ML18051B349

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Radiological Environ Monitoring Rept,1984. W/850416 Ltr
ML18051B349
Person / Time
Site: Palisades Entergy icon.png
Issue date: 12/31/1984
From: Frisch R
CONSUMERS ENERGY CO. (FORMERLY CONSUMERS POWER CO.)
To: James Keppler
NRC OFFICE OF INSPECTION & ENFORCEMENT (IE REGION III)
References
NUDOCS 8504300119
Download: ML18051B349 (32)


Text

ATTACHMENT Consumers Power Company Palisades Plant Docket 50-155 1984 RADIOLOGICAL ENVIRONMENTAL MONITORING REPORT Covering the Period from January 1 through December 31, 1984 April 16, 1985 30 pages IC0385-0099A-NL04

1 A. INTRODUCTION The data obtained by an analysis of samples taken during 1984 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 statistically 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 statistical level) which is the minimum detectable difference that

~xceeds zero at a 95% confidence level. Doses to the public will be evaluated if the report level is exceeded. A total of 32 analytical results (15-Sr89, 15-Sr90, and 2-gross beta) were unavailable from the laboratory contractor in the following sample categories: 1) aquatic -

fish, 2) food crops, and 3) bottom sediments at time of report prepara-tion. A supplemental report will be issued when the sample results are received. Palisades was off-line for most of 1984 due to an extensive refueling outage. Power generation was resumed on November 22, 1984.

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 peri-meter site values.

No I-131 activity was reported above minimum detectable levels.

A total of 627 samples were collected and analyzed; however 18 sample results were deleted from statistical evaluation due to low and/or estimated sample volumes. The missing sample results do not indicate any significant reduction in the overall sample program.

Technical Specification sensitivities were met. July air sample results exceeded the statistical levels but not any reportable limits.

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; however, this is consistent with monthly reported tritium effluent releases. There were no gross beta releases above the administra-tive notification limit of 10 pCi/l from lake-out discharge.

Technical Specification sampling and sensitivity requirements were met.

IC0385-0099A-NL04

2

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 historically higher in gross beta concentrations than either the township park off-site well or on-site well locations. To establish the cause of the higher State Park well water gross beta concentrations, a comparative K-40 analytical study between the State Park off-site well and the Palisades site well was initiated October 1984. Well water samples taken since June 1984-on have been analyzed. Results are inconclusive at this time. All Technical Specification sampling and sensitivity requirements were met.
5. Milk No problems were encountered in obtaining milk samples for 1984.

I-131 and Cs-137 were less than detectable for all sample locations.

Statistical analysis between site and control locations initially indicated that Sr-90 levels exceeded the reporting level. The difference between the means of the near site locations and the control locations was 1.29 pCi/l. The validity of this value is questionable because of an abnormally low control value. Values for 1984 for both Big Rock Point and Palisades were lower than 1983 values, as expected, from fallout decay. In addition there were no values for Sr-89 or Cs-137 above LLD values in the 1984 analysis results. The control value for Big Rock in 1984 was 2.3 pCi/l while Palisades was 1.5 pCi/l. In the years 1983 through 1984, Palisades had a control value over 1 pCi/l higher than Big Rock Point. For the above reasons and the fact that Palisades had been off-line during late 1983 and most of 1984, the positive indication is invalid. Copies of the milk analysis are attached. This trend will be closely monitored in 1985.

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 statistical significance level. In many cases the control sample beta values were higher than the site values. The results of 10 analyses (5-Sr89 and 5-Sr90) were unavailable to complete a full data report for sediment samples; however initial results on 7 completed analyses from 12 samples indicate that Sr89 levels are MDL with Sr90 quantities being slightly above LLD limits.

No reportable Sr89 or Sr90 levels have yet been reached. Levels of Sr90 from 1984 and 1983 samples appear to be within 4% of each IC0385-0099A-NL04

1-1 3

other. No detectable levels of Csl37 were found at any sample location. Technical Specification sampling and analysis require-ments were met.

7. Organic - Fish .and Crops A total of 22 analyses results (10-Sr89, 10-Sr90 and 2-gross beta) were unavailable to complete a full data report for organic samples; however, initial results on 16 completed analyses from 26 samples indicated that reportable limits of Sr90 (from Technical Specifica-tion 4.11.2) were not exceeded. Sr90 results ranged from <.005 pCi/gm to 0.009 pCi/gm with no detectable levels of Csl37 found.

Technical Specification sampling and analysis requirements were met.

8. Gamma Dose - TLD There were 5 reported missing TLD's during 1984 with an additional 4 TLD reader cards being damaged (unreadable) at the laboratory.

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 23 TLD stations: 10 directly on-site; 10 off-site (1-6 mi); and *3 control locations. In separate compari-son of off-site TLD data and on-site TLD data to the control TLD locations, the on-site locations had an average of 5.1 mR/month to an average of 5.3 mR/month for control TLD's. The off-site TLD's average 5.5 mR/month. This is consistent with expected results based on reported ef(luent releases. Technical Specification analytical sensitivities were met.

C.

SUMMARY

No required Technical Specification analysis was missed in 1984.

Eighteen of the 627 air samples collected in 1984 were deleted from the statistical analysis because of estimated flows due to meter malfunctions.

1. Technical Specification requirements for calibration of air sampler meters was met.
2. A supplemental 1984 Palisades Annual Report will be forthcoming as soon as the 32 analytical results from 16 samples become available.
3. The missing or deleted results did not constitute a significant reduction in the overall program and no special reports per Techni-cal Specification 6.9.3.2 were made on 1984 requirements.

D. The 1984 data analysis was done by Teledyne Isotopes Midwest Laboratory, Northbrook, Illinois.

IC0385-0099A-NL04

4 E. ATTACHMENTS Tables RSD-E-03A, B, C, D as required by Technical Specification 6.9.3.1.b.

Sample location maps.

Trend graphs of analytical results.

Milk sample results from Teledyne Isotopes Midwest Laboratory.

IC0385-0099A-NL04

Page 1 of 4 TABLE RSD-E-03A Environmental Radiological Monitoring Program Summary Palisades Nuclear Plant, Docket 50-255 Van Buren County, Michigan, January 1, 1984 to December 31, 1984 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) Locations Annual Mean Locations Measurements(c)

Unit of Measurement LLD Mean(b) Name Mean(b) Mean(b).

Range(b) Distance & Direction Range(b) Range(b)

Air (pCi/m 3 ) Gross Beta 627 0.01 (457/468) GR 55 mi NNE .03 (152/159) None 0.02( .02-.03) (.007-.087) 0.02(.02-.03) 1-131 627 0.02 all LLD N/A LLD None 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 2.4(1.2-3.6) (12/12) None 2.4(1.2-3.6) 2.3(1.1-3.0)

Tritium 24 100.0 (12/12) Discharge 490.8 (12/12) None 490.8(100-1570) (100-1570) 189.2(100-400)

Drinking Water Gross Beta 12 LO (pCi/l) Control, lake and well water samples are drinking water supplies.

Tritium 12 100.0 Well Water Gross Beta 36 1.0 (12/12) State Park 4.8 (24/24) None (pCi/l) 1.4(1-1.8) (1 mi N) (2.4-9.3) 3.2(0.7-9.3)

MI0385-0059A-NL04

Page 2 of 4 TABLE RSD-E-03A Environmental Radiological Monitoring Program Summary Palisades Nuclear Plant, Docket 50-255 Van Buren County, Michigan, January 1, 1984 to December 31, 1984 Analysis and Lower Limit All All Nonroutine Medium or Total Number of of Indicator Location with Highest Control Reported Pathwa:z: SamEled Anal:z:ses Performed Detection( a) Locations Annual Mean Locations Measurements(c)

Unit of Measurement LLD Mean(b) Name Mean(b) Mean(b)

Range(b) Distance & Direction Range(b) Range(b)

Milk I-131 48 .5 (0/36) All LLD N/A 0/12 LLD None (pCi/l)

Sr-89 48 5.0 (0/36) All LLD N/A 0/12 LLD None Sr-90 48 1.0 (36/36) GM (5 mi SE) 2.8 (12/12) None 2.8(1-4.5) (2.1-4.2) 1.5(1-2.6)

Cs-137 48 1.0 (0/36) All LLD N/A 0/12 LLD None Other Gamma 1.0 (0/36) N/A N/A 0/12 LLD None Gamma Exposure TLD (monthly) 276 1.0 (234/240) ST-18 (.75 mi SE) 5.9 (36/36) None (mR/month) 5.3(3.3-11.1) On Perimeter (3.9-11.1) 5.3(3.9-7.2)

(mR/quarter) TLD (quarterly) 92 (78/80) ST-04 3.5 mi ESE 19.5 (12/12) None 15.4(12.2-27.0) (16.2-27.0) 15.2(13.2-17.8)

TLD (annually) 23 (19/20) ST-20 (0.5 mi S) 64.0 (3/3) None (42.0-64.0) On Perimeter (49.0-55.5) 52.0 52.6

  • Gross Beta 13 1.0 (11/11) JS (3.5 mi SE) 2.3 None None Crops 2.2(0.8-7.0 Turnip Greens (l.0-7 .o)
    • Sr-89 13 0.025 (0/8) N/A None None NOTE:
  • Results of 2 samples were unavailable at time of report preparation
    • Results of 5 samples were unavailable at time of report preparation MI0385-0059A-NL04

Page 3 of 4 TABLE RSD-E-03A Environmental Ra.diological Monitoring Program Summary Palisades Nuclear Plant, Docket 50-255 Van Buren County, Michigan, January 1, 1984 to December 31, 1984 Analysis and Lower Limit All All Nonroutine Medium or Total Number of of Indicator Lqcation with Highest Control Reported Anal:tses Performed Detection( a) Locations Annual Mean Locations Measurements(c)

Pathwa:t SamEled Unit of Measurement LLD Mean(b) Name Mean(b) Mean(b)

Range(b) Distance & Direction Range(b) Range(b)

    • Sr-90 13 0.005 (7 /8) TH 5.0 mi S .008 None None Crops

.005(.005-.008) Apples N/A Cs-137 13 0.08 (0/13) N/A None None MDL I-131 13 0.08 (0/13) N/A None None MDL Other Gamma 13 0.1 (0/13) N/A None None MDL Gross Beta 12 1.0 (8/8) Ludington S Pier 13.3 (4/4) None Sediment 8.2(5.8-10.8) N/A 10.4(7.5-13.3) 12 0.025 (1/4) South Haven Beach .033 (0/3) None

    • Sr-89 0.027(.025-.033) N/A LLD 12 0.005 (4/4) Discharge 0.022 (0/3) None
    • Sr-90 0.019(.016-.022) N/A LLD 12 0.08 (0/8) N/A (0/4) None Cs-137 all LLD LLD 12 0.1 (0/8) N/A (0/4) None Other Gamma all LLD LLD 12 0.05 (4/8) Discharge 1. 76 (3/4) None
      • I-131
0. 72( .05-3.46) (0.5-3.46) 0.29(.05-.73)

NOTE: ** Results of 5 samples were unavailable at time of report preparation.

      • I-131 results have elevated LLD's due to delay in sample counting times.

MI0385-0059A-NL04

Page 4 of 4 TABLE RSD-E-03A Environmental Radiological Monitoring Program Summary Palisades Nuclear Plant, Docket 50-255 Van Buren County, Michigan, January 1, 1984 to December 31, 1984 Analysis and Lower Limit All All Nonroutine Medium or Total Number of of Indicator Location with Highest Control Reported Pathwa~ SamEled Anal~ses Performed Detection( a) Locations Annual Mean Locations Measurements(c)

Unit of Measurement LLD Mean(b) Name Mean(b) Mean(b)

Range(b) Distance & Direction Range(b) Range(b)

Aquatic Gross Beta 13 1.0 (7 /7) Vicinity of discharge 2.6 (6/6) None (pCi/g Wet) 2.2(1.6-3.1) & Ludington S Pier (1.9-3.1) 2.3(1.4-3.4)

'~*Sr89 13 0.025 (0/4) Ludington S Pier 0.039 (1/4) None All LLD ( .025-.083) .039(.025-.083)

    • Sr90 13 0.005 (1/4) Ludington S Pier .007 (2/4) None 0.006(.005-.007) (.005-.009) .007(.005-.009)

Gamma 13 0.1 (0/13) N/A None None All LLD Cs-137 13 0.08 (0/13) N/A None None All LLD

      • I-131 12 0.05 (417) Vicinity of discharge 1.03 (3/5) None 0.39(.05-2.0) ( ,05-2.0) 0.59( .05-1.94)
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 based upon detectable measurements only. Fraction of detectable measurents at specified locations is indicated in parentheses.
c. Nonroutine reported measurements are defined in the Palisades Technical Specifi.cations, Section 6.9."3.2.

NOTE: ** Results of 5 samples were unavailable at time of report preparation.

      • I-131 results have elevated LLD's due to delay in sample counting times.

MI0385-0059A-NL04


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page 1 of 3 TABLE RSD-E-03B SAMPLING LOCATIONS PALISADES NUCLEAR PLANT Sample m

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  • 4 JS Jerry Sarno x x x x RRl, Covert, 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
    • 7 .a SN35 Emergency Siren 35 x 4-3/4 miles NNE 8 SP State Park x x x x 1 mile N
  • 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 PALISADES NUCLEAR PLANT Sample

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  • 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 Hudsonville Creamery, Burnip, Michigan (35 miles NE), and the other 6 months from the Constantine Dairy, Constantine, Michigan (48 miles SE).

TABLE RSD-E-03C PALISADES NUCLEAR PLANT JANUARY 1, 1984 TO DECEMBER 31, 1984 SAMPLING AND ANALYSIS

SUMMARY

Number of Samples Frequency Medium Description Location Collected Type of Analysis of Analysis Air Continuous at All; as identified 609* Gross Beta, I-131 Weekly/12 Approx 1 CFM on 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/1 Water-Lake Composite Well 1 Gallon Site, TP, SP 36 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 276 TLD Dose Monthly/23 Dose on Table RSD-E-03B 92 Quarterly/23 23 Annually/23 Crops Grab JS, PR, RB, HS, TH 13 Gross Beta, Isotopic, When Sr-89 and Sr-90, Cs-137, I-131 Available Sediment Grab Discharge, N & S Site 2 Gross Beta, Isotopic When Boundary, 5 miles North Sr-89 and Sr-90, Cs-137, Available Ludington (control) I-131 Aquatic Grab Intake, Discharge 13 Gross Beta, Sr-89, Sr-90, When Gamma, I-131 Available

  • 18 results deleted because of meter or sampler malfunctions.

MI0385-0059A-HP01

Page 1 of 3 TABLE RSD -E-03D HIGH, LOW AND AVERAGE CONCENTRATIONS FOR HIGHEST AVERAGE SAMPLING LOCATION PALISADES NUCLEAR PLANT JANUARY 1, 1984 to DECEMBER 31, 1984 Medjum Type of Analysis(l) Location High Low Average(5)

Air Gross Beta GR 55 mi NNE 0.087 pCi/m 3 0,007 pCi/m 3 0.03 pCi/m 3 I-131 All LLD .02 pCi/m 3 Lake Water Gross Reta Discharge 3.6 pCi/l 1.2 pCi/l 2.4 pCi/1 Gross Alpha Discharge 1 pCi/l 1 pCi/l 1 pCi/1 Tritium Discharge 1570 pCi/l 100 pCi/l 490.8 pCi/1 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) 9.3 pCi/l 2.4 pCi/l 4.8 pCi/l (1) Minimum detectable level (MDL) =air, gross beta 0.01 pCi/m 3 , I-131 0.02 pCi/m 3 ; water, gross beta 1.0 pCi/l, gross alpha 1.0 pCi/l, H-3 100 pCi/1.; milk, I-131 0.5 pCi/1, Sr-89 5.0 pCi/1, 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, shipping delays or statistical phenomenon.

(2) Samples collected monthly in season.

(3) Two samples per location.

(4) Tritium analysis performed on South Haven treated only.

(5) Only samples greater than LLD included in average.

(6) Includes transit dose which averages approximately 6.4 mR/round trip.

MI0385-0060A-HP01

Page 2 of 3 TABLE RSD -E-03D HIGH, LOW AND AVERAGE CONCENTRATIONS FOR HIGHEST AVERAGE SAMPLING LOCATION PALISADES NUCLEAR PLANT JANUARY 1, 1984 to DECEMBER 31, 1~84 Medium Type of Analysis(l) Location High Low Average(5)

Milk I-131 All LLD Sr-89 All LLD Sr-90 GM (5 mi SE) 2.8 pCi/l 2.1 pCi/l 4.2 pCi/l Cs-137 All LLD Other Ganuna All LLD Gamma Dose (6) TLD (Monthly) ST-18 .75 mi SE 11.1 mR 3.9 mR 5.9 mR (on perimeter)

TLD (Quarterly) ST-04 3.5 mi ESE 27.0 mR 16.2 mR 19.5 mR TLD (Annual) ST-20 0.5 mi S (on perimeter)

Crops (2)

  • Gross Beta JS(3.5 mi SE) 7.0 pCi/g 1.0 pCi/g 2.3 pCi/g
    • Sr-90 TH(5.0 mi S) 0.008 pCi/g 0.005 pCi/g 0.005 pCi/g Cs-137 All LLD Other Gamma All LLD I-131 All LLD NOTE: *Results of 2 samples were unavailable at time of report preparation.
    • Results of 5 samples were unavailable at time of report preparation.

MI0385-0060A-HP01

Page 3 of 3 TABLE RSD -E-03D HIGH LOW AND AVERAGE CONCENTRATIONS FOR HIGHEST AVERAGE SAMPLING LOCATION PALISADES NUCLEAR PLANT JANUARY 1, 1984 to DECEMBER 31, 1984 Medium Type of Analysis(l) Location High Low Average{5)

Sediment(3) Gross Beta Ludington s Pier 13.3 pCi/g 7.5 pCi/g 10.4 pCi/g

    • Sr-89 South Haven Beach 0.033
      • I-131 Discharge 3.46 0.05 1. 76 Aquatic Gross Beta Discharge and Ludington S Pier 3.1 pCi/g 1.9 pCi/g 2.6 pCi/g
    • Sr-89 Ludington s Pier 0.083 pCi/g 0.025 pCi/g 0.039 pCi/g
    • Sr-90 Ludington s Pier 0.009 pCi/ 0.005 pCi/g 0.007 pCi/g Gamma All LLD
      • I-131 Discharge 2.0 0.05 1.03 NOTE: ** Results of 5 samples were unavailable at time of report preparation.
      • I-131 results have elevated LLD's due to delay in sample counting times.

MI0385-0060A-HP01

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I I I I I I I I I I I I J A. N FEB M.A. R APR M.~ 'I' JUN JUL AUG SEP OCT 1--IOV DEC D.l!iT E LEGEND: LOC.l'..TIO~J oti + + HESSE'!" ~ o;l 9 KEMP 8 DD MILLER A A A SHERMAN-CONTROL

1984 P"'4LJSJ_4DES 1l!ILK S"'41\.fPLES Sl-IERi.\l..4N-CO~VTROL VS HESSEY .MILLER KEllfP l'S-137 PCI_,/L PCI 4C* -

35 -

3 *J -

2-5 -

20 -

1 5 -

1 C* -

5 I II I II

  • I I c, -

I

' I I I I I I I I I I J A t**l FEB MAR APR M A 'T' ~'UN JUL /.l.UG SEP OCT N 0 V' DEC Dti. TE L EGEHD : L 0 C .A. T I 0 t*J + + + HESSE"l' (,i (:i t;i KEMP 8 0 8 MILLER A 6 6 SHERMAN-CONTROL

n-:t ,,..._IR 1984 P.4LI1-'5~4DE s TLLO )-.Ji/ LV1 ~ *-

PlO CONTROL l'S P02 P03 MILLIRElV MR 20 15 10 0

J .e. N FEB MAR APR MAY JUN JUL AUG SEP OCT HOV DEC D ,!I.TE LEGEHD: LOCATIOl*J *+ + + P0 2 5 SS E ~ e ~ PD.3 5 SE 8 8 8 P10C 55 NNE

0.3/22/e:::-

1984 PALISJ_4DE S TLD . .

  • Pl 1 CONTROL llS P08 P09 J.!JLLJRE}J MR 20 15 1 0 0

JAN FEB MAR APR M.A. '1' JUN JUL .A. U G SEP OCT NOV DEC D ti.TE LEGEND: LOGATIOI*~ *+ + *+ P0 B 1 N ~ i i P09 1 . S S DD D P11C 35 E

n.7> /'?? /.o.~

1984 PALISJ.4DE S TLD '"-~--.J~-1 ........

P12 CONTROL VS POB P06 P07A MlLLJRE}.f MR 20 15 10 5

0 JAN F" EB MAR .a.PR MA. Y JUN JUL AUG S IE P OCT NOV DEC D .!I.TE LEGEND: LIJCATIOI-~ + + + P05 3 E 4-&-+ PQB 4,75 NE 8 8 8 P07A 4.75NNE -1.t--!:r--tr P 1 2 C 3 0 S S E

P.£.L :S~8ES ~~G?

Table 13. Milk Collection: Monthly Un i ts : pCi / l Collection Lab Date Code 1-131 Sr-89 Sr-90 Cs-134 Cs-137 Ba-La-140 Required LLD 0.5 5.0 1.0 5.0 5.0 5.0 GH 1-09-84 PAMI- 51,2 <0.5 <5.0 2.8+/-0.4 <5.0 <5.0 <5.0 2-04-84 124,5 <0.5 <5.0 2.6+/-0.4 <5.0 <S.O <S.O 3-06-84 202 '(0. 5 <5.0 2.9+/-0.6 <S.O <5.0 <5.0 4-07-84 286 <0.5 <5.0 3.1+/-0.6 <5.0 <5.0 <5.0 5-02-84 371 <0.5 <5.0 3.2+/-0.7 <5.0 <5.0 <5.0 6-06-84 630 <0.5 <5.0 3.1+/-0.6 <S.O <S.O <5.0 7-03-84 868 <0.5 <5.0 2.7+/-0.6 <5.0 <5.0 Noa 8-09-84 1137 <O.S <5.0 3.4+/-0.5 <S.O <5.0 <5.0 9-04-84 1351 <0.5 <S.O 3.0+/-0.6 <S.O <5.0 <S.O 10-01-84 1593 <O.S <5.0 3.0+/-0.5 <S.O <S.O <5.0 11-07-84 1777 <0.5 <5.0 2.0+/-0.6 <S.O <S.O <5.0 12-05-84 18.37 ,8 <0.5 <5.0 <l.O <S.O <5.0 <5.0 KK 1-06-84 PAM!- 53 <0.5 <5.0 3.3+/-0.6 <5.0 <S.O <S.O 2-05-84 123 <0.5 <S.O 4.5+/-0.8 <S.O <S.O <5.0 3-06-84 203,4 <0.5 <5.0 2.2+/-0.4 <S.O <S.O <S.O 4-06-84 287 <0.5 <S.O 2. 0+/-1. 0 <5.0 <5.0 <5.0 5-01-84 372 <0.5 <5.0 3.6+/-0.6 <5.0 <5.0 <5.0 6-05-84 631 <0.5 <5.0 4.2+/-0.6 <S.O <S.O <S.O 7-03-84 869 <O.S <5.0 2.5+/-0.5 <5.0 <5.0 . ND 8-07-84 1138 <O.S <5.0 2.3+/-0.5 <5.0 <S.O <5.0 9-04-84 1352 <0.5 <5.0 2.2+/-0.6 <5.0 <S.O <5.0 10-01-84 1594 <O.S <5.0 2.3+/-0.5 <5.0 <5.0 <5.0 11-02-84 1775 <0.5 <5.0 1. 9+/-0. 6 <5.0 <5.0 <5.0 12-02-84 1835 <0.5 <5.0 1. 8+/-0. 4 <5.0 <5.0 <5.0 19

Table 13. Milk (continued)

Collection Lab Date Code I-131 Sr-89 Sr-90 Cs-134 Cs-137 Ba-La-140 Required LLD 0.5 5.0 1. 0 5.0 5.0 5.0 SD Sherman Oairx 1-10-84 PAMI-54 <0.5 <5.0 1. 3+/-0. 6 <5.0 <5.0 <5.0 2-05-84 122 <0.5 <5.0 <1.1 <5.0 <5.0 <5.0 3-06-84 205 <0.5 <5.0 <1.1 <5.0 <5.0 <5.0 4-06-84 288 <0.5 <5.0 <l.O <5.0 <5.0 <5.0 5-01-84 373 <0.5 <5.0 1. 5+/-0. 5 <5.0 <5.0 <5.0 6-05-84 632 <0.5 <5.0 1. 6+/-0. 5 <S.O <5.0 <5.0 7-03-84 870 <0.5 <S.O 2.6+/-0.8 <5.0 <5.0 Noa 8-07-84 1139 <0.5 <S.O 2.4+/-0.6 <5.0 <5.0 <5.0 9-04-84 1353 <0.5 <5.0 1. 4+/-0. 5 <5.0 <5.0 <5.0 10-01-84 1595 <0.5 <5.0 <l.O <5.0 <5.0 <5.0 11-02-84 1776 <0.5 <5.0 1. 8+/-0. 6 <5.0 <5.0 <5.0 12-02-84 1836 <0.5 <5.0 <l.O <5.0 <5.0 <5.0 GM Glen Miller 1-09-84 PAMI-55 <0.5 <5.0 2.9+/-0.6 <5.0 <5.0 <5.0 2-05-84 126 <0.5 <5.0 2.5+/-0.6 <5.0 <5.0 <5.0 3-06-84 206 <0.5 <5.0 2.2+/-0.6 <5.0 <5.0 <5.0 4-06-84 289 <0.5 <5.0 4.2+/-0.7 <5.0 <5.0 "<5.0 5-02-84 374 <0.5 <5.0 2.2+/-0.6 <5.0 <5.0 <5.0 6-06-84 633 <0.5 <5.0 3.5+/-0.7 <5.0 <5.0 <5.0 7-03-84 871 <0.5 <5.0 3.1+/-0.8 <5.0 <5.0 Noa 8-09-84 1140 <0.5 <5.0 3.6+/-0.6 <5.0 <5.0 <5.0 9-04-84 1354 <0.5 <5.0 3.4+/-0.6 <5.0 <5.0 <5.0 10-01-84 1596,7 <0.5 <5.0 2.1+/-0.4 <5.0 <5.0 <S.O 11-07-84 1774 <0.5 <5.0 2.1+/-0.4 <5.0 <5.0 <5.0

  • 12-05-84 1834 <0.5 <5.0 2.3+/-0.4 <5.0 <5.0 <5.0 a ND = No Data. LLD for Ba-La-140 could not be reached due to delay in counting. Milk will be analyzed for Ba-La-140 by chemical separation.

20

\.

I consumers Power company General Offices: 1945 West Parnall Road, Jackson, Ml 49201 *.(517) 1as-osso April 16, 1985 James G Keppler, Administrator Region III US Nuclear Regulatory Commission 799 Roosevelt Road Glen Ellyn, IL 60137 DOCKET 50-255 - LICENSE DPR PALISADES PLANT - 1984 RADIOLOGICAL ENVIRONMENTAL MONITORING REPORT Attached is the 1984 Radiological Environmental Monitoring Report for the Palisades Plant. This covers the period January 1 through December 31, 1984 and is submitted in accordance with Technical Specification 6.9.3.1.B. A supplemental report will be submitted when the unavailable analytical results are available from the laboratory contractor. This report also includes the results of the land use census required by Technical Specification 4.11.3.

'2te~rt<Ll Ralph R Frisch Senior Licensing Analyst CC D~rector, Office of Nuclear Reactor Regulation Director, Office of Inspection and Enforcement NRC Resident Inspector - Palisades Attachment Jl.PR 1 9 1985 OC0485-0001B-NL02