ML18051B349

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Radiological Environ Monitoring Rept,1984
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 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 3

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

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 4

Medium or Pathway Sampled Unit of Measurement Air (pCi/m3 )

Lake Water (pCi/l)

Drinking Water (pCi/l)

Well Water (pCi/l)

MI0385-0059A-NL04 Analysis and Total Number of Analyses Performed Gross Beta 627 1-131 627 Gross Alpha 24 Gross Beta 24 Tritium 24 Gross Beta 12 Tritium 12 Gross Beta 36 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 Lower Limit of Detection(a)

LLD 0.01 0.02 1.0 1.0 100.0 LO All Indicator Locations Mean(b)

Range(b)

(457/468) 0.02(.02-.03) all LLD (0/12) 1 ( 1)

(12/12) 2.4(1.2-3.6)

(12/12) 490.8(100-1570)

Location with Highest Annual Mean Name Mean(b)

Distance & Direction Range(b)

GR 55 mi NNE

.03

(.007-.087)

N/A Discharge 1 ( 1)

Discharge 2.4(1.2-3.6)

Discharge 490.8 (100-1570)

Page 1 of 4 All Control Locations Mean(b).

Range(b)

(152/159) 0.02(.02-.03)

LLD (0/12) 1 (12/12) 2.3(1.1-3.0)

(12/12) 189.2(100-400)

Control, lake and well water samples are drinking water supplies.

100.0 1.0 (12/12) 1.4(1-1.8)

State Park (1 mi N) 4.8 (2.4-9.3)

(24/24) 3.2(0.7-9.3)

Nonroutine Reported Measurements(c)

None None None None None None

Medium or Pathwa:z: SamEled Unit of Measurement Milk (pCi/l)

Gamma Exposure (mR/month)

(mR/quarter)

Crops NOTE:

  • Results of 2
    • Results of 5 MI0385-0059A-NL04 Analysis and Total Number of Anal:z:ses Performed I-131 48 Sr-89 48 Sr-90 48 Cs-137 48 Other Gamma TLD (monthly) 276 TLD (quarterly) 92 TLD (annually) 23
  • Gross Beta 13
    • Sr-89 13 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 Lower Limit All of Indicator Location with Highest Detection( a)

Locations Annual Mean LLD Mean(b)

Name Mean(b)

Range(b)

Distance & Direction Range(b)

.5 (0/36)

All LLD N/A 5.0 (0/36)

All LLD N/A 1.0 (36/36)

GM (5 mi SE) 2.8 2.8(1-4.5)

(2.1-4.2) 1.0 (0/36)

All LLD N/A 1.0 (0/36)

N/A N/A 1.0 (234/240)

ST-18 (.75 mi SE) 5.9 5.3(3.3-11.1)

On Perimeter (3.9-11.1)

(78/80)

ST-04 3.5 mi ESE 19.5 15.4(12.2-27.0)

(16.2-27.0)

(19/20)

ST-20 (0.5 mi S) 64.0 (42.0-64.0)

On Perimeter 52.0 1.0 (11/11)

JS (3.5 mi SE) 2.3 2.2(0.8-7.0 Turnip Greens (l.0-7.o) 0.025 (0/8)

N/A samples were unavailable at time of report preparation samples were unavailable at time of report preparation Page 2 of 4 All Control Locations Mean(b)

Range(b) 0/12 LLD 0/12 LLD (12/12) 1.5(1-2.6) 0/12 LLD 0/12 LLD (36/36) 5.3(3.9-7.2)

(12/12) 15.2(13.2-17.8)

(3/3)

(49.0-55.5) 52.6 None None Nonroutine Reported Measurements(c)

None None None None None None None None None None

Medium or Pathwa:t SamEled Unit of Measurement Crops Sediment NOTE: ** Results of 5 Analysis and Total Number of Anal:tses Performed

    • Sr-90 13 Cs-137 13 I-131 13 Other Gamma 13 Gross Beta 12
    • Sr-89 12
    • Sr-90 12 Cs-137 12 Other Gamma 12
      • I-131 12 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 Lower Limit All of Indicator Lqcation with Highest Detection( a)

Locations Annual Mean LLD Mean(b)

Name Mean(b)

Range(b)

Distance & Direction Range(b) 0.005 (7 /8)

TH 5.0 mi S

.008

.005(.005-.008) Apples N/A 0.08 (0/13)

N/A MDL 0.08 (0/13)

N/A MDL 0.1 (0/13)

N/A MDL 1.0 (8/8)

Ludington S Pier 13.3 8.2(5.8-10.8)

N/A 0.025 (1/4)

South Haven Beach

.033 0.027(.025-.033)

N/A 0.005 (4/4)

Discharge 0.022 0.019(.016-.022)

N/A 0.08 (0/8)

N/A all LLD 0.1 (0/8)

N/A all LLD 0.05 (4/8)

Discharge

1. 76
0. 72(.05-3.46)

(0.5-3.46) 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 3 of 4 All Control Locations Mean(b)

Range(b)

None None None None (4/4) 10.4(7.5-13.3)

(0/3)

LLD (0/3)

LLD (0/4)

LLD (0/4)

LLD (3/4) 0.29(.05-.73)

Nonroutine Reported Measurements(c)

None None None None None None None None None None

Analysis and Medium or Total Number of Pathwa~ SamEled Anal~ses Performed Unit of Measurement Aquatic Gross Beta 13 (pCi/g Wet)

'~*Sr89 13

      • I-131 12 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 Lower Limit All of Indicator Location with Highest Detection( a)

Locations Annual Mean LLD Mean(b)

Name Mean(b)

Range(b)

Distance & Direction Range(b) 1.0 (7 /7)

Vicinity of discharge 2.6 2.2(1.6-3.1)

& Ludington S Pier (1.9-3.1) 0.025 (0/4)

Ludington S Pier 0.039 All LLD

(.025-.083) 0.005 (1/4)

Ludington S Pier

.007 0.006(.005-.007)

(.005-.009) 0.1 (0/13)

N/A All LLD 0.08 (0/13)

N/A All LLD 0.05 (417)

Vicinity of discharge 1.03 0.39(.05-2.0)

(,05-2.0)

a. Nominal Lower Limit of Detection (LLD) as defined in HASL-300 (Rev 8/73), pages D-08-01, 02, and 03.

Page 4 of 4 All Control Locations Mean(b)

Range(b)

(6/6) 2.3(1.4-3.4)

(1/4)

.039(.025-.083)

(2/4)

.007(.005-.009)

None None (3/5) 0.59(.05-1.94)

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 Nonroutine Reported Measurements(c)

None None None None None None


~~----

TABLE RSD-E-03B SAMPLING LOCATIONS PALISADES NUCLEAR PLANT m

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TH Tower Hill Farms x

x RR3, Coloma, Michigan 5 miles S 3

HS Herbert Soderberg x

x RRl, Covert, Michigan 5 miles. S

  • 4 JS Jerry Sarno x

x RRl, Covert, Michigan 3~ miles SE 5

PR Paul Rude x

x RRl, Covert, Michigan 3.\\ miles ESE 6

RB Richard Bus x x RR3, South Haven, MI 4-1/4 miles NE 7

SD Sherman Dairy x x South Haven, Michigan 6 miles NNE

    • 7.a SN35 Emergency Siren 35 4-3/4 miles NNE 8

SP State Park 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.

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Covert To'Wllship Park x

x l~ miles SSW Grand Rapids, Michigan x

x 55 miles NNE Kalamazoo, Michigan x

x 35 miles SSE Dowagiac, Michi~an x

x 30 miles SSE Perimeter of Palisades Emergency Siren 25 3 miles ENE Emergency Siren 21 3-1/3 miles E South Haven, Michigan 5-1/2 miles NNE Glenn Miller Rt 1, Box 20 Covert, MI 4.3 miles SE Kenneth Kemp Rt 4, Box 32 South Haven, MI 8 miles NE 24 were added to the program in T--

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  • SD Control Sample 30 STN

~ mile N of discharge 31 STS

~mile S of discharge LP.

Ludington Pump Storage 116 miles N

  • 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).

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Medium Description Air Continuous at Approx 1 CFM Lake 1 Gallon Water Composite Drinking 1 Gallon Water-Lake Composite Well 1 Gallon Water Grab Milk 1 Gallon Grab Gamma Continuous Dose Crops Grab Sediment Grab Aquatic Grab TABLE RSD-E-03C PALISADES NUCLEAR PLANT JANUARY 1, 1984 TO DECEMBER 31, 1984 SAMPLING AND ANALYSIS

SUMMARY

Number of Samples Location Collected All; as identified 609*

on Table RSD-E-03B Intake, Discharge 24 South Haven 12 Site, TP, SP 36 SDF, GM, KK, GH 48 All; as identified on Table RSD-E-03B JS, PR, RB, HS, TH 276 92 23 13 Discharge, N & S Site 2

Boundary, 5 miles North Ludington (control)

Intake, Discharge 13 Type of Analysis Gross Beta, I-131 Gross Beta, Gross Alpha, Tritium Gross Beta, Tritium Gross Beta I-131, Sr-89 and Sr-90, Cs-137 Isotopic TLD Dose Gross Beta, Isotopic, Sr-89 and Sr-90, Cs-137, I-131 Gross Beta, Isotopic Sr-89 and Sr-90, Cs-137, I-131 Gross Beta, Sr-89, Sr-90, Gamma, I-131

  • 18 results deleted because of meter or sampler malfunctions.

MI0385-0059A-HP01 Frequency of Analysis Weekly/12 Monthly/2 Monthly/1 Monthly/3 Monthly/4 Monthly/23 Quarterly/23 Annually/23 When Available When Available When Available

Medjum Air Lake Water Drinking Water Well Water TABLE RSD -E-03D HIGH, LOW AND AVERAGE CONCENTRATIONS FOR HIGHEST AVERAGE SAMPLING LOCATION PALISADES NUCLEAR PLANT JANUARY 1, 1984 to DECEMBER 31, 1984 Type of Analysis(l)

Location High Low Gross Beta GR 55 mi NNE 0.087 pCi/m3 0,007 pCi/m3 I-131 All LLD Gross Reta Discharge 3.6 pCi/l 1.2 pCi/l Gross Alpha Discharge 1 pCi/l 1 pCi/l Tritium Discharge 1570 pCi/l 100 pCi/l Gross Beta See Table RSD-E-03A Tritium (4)

See Table RSD-E-03A Gross Beta State Park (1 mi N) 9.3 pCi/l 2.4 pCi/l Page 1 of 3 Average(5) 0.03 pCi/m3

.02 pCi/m3 2.4 pCi/1 1 pCi/1 490.8 pCi/1 4.8 pCi/l (1) Minimum detectable level (MDL) =air, gross beta 0.01 pCi/m3, I-131 0.02 pCi/m3 ; 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

Medium Milk Gamma Dose (6)

Crops (2)

TABLE RSD -E-03D HIGH, LOW AND AVERAGE CONCENTRATIONS FOR HIGHEST AVERAGE SAMPLING LOCATION PALISADES NUCLEAR PLANT Type of Analysis(l)

I-131 Sr-89 Sr-90 Cs-137 Other Ganuna TLD (Monthly)

TLD (Quarterly)

TLD (Annual)

  • Gross Beta
    • Sr-89 JANUARY 1, 1984 to DECEMBER 31, 1~84 Location All LLD All LLD GM (5 mi SE)

All LLD All LLD ST-18.75 mi SE (on perimeter)

ST-04 3.5 mi ESE ST-20 0.5 mi S (on perimeter)

JS(3.5 mi SE)

All LLD High 2.8 pCi/l 11.1 mR 27.0 mR 7.0 pCi/g Low 2.1 pCi/l 3.9 mR 16.2 mR 1.0 pCi/g Page 2 of 3 Average(5) 4.2 pCi/l 5.9 mR 19.5 mR 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

Medium Sediment(3)

Aquatic NOTE:

    • Results of 5 TABLE RSD -E-03D HIGH LOW AND AVERAGE CONCENTRATIONS FOR HIGHEST AVERAGE SAMPLING LOCATION PALISADES NUCLEAR PLANT JANUARY 1, 1984 to DECEMBER 31, 1984 Type of Analysis(l)

Location High Low Gross Beta Ludington s Pier 13.3 pCi/g 7.5 pCi/g

    • Sr-89 South Haven Beach
      • I-131 Discharge 3.46 0.05 Gross Beta Discharge and Ludington S Pier 3.1 pCi/g 1.9 pCi/g
    • Sr-89 Ludington s Pier 0.083 pCi/g 0.025 pCi/g
    • Sr-90 Ludington s Pier 0.009 pCi/

0.005 pCi/g Gamma All LLD

      • I-131 Discharge 2.0 0.05 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 Page 3 of 3 Average{5) 10.4 pCi/g 0.033 0.022

1. 76 2.6 pCi/g 0.039 pCi/g 0.007 pCi/g 1.03

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PCI 1 0 B

4 2

0 1984 P.L4LIS~4DE~~ LAR-E T1~4TER /5~41~!PLE/5 JAN FEB SOUTH.l!AVEl'1 TREATED & RAW-CO.l\\TTROL VS INTAKE BETA PCI/L

.b. p R M A 'r" JUN JUL A. U G SEP OCT D.l!iTE LEGE1--4L*:

LiJLJJ.liOi~-1

+ + + il-iT.5.rO:.:E e e e S.H.TREATED c NOV Q.3/22/8._

DEC

PCI 20 1 5 1 Q 5

J.e.. N 1984 PJ.4LIS_j_4DE,5 rf.TELL Ff~4 TER,5-L41\\f PLE S FEB TO'Wl"!SHIP PAR}; & STATE PARl(-CONTROL VS SITE CROSS BETA PCJ/L J

e M.A. R APR JUN JUL

.A. U G

. S: E p Oil.TE OCT f-.IOV LEGEt-*lD:

LOCATIOH ti o;J (J

PAL SITE

+ + + ST PARK-CONT 8

8 8

TWP PARK-CONT n.~ /n'? /R

  • _.* -... -_, L.a.-/..... _

DEC

'*I>"

'...... :..... ~

1984 P.1.4LJ/SL4DE S 1\\!JLI( *s.1.41\\f PLE S PCI 25 -

20 -

1 5 1 0 0

I J A. N I

I FEB M.A. R LEGEND:

LOC.l'..TIO~J Sl!ERi.'JA..1.V-CONTROL* VS HESSEi'.MILLER KEtlJP

.SR-90 PCI/L I

APR I

M.~ 'I' I

JUN D.l!iT E I

I I

JUL AUG SEP I

OCT

~

o;l 9

KEMP I

1--IOV oti

+ + HESSE'!"

8 DD MILLER A

A A

SHERMAN-CONTROL (J.3/22/8:::

I DEC

1984 P"'4LJSJ_4DES 1l!ILK S"'41\\.fPLES PCI 4C* --

35 --

3 *J -

2 20 -

1 5 1 C*

5 I

c, -

I J A t**l II FEB I

MAR L E G E H D :

L 0 C.A. T I 0 t*J Sl-IERi.\\l..4N-CO~VTROL VS HESSEY.MILLER KEllfP l'S-137 PCI_,/L I

APR I

M A 'T' I

I

~'UN Dti. TE II I

JUL I

/.l.UG I

SEP I

I OCT

(,i

(:i t;i KEMP I

I N 0 V'

+ + + HESSE"l' 8

0 8

MILLER A 6 6

SHERMAN-CONTROL I

DEC

MR 20 1 5 1 0 0

J.e. N 1984 P.4LI1-'5~4DE s TLLO FEB MAR APR LEGEHD:

LOCATIOl*J PlO CONTROL l'S P02 P03 MILLIRElV MAY JUN JUL AUG D,!I.TE

  • + + + P 0 2 5

SS E 8

8 8

P10C 55 NNE SEP OCT HOV

~ e

~

PD.3 5

SE n-:t,,..._IR

)-.Ji/ LV1 ~ *-

DEC

MR 20 1 5 1 0 0

JAN FEB LEGEND:

LOGATIOI*~

MAR 1984 PALISJ_4DE S TLD APR

  • Pl 1 CONTROL llS P08 P09 J.!JLLJRE}J M.A. '1' JUN JUL

.A. U G D ti.TE SEP

  • + + *+

P 0 B 1

N

~

i i

P09 1. S S

0.3/22/e:::-

OCT NOV DEC DD D P11C 35 E

MR 20 1 5 1 0 5

0 JAN 1984 PALISJ.4DE S TLD F" EB MAR

.a.PR LEGEND:

LIJCATIOI-~

P12 CONTROL VS POB P06 P07A MlLLJRE}.f MA. Y JUN JUL D.!I.TE

+ + + P05 3 E

8 8

8 P07A 4.75NNE AUG S IE P OCT NOV 4-&-+ PQB 4,75 NE

-1.t--!:r--tr P 1 2 C 3 0 S S E n.7> /'?? /.o.~

'"-~--.J~-1........

DEC

Table 13.

Milk Collection Date Collection:

Monthly Un i ts :

p Ci / l Lab Code 1-131 Required LLD 0.5 1-09-84 PAMI-51,2

<0.5 2-04-84 124,5

<0.5 3-06-84 202

'(0. 5 4-07-84 286

<0.5 5-02-84 371

<0.5 6-06-84 630

<0.5 7-03-84 868

<0.5 8-09-84 1137

<O.S 9-04-84 1351

<0.5 10-01-84 1593

<O.S 11-07-84 1777

<0.5 12-05-84 18.37,8

<0.5 1-06-84 PAM!- 53

<0.5 2-05-84 123

<0.5 3-06-84 203,4

<0.5 4-06-84 287

<0.5 5-01-84 372

<0.5 6-05-84 631

<0.5 7-03-84 869

<O.S 8-07-84 1138

<O.S 9-04-84 1352

<0.5 10-01-84 1594

<O.S 11-02-84 1775

<0.5 12-02-84 1835

<0.5 P.£.L :S~8ES ~~G?

Sr-89 Sr-90 Cs-134 Cs-137 Ba-La-140 5.0 1.0 5.0 5.0 5.0 GH

<5.0 2.8+/-0.4

<5.0

<5.0

<5.0

<5.0 2.6+/-0.4

<5.0

<S.O

<S.O

<5.0 2.9+/-0.6

<S.O

<5.0

<5.0

<5.0 3.1+/-0.6

<5.0

<5.0

<5.0

<5.0 3.2+/-0.7

<5.0

<5.0

<5.0

<5.0 3.1+/-0.6

<S.O

<S.O

<5.0

<5.0 2.7+/-0.6

<5.0

<5.0 Noa

<5.0 3.4+/-0.5

<S.O

<5.0

<5.0

<S.O 3.0+/-0.6

<S.O

<5.0

<S.O

<5.0 3.0+/-0.5

<S.O

<S.O

<5.0

<5.0 2.0+/-0.6

<S.O

<S.O

<5.0

<5.0

<l.O

<S.O

<5.0

<5.0 KK

<5.0 3.3+/-0.6

<5.0

<S.O

<S.O

<S.O 4.5+/-0.8

<S.O

<S.O

<5.0

<5.0 2.2+/-0.4

<S.O

<S.O

<S.O

<S.O

2. 0+/-1. 0

<5.0

<5.0

<5.0

<5.0 3.6+/-0.6

<5.0

<5.0

<5.0

<5.0 4.2+/-0.6

<S.O

<S.O

<S.O

<5.0 2.5+/-0.5

<5.0

<5.0

. ND

<5.0 2.3+/-0.5

<5.0

<S.O

<5.0

<5.0 2.2+/-0.6

<5.0

<S.O

<5.0

<5.0 2.3+/-0.5

<5.0

<5.0

<5.0

<5.0

1. 9+/-0. 6

<5.0

<5.0

<5.0

<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 OC0485-0001B-NL02 Jl.PR 1 9 1985