ML18051A838
| ML18051A838 | |
| Person / Time | |
|---|---|
| Site: | Palisades  |
| Issue date: | 12/31/1983 |
| From: | Johnson B CONSUMERS ENERGY CO. (FORMERLY CONSUMERS POWER CO.) |
| To: | James Keppler NRC OFFICE OF INSPECTION & ENFORCEMENT (IE REGION III) |
| References | |
| NUDOCS 8404060377 | |
| Download: ML18051A838 (30) | |
Text
Consumers Power Company Palisades Plant - Docket 50-255 1983 RADIOLOGICAL ENVIRONMENTAL MONITORING REPORT Covering the Period from January 1 through December 31, 1983 March 30, 1984 8404060377 831231 PDR ADOCK 05000255 R PDR 27 Pages OC0384-0014AA-NL02
A. INTRODUCTION The data obtained by an analysis of samples taken. during 1983 was statis-tically analyzed at the 95% confidence level by the method described in Consumers Power Company internal procedures RSD-E-03. The data was statically evaluated against two criteria. The first is the statistical level which indicates the analysis of samples taken from near sites are higher than those taken from remote control sites but the difference is not significant. The second is the report level (two.times the statis-tical level) which is the minimum detectable difference that exceeds zero
- at a 95% confidence level. Doses to the public will be evaluated if the report level is exceeded.
B. DISCUSSION AND INTERPRETATION OF RESULTS
- 1. Air Samples Statistical analysis of the airborne particulate sample data between perimeter and control sites did not exceed reporting level. In many instances, control sites sample values were higher than the perimeter site values.
No I-131 activity was reported above minimum detectable levels.
A total of 624 samples were collected and analyzed; however 6 sample results were deleted from statistical evaluation due to low and/or estimated sample volumes. The missing sample resu.lts do not indicate any significant reduction in the overall sample program. Technical Specification sensitivities were met and no reportable leyels exceeded.
The results are consistent with actual effluent releases and site-specific meteorology .
. 2. Lake Water Statistical analysis between the plant lake water intake and the South Haven treated drinking water samples showed that statistical levels for gross beta or tritium were not exceeded. The plant lake water outlet samples contained tritium above the statistical limit; nowever, this is consistent with monthly reported tritium effluent releases. Lake water outlet samples for the months of.March and September were analyzed for gross beta when initial sample results were above the administrative notification limit of 10 pci/L {both were 11 pci/L). The sample reanalysis data placed gross beta levels at 7 pci/L and 6 pci/L respectively. Technical Specification sampling and sensitivity requi.rements were met.
IC0383-0013A-RS01
- 3. Drinking Water See lake water and well water discussion.
- 4. Well Water Statistical sample data analysis between the site well supply and two off-site locations showed that the statistical level was not exceeded. The State Park off-site control location has been histor-ically higher in gross beta concentrations than either the township park off-site well or on-site well locations. Technical specifica-tion sampling and sensitivity requirements were met, except for the May Palisades well sample. The sample was inadvertently mislabeled and sent in for analysis. The laboratory, because of the sample's conflicting identification, disposed of it. The missing.sample does not significantly affect the program.
- 5. Milk No problems were encountered in obtaining milk samples for 1983.
Statistical analysis of sample data between site and control locat~ons showed that reporting levels for Sr-90 and Cs-137 were not exceeded.
I-131 was less than detectable for all samples. The results of the milk sampling program provides reasonable assurance that plant .
effluent* releases .d~d not result in exposure to the public in excess of 5% of 10 CFR 20 limits. Technical Specification sampling and sensitivity requirements were met.
- 6. Sediment Statistical analyses of sediment data was done using control samples from the Ludington Pump Storage Facility (located approximately 200 miles North of South Haven) and site samples. Gross beta results did not exceed a statistica-1 significance level.* In many cases the control sample beta values were higher than the site values. Sr-90 was reported in 9 of the 13 sites, to include all 5 control sites.*
No reportable Sr-90 levels were reached. This is consistent with published environmental data showing residual amounts of Sr-90 in Lake Michig~n from- weapons testing. Levels of Sr-90 from 1983 and 1982 samples are within 10% of each other. _No detectable levels of Cs-137 were found at any sample location. Technical Specification sampling and analysis requirements were met.
IC0383-0013A-RS01
- 7. Organic - Fish and Crops The reportable limits for organic sample results are based on Technical Specification 4.11.2. S_r-90 results ranged from <,005 pci/gm to .024 pci/gm with no detectable levels of Cs-137 found.
These analytical results are approximately 15% less than those results reported in 1982. Technical Specification sampling and analysis requirements were met.
8; Gamma Dose - TLD There were no missing TLD's during 1983. Statistical analysis of TLD data was done by comparing all indicator locations to control locations. No monthly, quarterly or annual analyses exceeded the statistical level. The Palisades gamma dose sampling program consists of 21 TLD stations: 10 directly on-site; 8 off-site (1-7.5 mi); and 3 control locations. In separate comparison of off-site TLD data and on-site TLD data to the control TLD locations, the on-site locations had an average of 9.8 mr/month to an average of 10.4 mr/month for control TLD's. The off-site TLD's average 10.5 mr/month. This is consistent with expected results based on reported effluent releases. Statistical analysis of the annual TLD stations indicate a statistical level of 5.4 mR/yr would have been detected if present. Technical specification analysis sensitivities were met.
C.
SUMMARY
Only one required Technical Specification analysis was missed in 1983.
That sample is discussed in B.4. Six of the six hundred twenty four air samples collected in 1983 were deleted from the statistical analysis because of estimated flows due to meter malfunctions. Three of the malfunctions occurred in the last two weeks of December due to the extremely cold weather.
All Tech Specification analysis requirements were met except for sample noted above.
Technical Specification requirements for calibration of air samplers meters was met.
The missing or deleted results did not constitute a significant reduction in the overall program and no special reports per T.S. 6.9.3.2 were made on 1983 requirements.
D. 1983 data analysis was done by Eberline Laboratories. In 1984, the analysis will be performed by Teledyne Isotopes Laboratory, Northbrook, Illinois.
IC0383-0013A-RS01
E. ATTACHMENTS Tables RSD-E-03A, B, C, Das required by Technical Specification 6.9.3.1.B.
Sample location maps Trend graphs of analytical results IC0383-0013A-RS01
page 1 of 4 TABLE RSD-E-OJA Environmental RadiologlcaJ Monitoring Program Summary Palisades Nuclear Plant, Docket DPR-20 Van Buren County, Michigan, January 1, 1983 to December 31, 1983 Analysis and Lower Limit All All Nonroutine Medium or Total Number of of Indicator Locatlon with Highest Control Reported Pnthway Sampled Analyses Performed Detection( a) Locations Annual Mean Locations Measurements((:)
.Unit of Meas1irement LLD Meari(b) Name Mean(b) Hean(b)
Range(b) Distance & Direction Range(b) Range(b)
Air (pCi/m 3 ) Gross Beta 624 0.01 (464/468) KZ 35 mi SE .032 (154/156) None
.03 (.01-.09) ( .01-.07) .03 (.Ol-.07)
I-131 624 0.02 all LLD N/A LLD None J
, Lake Water Gross* Alpha 24 1.0. (0/12) Discharge <1 (<1) (0/12) <1 None (pCi/l) <1 (<1)
Gross Beta 24 1.0 (12/12) Discharge 4.7 (1-11) (12/12) None 4.7 (1-11) 3.6 ( 1-8)
Tritium 24 100.0 (12/12) Discharge 604.2 (12/12) None 604.2 ( 100-2200) ( 100-2200) 168,3 ( 100-380)
Drinking Water Gross Beta 12 . 1.0 (pCi/l) Control lake and well water samples are drinking water supplies.
Tritium 12 100.0.
Well Water Gross Beta 35 1.0 (11/11) State Park 6.1 (24/24) None (pCi/l) 2.2 ( 1-6) (1 mi N) (3'-9) *4.4 ( 1-9)
IC0383-0013A-RS01
Page 2 of 4 TARLE RSD-E-03A Environmental Radi.ological Monitoring Program Su~
Palis~des Nuclear Plant, Docket DPR-20 Van Buren County, Michigan, January 1, 1983 to December. 31, 1983 Analysis and Lower Limi.t All All Nonroutine
' Medium or Total* Number of of Indicator Location with Highest Control Reported
- Pathwal Sam~led Anallses Performed Detection( a) Locations Annual Mean Locations Measurements Unit of Measurement LLD Mean(b) Name Mean(b) Mean(b)
Range(b) Distance & Direction Range(b) Range(b)
Ml.lk I-1.31 48' .5 (0/36) All LLD NA 0/12 LLD None (pCi/l)
Sr-89 48 5.0 (0/36) All LLD NA 0/12 LLD None Sr-90 48 1.0 (36/36) GM (5 mi SE) 5.7 (12/12) None 4.7 ( 1-12) (2-12) 4.6 (1-11) j Cs-137 48 1.0 (36/36) GM (5 mi-SE) 4.9 (12/12) None 4.9 ( 3-9) ( 3-9) 4.8 ( 4-5)
KK (5 mi N) 4.9
( 3-7)
Other Gamma l.O (0/36) NA NA (0/12) LLD None Gamma Exposure TLD (Monthly) 252 l.O (216/216) ST-04 (3.5 mi ESE) 10.9 (36/36) None (mil/Month) 10.4 (4.7-14.5) (9-13.6) 10.4 (6.6-14.4)
- ~
(mR/Quarter) TLD (Quarterly) 84 (72/72) ST-06 (4.75 mi NE) 19.5 *(12/12) None 16.9 (13.5-22.6) (18.1-22.6) 17.l (15-19.9)
TLD (Annually) 21 (18/18) ST-05 (3 mi E) 57.1 (3/3) None 46.6 (42.1-57.1) '*9. 9 (45.0-54.8)
Crops Gross Beta 20 1.0 (20/20) RB (4.75 mi NE) 32 None None (pCi/g Wet) 9.8 (1.3-28) Cabbage N/A Sr-89 20 0.025 (0/20) NA None None MLD IC0383*0013A-RS01
Page 3 of *4 TABLE RSD-E-03A Environmental Radiological Monitoring Program Summar:z:
Palisades Nuclear Plant, Docket DPR-20 Van Buren County, Michigim, January l, 1983 to December 31, 1983 /
Analysis and Lower Limit All All Nonroutine Medium or Total Number of of Indicator Location with Highest Control Reported Pathway Sampled Analyses Performed Detection( a} I.ocations Annual Mean Locations Measurements
' LLD Mean.(b) Name Mean(b) Mean(b)
Unit of Measurement Range(b) Distance & Direction Range(b) Range(b)
Crops Sr-90 20 0.005 (16/20) RB (4.75 mi NE) .028 None None
.012 (.005-.032) Cabbage (NA)
Cs-137 20 0.08 (0/20) NA None None MDL I-131 20 o.oa. (0/20) NA None None MDL Other Gamma* 20 0.1 (0/20) NA None None MDL Sedi.ment Gross Beta 13 1.0 (8/8) North Boundary and 13.3 (5/5) None
.t (pCi/g Dry) 7.7 (4.6-13.3) Ludington S Pier (NA) 9.7 (6.8-13.3)
Sr-89 13 . 0.025 (0/8) NA (0/5) None All LLD LLD *~
Sr-90 13 0.005 (4 /8) : North Boundary .124 (5/5) None 0.45 (.005-.124) (NA) .057 (.036-.087)
Cs-137 I *13 0.08 (O/f}) NA (0/5) . *None All LLD LLD Other Gamma 13 0.1 (0/8) NA (0/5) None All LLD LLD IC0383-0013A-RS01
Page 4 of 4 TABLE RSD-E-03A Environmental Radiolog.ical Monitoring Program Summary Paliiades Nuclear Plant, Docket DPR-20 Van Buren County, Michigan, January 1, 1983 to December 31, 1983 Analysis and Lower Limit All All Nonroutine Medium or Total Number of of Ind lea tor Location with Highest Control Reported Pathway Sam~led Analyses Performed Detection(a) Locations Annual Mean Locations Measurements Unit of Measurement LLD Mean(b) Name Mean(b) Mean(b)
Range(b) Distance & Direction Range(b) Range(b)
Aquntf.c . Grqss Beta 10 1.0 (10/10) Vicinity of discharge 9.1 None None (pCi/g Wet) 9.1 (3.4-16.7) (3.4-16. 7)
Sr-89 1.0 0.025 (0/10) NA None None All LLD Sr-90 10 0.005 (5/10) Vicinity of discharge .015 None None
.015 (.005-.043) (.005-.043)
Gamma 1.0 . 0.1 (0/10) NA None None All LLD Cs-137 10 0.08 (0/10) NA None None All LLD
- ~
- a. Nominal Lower Limit of Detection (LLD) .as defined in HASL-300 (Rev 8/73), pages D-08-01., 02, and 03.
- b. Mean and range bas.ed upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parentheses.
- c. Nonroutine reported measurements are defined in the Palisades Technical Specifications, Section 6.9.3.2.
IC0383-001.3A-RS01
.. ' ... .. . . .. : ~:. . .. .. ~ .. ." ... ' *. .. ; ' -. ' ... . .
- t, TABLE RSD-E-OJC PALISADF.S NUCLEAR PLANT JANUARY 1, 1983 TO DECEMBER 31, 1983 SAMPLING AND ANALYSIS
SUMMARY
Number of Samples Frequency Medium Description Location Collected Type of Analysis of Analysis Air Continuous at All; as identified on 624* Gross Beta, I-131 Weekly/12 Approx 1 CFM Table RSD-E-03B Lake 1 Gallon Intake, Discharge 24 Gross Beta, Gross Alpha, Tritium Monthly/2 Water Composite Drinking 1 Gallon South Haven 12 Gross Beta, Tritium Monthly/I Water-Lake Composite j
Well 1 Gallon Site, TP,. SP 35 Gross Beta *Monthly/3
.. ~
Water Grab Milk 1 Gallon
- SDF, GM, KK, GH 48 I-131, Sr-89 and Sr-90, Cs-137 Monthly/4 Grab Isotopic Gamma Continuous All; as identified on .252 TLD Dose Monthly/21 Dose Table RSD-E-03B 84 Quarterly/21 21 Annually/21 Crops Grab JS, PR, RB, HS, TH 20 Gross Beta, Isotopic, Whe~
Sr-89 and Sr-90, Cs-137, Availabie-Sediment Grab Discharge, N & S Site 13 Gross Beta, Isotopi~ When Boundary, 5 miles North Sr-89 and Sr-90, Cs-137 Available Ludington (control)
Aquatic Grab Intake, Discharge 10 Gross Beta, Sr-89, Sr-90,. When Gamma Available.
- 6 results deleted because of me~er or sampler malfunctions.
IC0383*0013A-RS01
Page 1 of 3 :
TABLE RSD-E-03D llIGll, LOW AND AVERAGE CONCENTRATIONS FOR lllGllEST AVERAGE SAMPLING LOCATION PALISADES NUCLEAR PLANT JANUARY 1, 1983 to December 31, 1983 Medium Type of Analysis(l) Location High Low Average(5)
Air Gross Beta KZ Kalamazoo 35 mi SE .01 pCi/m 3 .07 pCi/m 3 .032 pCi/m 3 I-131 All LLD <.02 pCi/m 3 Lake Water Gross Beta Discharge 11 pCi/l 1 pCi/1 '
4.7 pCi/l Gross Alpha Discharge <1 pCi/1 <1 pCi/1 <1 pCi/1 Tritium Discharge 2200 pCi/l 100 pCi/1 604.2 pCi/l Drinking Water Gross Beta See Table RSD-E-03A Tritium(4)
- See Table RSD-E-03A Well Water Gross Beta State Park (1 mi N) 9 pCi/l 3 pCi/1 6.1 pCi/1 (l)Minimum detectable level (MpL) = air, gross beta 0.01 pCi/m 3 , I-:131 0,02 pCi/m 3 ; water, gross beta 1.0 pCi/1, gross alpha 1.0 pCi/l, H-3 100 pCi/l; milk, I-131 0.5 pCi/l, Sr-89 5.0 pCi/l, gamma isotopic 1.0 pCi/l; crops and sediment, gross beta 1,0 pCi/g, Sr-89 0,025 pCi/g, Sr-90 0.005 pCi/g, gamma isotopic 0.05 pCi/g; some samples may have higher MDLs due to sample size, shipRing delays or statistical phenomenon.
(2)Samples. collected monthly in season.
(3)Two"samples per location.
(4)Tritium analysis performed on South Haven treated only.
(S)Only samples greater than LLD included in average.
(6)Includes transit dose which averages approximately 6.4 mRlround trip.
IC038J-0013A-R$01
P11ge 2 of 3 TABLE RSD-E-03D HIGH, LOW AND AVERAGE CONCENTRATlONS FOR HIGHEST AVERAGE SAMPLING LOCATION PALISADES NUCLEAR PLANT JANUARY 1, 1983 to December 31, 1983 Medium Type of Analysis(l) Location High Low Average
.* Milk I-131 All LLD Sr-89 All LLD Sr-90 GM (5 mi SE) 12 pCi/l 2 pCi/l 5.7 pCi/l Cs-137 GM (5 mi SE) 9 pCi/1 3 pCi/l 4.9 pCi/1 KK (5 mi N) 7 pCi/l 3 pCi/1 4.9 pCi/l j
Other Gamma All LLD Gamma Dose(6)- TLD (Monthly) ST-04 (3.5 mi ESE) 13.6 mr 9 mr 10.9 mr TLD (Quarterly) ST-06 (4.75 mi NE) 22.6 mr 18.1 mr 19.5 mr TLD (Annual) ST-05 (3 mi E) 57.1 Crops(2) Gross Beta RB (4.75 mi NE) 32 pCi/g 6 pCi/g 15.3 pCi/g Sr-89 All LLD Sr-90 RB- (4,75-mi N~) .028 pCi/g .006 pCi/g .015 pCi~g All LLD Other Gamma All LLD IC0383-0013A-RS01
Page 3 of 3 TABLE RSD-E-03D llIGll, I.OW AND AVERAGE CONCENTRATIONS FOR llIGHEST AVERAGE SAMPLING LOCATION PALISADES NUCLEAR PLANT JANUARY l, 1983 to December 31, 1983 Medium Type of Analysis(!) Location High Low Average Sed:l.ment(3) Gross Beta North Boundary and Ludington 13.3 pCi/g 4.6 pCi/g 9.5 \>Ci/g S Pier Sr-89 North Boundary Sr-90 ~ m:I. north .124 pCi/g <.005 .058 Cs-137 All LLD Other.Gamma All LLD Aquatic Gross Beta Discharge 16.7 pCi/g 3.4 pCi/g 9.1 pCi/g All LLD Sr-90 Discharge .043 pCi/g .005 pCi/gm .015 pCi/g Gamma All LLD
- ~
IC0383*0013A-RS01
page 1 of 3 TABLE RSD-E-03B SAMPLING LOCATIONS PALISADES NUCLEAR PLANT Sample Ill Q) Q)
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1 ST Palisades Nuclear Plant x x x x x x 2 TH Tower Hill Farms x x x x RR3, Coloma, Michigan 5 miles S 3 HS Herbert Soderberg x x x RRl, Covert, Michigan 5 miles S
- 4 JS Jerry Sarno x x x x RRl, Cov~rt, Michigan 3~ miles SE 5 PR Paul Rude x x x x RRl, Covert, Michigan 3~ miles ESE 6 RB Richard Bus x x x x RR3, South Haven, MI 4-1/4 miles NE 7 SD Sherman Dairy x x x South Haven, Michigan 6 miles NNE
- TLD P-22 is a control in lead cave at station 4.
- Station 7 .a was added to
- the program in January 1984.
page 2 of 3 TABLE RSD-E-03B SAMPLING LOCATIONS '!'
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13-21 Pl3-P21 Perimeter of Palisades x
- 23 SN25 Emergency Siren 25 x 3 miles ENE
- 24 SN21 Emergency Siren 21 x 3-1/3 miles E 25 SH South Haven, Michigan x x 5-1/2 miles NNE 26 GM Glenn Miller x Rt 1, Box 20 Covert, MI
. 4.3 miles SE -
27 KK Kenneth Kemp x Rt 4, Box 32 South Haven, MI 8 miles NE
- Stations 23 and 24 were added to the program in
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- Control sample is obtained 6 months of the year from Hudsonv"ille Creamery, Burnip, Michigan (35 miles NE), and the other 6 months from the Constantine Dairy, Constantine, Michigan (48 miles SE).
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03/28/B 1983 .PALJ.S:4DES AIR P~4RTICULA.TE DOff'A(:.JAC-C0.1\7TROL VS SHERMAN DAIRY, R.BUS, P.RUDE
. WEEKLY GROSS BETA PC!/Cf.I.BIG METER PCI 0.12.5
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WEEK LEGEND: LOCATION ~ * ~ DOWAO-C 39 SSE ....._.__... P.RUDE 3 E a a s R.BUS 4.75 NE 4 4 & S DAIRY 7.5 NNE
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General Offices: 1945 West Parnall Road, Jackson, Ml 49201 * (517) 788-0550 March 30, 1984 James G Keppler, Administrator Region III US Nuclear Regulatory Connnission 799 Roosevelt Road Glen Ellyn, IL 60137 DOCKET 50-255 - LICENSE DPR PALISADES PLANT - 1983 RADIOLOGICAL ENVIRONMENTAL MONITORING.REPORT Attached is the 1983 Environmental Monitoring Report for the Palisades Plant.
This covers the period January 1 through December 31, 1983 and is submitted in accordance with Technical Specification 6.9.3.1.B.
Brian D Johnson Staff Licensing Engineer CC Director, Office of Nuclear Reactor Regulation Director, Office of Inspection and Enforcement NRC Resident Inspector - Palisades Attachment If:.* ~5
- \ 1 OC0384-0014AA-NL02 APR 3 1984