr. Mark Lovett, and Mrs. Mary Allums. Simultaneous with the milk animal survey, the nearest resident in. each meteorological sector was identified. No new residences were found. 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. : Annual ENV Report /6 36
4 TABLE 1 OF ATTACHMENT 1 JOSEPH M. FARLEY NUCLEAR PLANT LAND USE SURVEY JUNE 6-9, 1989 , (DISTANCE MILES M NEAREST) RADIAL SECMRS (22.5 DEGREES) RESIDENT MILK ANIMAL North Northeast (01) 2.5 >5 Northeast (02) 2.4 >5 , East Northeast (03) 2.4 >5 2.8 >5 East (04) 5 East Southeast (05) 2.8 >5 i Southeast (06) 3.4 >5 South Southeast (07) >5 >5 South (08) 4.3 >5 f South Southwest (09) 2.9 >5
~
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 L l Annual ENV Report /6 37}}