ML20246C690

Annual Radiological Environ Operating Rept, 1988

ML20246C690
Person / Time
Site:	Big Rock Point File:Consumers Energy icon.png
Issue date:	12/31/1988
From:	CONSUMERS ENERGY CO. (FORMERLY CONSUMERS POWER CO.)
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ML20246C688	List: ML20246C685 ML20246C690 ML20246C720
References
NUDOCS 8905100014
Download: ML20246C690 (30)

Text

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4 ATTACHMENT Consumers Power Company Big Rock Point Plant Docket 50-155 BIG ROCK POINT NUCLEAR PLANT ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT

, JANUARY THROUGH DECEMBER 1988 May 1, 1989 l

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.fik 20 Pages OC0589-0009-NLO2

1988 Big Rock Point Annual Radiological Environmental Operating Report I. Introduction The 1988 Big Rock Point Annual Radiological Environmental Operating Report provides a summary and data interpretation of the Big Rock Point Radiological Environmental Monitoring Program as conducted during the 1988 reporting period. Re .rting requirements are detailed in Technical Specifications 6.9.2.1, 13.2 and Tabler, 13.3-1 through 13.3-3. Big Rock Point was off-line for the second quarter of 1988 due to a refueling / maintenance outage.

i There are no remaining 1988 laboratory sample analyses pending completion for inclusior. into this report. The results of all environmental samples collected are evaluated as follows:

A. Air iodine and particulate, TLD's (monthly and quarterly), and milk data were statistically evaluated at the 95% confidence level (using SAS program) by the methodology detailed in Palisades' Procedure HP 10.2. The data was compared against two criterium: the first criteria is the statistical dif ference which indicates that sample results from near sites are greater than those from control sites, but that the difference is ny significant. The second criteria is the evaluation level (twice the statistical difference) which is the minimum detectable difference that exceeds zero at the 95%

confidence level. If the evaluation level is exceeded, then correlation of the results with effluent releases is done.

B. Well water, lake water intake / discharge, sediment, fish and other aquatic biota samples were evaluated using data means comparisons against an appropriate control location (if available) and BRP Technical Specification limits.

II. Discussion and Interpretation of Results A. Air Samples Comparison of the airborne particulate sample data between near-site and control locations did not exceed the statistical difference. In many instances, control location sample values were greater. There was no Iodine-131 activity reported above minimum detectable levels.

A total of 364 air samples were collected and analyzed during 1988, however 14 sample results were deleted from statistical evaluation as follows:

Eight (8) sample results for Iodine-131 did not meet LLD require-ments due to low air volume sample flow. These low flow conditions were caused by either faulty air pumps, air filters getting wet (precipitation) or loss of power to the air sampling units. The IC0489-0086A-HP01 1

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affected air monitoring stations and dates were: 1-ST on 5/12/88; 3-CH on 7/7/88; 6-BC on 1/7/88, 4/21/88 and 6/9/88; and 5-PT on 8/25/88, 9/1/88 and 11/10/88.

Six (6) sample results for air particulate gross beta also did not meet LLD requirements due to low air volume sample flow. These low flow conditions were caused by either faulty air pumps, air filters getting wet (precipitation), improper placement of an air filter in the sample holder or loss of power to the air sampling units. The affected air monitoring stations and dates were 4-SL on 10/20/88; 6-BC on 1/7/88 and 3/31/88; and 5-PT on 4/21/88, 8/25/88 and 11/10/88.

The deleted samples constitute 2.2% of the Iodine-131 and 1.6% of the air particulate / gross beta total analyses not used in the statistical evaluations. This is an overall decrease of 1.7% in the sample deletion rate from 1987. Technical Specification sensitivi-ties were met on all samples other than those already noted.

At various time periods during the first half of 1988 (principally in May at locations 1-ST, 4-SL and 7-TR), there were recurring problems with in-service air meter breakage at several air sampling '

locations. This created a shortage of suitable replacement meters and allowed other air meters to remain in-service beyond their calibration expiration dates. Since June, additional (newer model) air meters have been obtained to correct this situation. The temporarily extended in-service use of the expired calibration air meters did not affect any sample LLDs.

The air iodine / particulate samples are collected on a weekly basis from 7 air sampling locations. Air is metered through the sampling unit at a continuous 1 cfm fflow rate through a Celman 47mm air filter (air particulate) and a Scott air iodine cartridge. Both filters are in-line with each other and housed within the same filter holder.

The 1988 air sample results are consistent with actual ef fluent releases and site-specific meteorology.

B. TLD's - Camma Dose There were a total of 214 monthly, 70 quarterly and 16 annual TLD's collected and analyzed during 1988. Two (2) monthly, two (2) quarterly and two (2) annual TLD's from stations BRP-05 and BRP-15 were reported missing.

The following is detailed for the missing TLD's:

1. The December monthly, 4th quarter and annual TLD's at locations BRP-05 and BRP-15 were suspected of being dislodged from their respective mountings due to high winds and snow squalls.

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Search of the ground area around the TLD locations revealed negative results.

2. Due to the time of year and extent of the missing BRP-05 and BRP-15 TLD's, replacement or spare TLD's could not be posted nor could legitimate pro rated quarterly or annual results be calculated for inclusion into this report.

The Big Rock Point gamma assessment program consists of 18 TLD locations: 5 directly onsite, 6 inner ring (site boundary), 3 outer ring (1.0 to 4.5 miles out), 3 control (10.5 to 50 miles out) and 1 1 TLD control placed in a lead storage cave. For 1988, the average monthly gamma readings were: 3.7 mR for the inner ring (site boundary) TLD's; 4.0 mR for the outer ring (1 to 4.5 miles out)

TLD's; and 4.2 mR for the control TLD locations. The lead cave control TLD recorded an average of 2.9 mR/ month. This is consistent with historical data and actual effluent releases. The 5 onsite TLD locations serve as individual reference sources only and are not collectively evaluated.

The monthly and quarterly SAS statistical TLD data evaluations were accomplished by comparing the inner ring TLD's (site boundary locations BRP 09-13 and 16) and the outer ring TLD's (1.0 to 4.5 miles out, locations BRP 02-04) against the control TLD locations (BRP 05-07). The annual TLD dn:a evaluation was done by a direct comparison of data points only.

In comparing the inner ring TLD's to the control TLD's; station BRP-06 (Boyne City,12.0 mi SE) had the greatest monthly means for an indicator location. Station BRP-12 (Southeast site boundary, 0.9  ;

mi) had the greatest quarterly and annual means. When the same l comparison was made between the outer ring and control station TLD's; again BRP-06 (Boyne City,12.0 mi SE) had the greatest monthly means with station BRP-04 (Susan Lake, 3.5 mi SE) having greatest quarterly and annual means.

Background and intransit gamma exposure levels were accounted for and subtracted from the TLD data prior to statistical evaluation.

No statistical or evaluating levels were exceeded, and in many instances, control location TLD data was greater than near-site TLD data. BRP Technical Specification sensitivities were met.

Environmental gamma doses are measured monthly, quarterly and l annually by placement of 3 appropriately identified TLD badges per {

designated location. Each Teledyne TLD badge contains a 4-zone  !

CaSO4 phosphor wafer (the wafer also includes an. additional backup / reserve read-out zone). Sensitivity for the multi-zone TLD's ]

are 0.5 millirem with a linear response of 0.1 millirem to 1000 Rem. '

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1 C. Milk l

A total of 48 individual monthly milk samples were collected from 4 '

different dairy farms during 1988. Dairy farms 20-JC, 21-DK and 22-RM serve as indicator locations; and dairy f arm 23-BB serves as a control location. The milk samples are obtained as grab samples only (dipped from the milk tanks).

Only the Sr-90 data was statistically evaluated; all other activity results were below LLD. It should be noted however, that the May I-131 sample results from all four (4) dairy locations had elevated {

LLDs. This was due to the relocation of the contractor's laboratory facilities and subsequent delays in sample analysis. The May I-131 results were deleted from evaluations. As reported in the 1987 Big Rock Point Annual Radiological Environmental Operating Report, the ,

1988 Sr-90 statistical evaluation level between the indicator and  !

control locations was again exceeded. However, the overall amount of Sr-90 (pci/L) detected was less. The annual mean of all  ;

indicator locations was 4.9 pCi/L in 1987 vs. an annual mean of 4.6 pCi/L in 1988. Dairy farm location 20-JC (J. Colovich, 4.5 mi SE) <

reported the greatest annual mean (indicator location) for both 1987 I and 1988. Results were 6.3 pCi/L and 5.5 pCi/L, respectively. The dairy f arm control location 23-BB (B. Bochniak,11.5 mi E) repJrted essentially the same results for both 1987 and 1988; that being 3.0 pCi/L and 2.9 pCi/L, respectively.

Evaluation of input data indicates that the Sr-90 activity levels were not caused by Plant effluents in that:

1. No Sr-89, I-131 or Cs-137 activity (less than LLD) was present in either milk or air filter samples.

2. The East sector from Big Rock Point has higher X/Q meteorology-cal data than the Southeast sector. Indicator dairy farm location 21-DK (D. Kuebler, 2.5 mi E) had 1988 Sr-90 annual l mean of 4.4 pCi/L which is lower than the Coluvich data. I

3. Selected crop samples from a garden (C. Halmin, 1.4 mi E) had minimal detectable levels of Sr-90 activity present with all j other isotopic activity results reporting below LLD as well. 1 Milk samples are required monthly (usually collected by the 1st Thursday of the month) from each designated collection location (4 t otal ) . A two gallon quantity of raw milk (grab sample) is obtained per collection location in order to meet analytical requirements.

Samples are treated with a sodium bisulfite (40 grams per gallon) preservative prior to being sent to Teledyne Isotopes for analysis.

D. Lake Water A total of 24 individual monthly lake water composite samples were I collected from 2 locations during 1988. Lake water samples f rom the IC0489-0086A-HP01 4

Lake-in (plant intake) and the Charlevoix Hunicipal Water System are collected daily and composited into monthly samples.

Evaluation of the monthly lake water analytical results was based on a data means comparison between the Lake-in and the Charlevoix Hunicipal Water Department (control location). The lake water results were also evaluated against BRP Technical Specification reporting limits.

Tritium and gross beta analyses are required for all lake water samples. The indicator and control location sample means were <500 pCi/L (LLD) for tritium and <4.0 pCi/L (LLD) for gross beta.

Both lake intake and Charlevoix Hunicipal Water samples are collected daily for composite into a monthly sample. A one gallon quantity of sample is sent to Teledyne Isotopes for analysis. No treatment of the water samples with a preservative is necessary.

E. Well Water A total of 12 individual monthly well water samples were collected from the BRP site well during 1988. Effective April 6, 1987, the City of Charlevoix started drawing water from Lake Michigan. The city-owned well fields had to be closed due to chemical contami-nation.

Evaluation of the BRP site well sample results is not needed because no positive results were received. Tritium and gross beta analyses are required for each monthly sample. For all well water samples, tritium results were <500 pCi/L (LID) and <4.0 pCi/L (LLD) for gross beta. No special or supplemental analyses were required during 1988.

A one gallon quantity of sample is sent to Teledyne Isotopes for analysis. No treatment of the water samples with a preservative is necessary.

F. Crops The collection of food crops / vegetation samples is not required by the BRP Radiological Environmental Monitoring Technical Specifica-tions. There are no regular select locations where food crop (in season) samples are collected, however in order to verify stack l effluent deposition patterns, several crop samples are usually l obtained annually, if available, from sectors E, SE, ESE or SSE.  !

For 1988, 2 dif ferent crop samples were collected f rom the following I locationt l

1. Carrot tops / cabbage leaves (mixed) from the C. Halmin garden, 1.4 mi E from BRP.

2. Pepper leaves / tomato plants (mixed) from the same location.

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1 Samples were collected' Cccober 27, 1988.

Evaluation of the. crop sample analytical results was direct. All data was combined and reported. No control location was used.

Of the isotopes listed on Table HP 10.2-2,' only the Sr-90 analyses resulted in any specific activity. All other analyses were less than Technical Specification LLD. No BRP Technical Specification reporting limits were exceeded nor were any special/ supplemental analyses required during 1988. Suspect background influences of Sr-90 similar to milk discussions.

Currently, food crop samples are not routinely collected like other sample media required by the BRP Radiological Environmental Monitor- +

ing Program. The samples are obtained seasonally, usually from the E, SE, ESE or SSE meteorological sectors and when specifically requrested by either the BRP or RSD Radiological Environment <t Coordinator. When collected, approximately 1 Kg of sample is placed-in a sealable plastic bag for shipment to Teledyne. Isotopes. No special treatment of the food crop samples with a preservative is necessary.  !

C. Sediment A total of 9 individual sediment samples were collected from 3 locations during 1988. Two (2) sediment samples were obtained from the BRP discharge channel; two (2) sediment samples from Nine Mile Pointe (2-NM, 3 mi ENE); and five (5) sediment samples from the -)

Ludington (North and South Jetty) control station. . Sediment samples are collected semi-annually.

Evaluation of the sediment analytical results was based on data means comparisons between the BRP/Ludington control samples and the BRP Technical Specification reporting limits.- The individual BRP sample locations were combined into one indicator location for comparison purposes; however if any one individual sample location had a greater specific isotopic annual mean than the other loca-tion (s), then that location is identified on Table HP 10.2-2.

Of the isotopic analyses listed on Table HP 10.2-2, only Sr-89 and some of the non parameter other gamma isotopes were less than LLD.

All other analyses resulted in trace amounts of activity present.

The Ludington control location reported a greater mean gross beta activity level than the BRP (site) locations.

No BRP Technical Specification action or reporting levels were exceeded, nor were any special or supplemental analyses required during 1988.

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Sediment samples are collected semi-annually from each designated location. A one (1) liter quantity grab sample is usually obtained a few yards off-shore. No treatment of the samples with a preserva-tive is necessary prior to shipment to Teledyne Isotopes.

H. Fish A total of 14 individual fish samples were collected from 6 loca-tions during 1988. Nine (9) samples were obtained from BRP site area (discharge, i mile South boundary, i mile North boundary, Mt.

McSauba and Nine Mile Pointe); and five (5) samples from the Ludington (North and South Jetty) control station. Fish samples are collected semi-annually.

Evaluation of the fish analytical results was based on data means comparisons between the BRP/Ludington samples and the BRP Technical Specification reporting limits. The BRP individual sample locations were combined into one indicator location for comparison purposes; however if any one individual sample location had a greater specific isotopic annual mean than the other locations, then that location is identified on Table HP 10.2-2.

Of the isotopic analyses listed on Table HP 10.2-2 only Sr-90 was present in trace amounts. All other isotopes (Sr-89 and other gamma) were less than LLD. The greatest level of Sr-90 was found in the i-mile South samples. No BRP Technical Specification reporting levels were exceeded, nor were any special analyses required during 1988. It should be noted that no fish were caught at Nine Mile Pointe (2-NM, 3 mi ENE) during the 2nd semi-annual sample collection period (10/15/88). Overall, there were less different species of ,

fish caught during 1988 than in past years.  !

t As a minimum, at least two (2) different fish species (ie, forage, sport fish, etc.) per designated sample location per year are collected. When caught, a one (1) liter quantity of fish sample is prepared for shipment to Teledyne Isotopes. Each sample is treated with 10 ml of a 10% formaldehyde solution for preservation.

I. Aquatic Biota The aquatic biota category consists of: crayfish, algae and periphyton. A total of 28 individual samples were collected from 6 locations during 1988. Sample types and locations are as follows:

Crayfish: 9 samples BRP (discharge, i mile South boundary, i mile North boundary, Nine Mile Pointe, and Mt. McCauba). No samples were collected at Ludington control.

Algae: 7 samples BRP (discharge, i mile South Boundary, i mile North boundary, Nine Mile Pointe and Mt. McSauba). Two (2) samples were collected at Ludington control (North and South Jetty).

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l Periphyton: 10 samples BRP (discharge, i mile South boundary, i l mile North boundary, Nine Mile Pointe, and Mt. McSauba). No samples were collected at Ludington control.

Aquatic biota samples are collected semi-annually at all designated l locations, however due to inclement weather at the time of sample I collection, the following locations had non-existant sample sized j quantities of aquatic biota available Crayfish Unavailable at Mt. McSauba during collection period i 10/15/88.

Algae: Unavailable at discharge during the collection period of l 6/18/88 and 10/15/881 and unavailable at i mile South during collection period 10/15/88.

Evaluation of the biota analytical results was based on a data means i comparison with the BRP Technical Specification reporting limits; {

and in the case of the algae samples, an additional comparison was '

made with the Ludington control samples. All the individual BRP sample locations were combined into one indicator (site) location for comparison purposes; however if any one individual sample location had a greater specific isotopic annual mean than the other locations, then that location is identified on Table HP 10.2-2. All elevated LLDs are evaluated as positive results.

Of the isotopic analyses listed in Table HP 10.2-2 for crayfish, only Sr-89 and the non parameter "other gamma" isotopes had <LLD activity. There were trace amounts of activity present for all other analyses. The discharge channel had the greatest annual sample mean for the reported isotopes. It should be noted that the 10/14/88 crayfish sample collected at i mile South had an elevated Sr-89 LLD due to the analyzing of too small a sample size by the l contractor laboratory.

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For the periphyton isotopic analyses, again only the non parameter "other gamma" isotopes resulted in <LLD activity. There were trace amounts of activity present for all other analyses. With the exception of i mile North having the greatest annual sample mean for Sr-89 and Sr-90 results, the discharge channel was the highest ,

indicator location for all analyses. The 10/14/88, i mile South periphyton sample results for Sr-89 was reported with an elevated LLD due to the analyzing of too small a sample size by the contractor laboratory.

The BRP algae samples were the only biota samples evaluated with a control station. There was no overall mean activity level for non parameter "other gansna" isotopes and Sr-89 reported for the indicator locations; however both i mile North and i mile South samples resulted in trace amounts of Mn-54, Co-60, and Cs-137 present.

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Nine Mile Pointe reported the greatest annual sample mean for gross )

beta with Mt. McSauba reporting the greatest annual sample means for Sr-89 and Sr-90 results. Also algae sample collected 6/16/88 at Nine Mile Pointe had elevated Sr-89 and Sr-90 results; and the 10/14/88 sample collected at Ht. McSauba had elevated Sr-89 results due to the analyzing of too small a sample size by the contractor ,

laboratory.

l No BRP Technical Specification action or reporting levels were exceeded, nor were any special or supplemental analyses required I during 1988.

1 Aquatic biota samples (crayfish, algae and periphyton) are collected semi-annually at each designated location, however inclement weather and/or rough water conditions can either make collecting sufficient sample quantities impossible or wash biota populations out of the immediate sampling vicinity. One (1) liter quantities of biota are cent to Teledyne Isotopes for analysis. Each sample is treated with 10 ml of a 10% formaldehyde solution for preservation.

J. Broad Leaf Vegetation No broad leaf vegetation samples were collected from the surrounding BRP environs during 1988. The collection of broad leaf vegetation samples serves as a backup and/or alternative sampling media in case any milk sampling location (s) become(s) unavailable. There were no problems associated with the quantity or quality of milk samples for the 1988 reporting year.

K. Caseous and Liquid Radwaste Effluent Composite Samples Although not a direct reporting component in the BRP Annual Radio- f logical Environmental Monitoring Report, results of the gaseous and liquid monthly radwaste effluent composite samples are evaluated against overall environmental trending data. This evaluation is the i basis for determining isotopic dispersion and deposition patterns within the surrounding environs of BRP. All isotopic LLDs are compared to BRP Technical Specification reporting levels.  !

l During 1988, there were three (3) monthly liquid radwaste effluent {

compocite samples (May, September and November) that had elevated '

Sr-89 LLDs. This was a result of the contractor laboratory analyzing too small a sample size. All other isotopic LLDs were met. The elevated Sr-89 results were evaluated as positive results.

3 There were no elevated LLDs for the gaseous effluent composite I samples. l l

Both the gaseous and liquid radwaste effluent composite samples are collected monthly and sent to Teledyne Isotopes for analysis. The liquid effluent composite sample is based on a specific ratioed volume amount of sample collected per total batch volume released.

The gaseous radwaste ef fluent composite sample results are based on IC0489-0086A-HP01 9 l

s analyzing four (4) or five (5) weekly stack gas filters. No apecial sample treatment with a preservative is required prior to laboratory analysis.

III . Assessment of Big Rock Point's Operational Environmental Impact In reviewing the 1988 Big Rock Point radiological environmental monitoring data 'and comparing'it to previous operational and pre-operational data, all trending parameters continue to indicate that the operation of Big Rock Point has minimal environmental impact. Most isotopic activity is at environmental " background" levels.-_ Since the Chinese stopped open atmospheric testing of nuclear devices in late 1981-82,. environmental background radiation levels continue to decrease.

The effect of the Chernobyl fallout (April 1986) on milk aquatic biota l and fish also appears to have had no lasting results. Evidence of an overall environmental isotopic build-up (attributable to Plant effluents) remains negligible as well. In most instances, sample analytical results were below previously established environmental background levels.

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Enclosures A. Big Rock Point 1988 Land Use Census l

l B. Health Physics Procedure 10.09: Big Rock Point Radiological Environ-mental Program Sample Collection and Shipment Procedure (with sample locations, maps, etc.)

C. Big Rock Point 1988 (annual) Radiological Environmental Monitoring Program Data as provided by Teledyne Isotopes Midwest La bo ra to ry ,

Northbrook, Ill.

D. Teledyne Isotopes Midwest Laboratory EPA Interlaboratory Comparison Program Results E. Data Craphs

1. Big Rock' Point Air Particulate (gross beta) 1988 Trending and Big Rock Point Air Particulate (gross. beta) 1983 - 1988 Operational Comparison Graphs

2. Big Rock Point TLD (gamma) 1988 Trending and Big Rock Point _TLD (gamma) Monthly, Quarterly and Annual 1983 - 1987 Operational Comparison Graphs

3. Big Rock Point Milk (Sr-90) 1988 Trending and Big Rock Point Milk (Sr-90) 1983 - 1988 Operational Comparison Craphs

4. Big Rock Point Well Water (gross beta) 1988 Trending

5. Big Rock Point Lake Water (Intake vs. Discharge gross beta and .

tritium) 1988 Trending and Big Rock Point Lake Water (intake vs.

discharge gross beta and tritium); 1960 - 1962 Pre-operation /1983

- 1988 Operational Comparison Graphs

6. Big Rock Point Fish (gross beta) 1988 Trending and Big Rock Point Fish (gross beta) 1983 - 1988 Operational Comparison Graphs (including Ludington Control 1984 - 1988)

7. Big Rock Point Sediment (gross beta) 1988 Trending and Big Rock Point (gross beta) 1983 - 1988 Operational Comparison Graphs (including Ludington Control 1984 - 1988)

8. Big Rock Point Aquatic Biota (crayfish, algae periphyton gross beta) 1988 Trending and Big Rock Point Aquatic Biota; 1960 - 1962 Pre-operation /1983 - 1988 Operational Comparison Graphs (including Ludington Control 1984 - 1988 - algae only)

IC0489-0086A-HP01 11

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ENCLOSURE A BIG ROCK POINT 1988 LAND USE CENSUS l

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OC0589-0009-NLO2

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To JLBeer, Big Rock Point o1]IY From MAMoore,@alisades ' CONSUMERS POWER Date October 5, 1988 COMPANY Subject BIC ROCK POINT- Internal 1988 LAND USE CENSUS Correspondence CC RLBurdette, Big Rock Point M AM88 *010 DCC: 740/72*10*03/LP The attached tables and map are the results of the Big Rock Point Land Use Census conducted August 17, 1988. Table 10.11-1 references the distance from Big Rock Point to the nearest residence, garden, beef / dairy cattle and goat per meteorological sector. Table 10.11-2 identifies the locations of the nearest residence, of all gardens (greater than 500 square feet) within a three (3) mile radius of the plant, and all beef / dairy cattle within a five I (5) mile radius of the plant. The only goats located while conducting the 1988 BRP Land Use Census were in the SSE sector at the 3.25 mile limit. Table 10.11-3 lists the critical receptor locations used in calculation of offsite doses by the CASPAR computer program. An accompanying map illustrates Table 10.11-2.

Prior to conducting the BRP 1988 Land Use Census, both the Charlevoix. County _  !

Agricultural Extension Of fice and Consumers Power Company Northwestern Region

- District Manager's Office (Traverse City) were contacted August 12, 1988 as required in Procedure HP 10.11.- There' vere no significant differences between the 1987 and 1988 Land Use Census.

If you have any questions, please contact me.

I Reviewed and Authorized /0 48 '

TP Neal, RMC Administrator Date IC0988-0194A-HP01

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BIC ROCK POINT LAND USE CENSUS REPORT TABLE 10.11-1 Distance to the nearest residence, garden, milk cow, beef cow and goat in'each Sector.

SECTOR RESIDENCE CARDEN DAIRY COW BEEF CATTLE COAT WSW 2.5 mi >5 mi >5 mi >5 mi >5 mi SW 1.1 mi >5 mi >5 mi >$ mi >5 mi SSW 1.3 mi 2.1 mi >5 mi >5 mi >5 mi S 1.9 mi >5 mi >5 mi 2.5 mi >5 mi SSE 1.7 mi 1.8 mi 3.5 mi 3.5 mi 3.25 mi

.SE 1.7 mi >5 mi 4.5 mi 2.0 mi >5 mi ESE 1.5 mi 2.4 mi 2.6 mi 2.6 mi >5 mi E 1.4 mi 2.5 mi 2.5 mi 2.5 mi >5.mi ENE 2.3 mi >5 mi >5 mi >5 mi >5 mi i

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l IC0988-0194A-HP01 .]

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3 BIC ROCK POINT LAND USE CENSUS REPORT TABLE 10.11-2 Verification of -Items Locations of nearest residence; of all gardens greater than 500 square feet within a three mile radiums of plant; and all beef / dairy cattle within a five mile radius of plant.

Sector and Road Location Description Item Numbe r/ Comment WSW Birchwood Ranch Shores Residence 1 McSauba North Point SW Lackin's residence Residence 1 Dirt Road (Birchwood Ranch Shores)

Dirt trail off of Martin .

Rd l

SSW Edward K. Shanahan, Residence 1 {

Private Drive Private drive North of j US-31 q l

SSW Robert Burns Carden 1 I Boyne City Road South side of road adj.

to Mfg Nat'l Bank property S C. Skeel Residence 1 North (dead) end North of Boyne City Road of See Road S D. Buckner Cattle 2-beef l See Road 8398 See Road, approx. 250' i South of See Road and Boyne City Road intersection SSE Robert Dyksterhouse Residence 1 I Private drive West of Old US-31, adj. Carden 1 Susan Lake SSE Hoxie, Box 411 Carden 1 Shrigley Road Shrigley Road SSE Lester Umlar Farms Cattle 30-beef Intersection of Southwest corner of Boyne City and intersection Quarterline Roads 1

IC0988-0194A-HP01 i

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Table 2 (cont'd)

Sector and Road Location Description Item Numbe r/ Commen t SSE Jerry & Hazel Haggerty Cattle 8-dairy Intersection of Farms, Southeast corner Boyne City and of intersection Quarterline Roads SSE John Haggerty Farm Coats 3 Intersection of Northeast corner of Boyne City and intersection 1 Quarterlinr Roads SE Daniel & Rebecca Berg Residence 1 <

Intersection of Old Route 3; Southwest corner f US-31 and Smith Road of intersection i SE Ceorge Smith Cattle 2-beef i Smith Road End of Smith Road, South  !

of Old US-31 SE R.M. Jess, 407 Shrigley, Cattle 8-beef Intersece. ion Old Southeast corner of '

US-31 & Shrigley Rd intersection SE Betty Straw Cattle 9-beef Intersection of Northeast corner of Burgess and Quarter- intersection line Roads SE Lee Sneathen, Jr. Farms, Cattle 20-beef '

Intersection of West side of intersection 4-dairy Maple Grove and j Dalton Road i SE

• John and Shirley Colovich Cattle 40-dairy Mapic Grove between East side of Maple Crove Rd. 5-beef Quarterline and Dalton Road intersections ESE J. Bowman, Burgess Road, Residence 1 Burgess Road 1 mile South of US-31 ESE CM Carden 1 Upper Bay Shore Road 1 mile East of Upper Bay Shore and Burgess Road intersection (South side of road)

IC0988-0194A-HP01

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Table 2 (cont'd) l Sector and Road Location Description Item Numbe r/ Coment l

l l ESE C. Hamlin, R. 3, East side Carden 1 Burgess Road of Burgess Road ESE L W Kuebler, } mile East Cattle 12-beef Upper Bay Shore Road of Upper Bay Shore and (North side of road) Burgess Rd intersection ESE Merle Hand, 304 Upper Bay Cattle 6-beef Upper Bay Shore Road Shore Rd, i mile West of 3-dairy Upper Bay Shore and Maple Crove Road (South side of road)

ESE

• Dan Kuebler Farms, Cattle 13-beef Upper Bay Shore Road i mile West of Upper Bay 15-dairy (bisected by E sector Shore and Maple Crove Road Carden 1 boundary line) (North side of road)

ESE Ed Smally, Box 314B, West Cattle 1-dairy Stolt Road end (turnaround area) of 5-beef Stolt Road, 3/4 mi from intersection of Stolt and Maple Crove Road ESE Thomas Hamlin, Northeast Cattle 3-dairy Stolt Road corner intersection of 9-beef Stolt and Murry Roads E Ralph J. Purvis, i mile Residence 1 Burgess Road South of intersection of Burgess and US-31 E Leo Burnett, Northwest Carden 1 Maple Crove Road corner of intersection of short dead-end road and Maple Crove Road; i mile South of US-31 E

• Dan Kuebler Farms, Cattle 13-beef Upper Bay Shore } mile West of Upper Bay 15-dairy Road (bisected by Shore and Maple Crove Road Carden 1 ESE sector boundary (North side of road) line) l l

IC0988-0194A-HP01

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Table 2 (cont'd)

Sector and Road Location Description Item Number / Comment E T. McClellan, Northeast corner Cattle 1-beef Intersection of Maple of intersection of Maple Grove 1-dairy Grove and Upper Bay and Upper Bay Shore Road Shore Road E Hiram & Margaret Steward, 1 Cattle 7-dairy Upper Bay Shore Road mile East of intersection of Upper Bay Shore Road and Burnett Road E Raymond Griffin, Northeast Cattle 3-dairy Intersection of Upper corner of intersection 30-beef Bay Shore and Murry Roads E John Murry, Southeast corner Cattle 3-beef ,

Intersection of Upper of intersection l Bay Shore and Murry Roads l E John Speigel, West corner Cattle 2-beef Intersection of Murry of intersection Road and Old US-31 ENE Werner Cunningham, South side Residence 1 US-31 of US-31, 2,3 miles East of BRP Plant

• Note: Current milk sampling locations.

1 I

IC0988-0194A-HP01 1 l

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7 BIC ROCK POINT LAND USE CENSUS REPORT

' TABLE 10.11 Critical Receptor Identification ~

Distance Sector (miles) Location / Description -Item ***X/0 (Sec/m3 )

E 0.6 **Lexalite Plastics Factory 4.20E-08 Corp.

E 1. 4 ' Ralph J. Purvis, i Residence / 5.00E-08 mi. South of inter- Carden section of Burgess and US-31 E 0.57 Site Boundary N/A 4.20E E 2.50

• Dan Kuebler Farms,. Beef Cattle 3.60E-08  ;

} mile West of Upper Dairy Cows Bay Shore and Burges Road intersection (North side of road)

SSE 3.25 John Haggerty Farm, Coats 2.40E-08 intersection of Boyne City and Quarterline Roads

• Note Current milk sampling location.

• • Notet Not used as critical receptor location in BRP CASPAR program, however factory is adjacent to site boundary and staffed 24-hours per day.

• • • Notes Based on BRP 3 year composite meteorological data, 1984-86.

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IC0988-0194A-HP01 l i

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ENCLOSURE B HEALTH PHYSICS PROCEDURE 10.9 j BIG ROCK POINT RADIOLOGICAL ENVIRONMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT i i

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OC0589-CJO9-NLO2 ii IL ema ,, o np wp r i- ~ %Q' f/

l PALISADE 3 NUCLEAR PLANT Prce W3 HP 10.9 I HEALTH PHYSICS PROCEDURE R visies 0 Page i TITLE: BIG ROCK POINT RADIOLOGICAL ENVIRONMENTAL l 2, PROCRAM SAMPLE COLLECTION AND SHIPMENT Table of Contents

)

tus 1.0 PURPOSE ............................. 1 l

2.0 REFERENCES

. . . . . . . ..................... 1 3.0 PREREQUISITES .. . . . . . . . . . . . . . . . . . . . . . . . .. 1 J

4.0 PRECAUTIONS AND LIMITATIONS ................... 1 5.0 PROCEDURE ............................ 2 5.1 REMP AIR SAMPLE COLLECTION . . . . . . . . . . . . . . . . . . .. 2 5.2 REMP WELL (DRINKINC) WATER SAMPLE COLLECTION -

CEARLEVOIX, MICHICAN . . . .................... 4 5.3 REMP MILK SAMPLE COLLECTION ................... 5 5.4 REMP AQUATIC BIOTA COLLECTION .................. 5 5.5 REMP SEDIMENT SAMPLE COLLECTION ................. 6 5.6 REMP TLD SAMPLE COLLECTION . . . . . ............... 7 6.0 ACCEPTANCE CRITERIA ....................... 9 7.0 RECORDS AND ATTACHMENTS ..................... 9 7.1 RECORDS '

............................. 9 7.2 ATTACHMENTS .................. ......... 9 ATTACHMENTS , " Big Rock Point Environmental Sample Collection Schedule" , " Big Rock Point Sampling Locations" , " Sample Identification" , " Sample Packaging and Shipping" . " Big Rock Point Sample Collection Forms" hp1285-01113 154 e

F -

PALISADES WUCLEAR PLANT Prec Ne.HP 10.9 l HEALTH PHYSICS PROCEDURE R3visic2 0 i Page 1 of 9 i TITLE: SIC ROCK POINT RADIOLOGICAL ENVIRONMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT-I J

1.0 PURPOSE l 1.1- To. provide methodology for collection, identification and shipment of I environmental samples in support of the Radiological Environmental Monitoring Program (REMP).

2.0 REFERENCES

2.1 Big Rock Point Technical Specifications 13.2; Table 13.3-1.

2.2 Regulatory Cuide 4.15(7)

'l 2.3 10 CFR 50, Appendix I 2.4 Nuclear Operations Department Procedure H05, " Radiological Environmental Monitoring."

2.5 Palisades Administrative Procedure 7.06, " Radiological Environmental Program Administrative Controls" 2.6 Radiological Environmental Monitoring Proaram Sample Shipping Manual, Teledyne Isotopes Midwest Laboratory, Rev 2, September 20, 1985 3.0 PREREQUISITES As indicated in Procedure 4.0 PRECAUTIONS AND LIMITATIONS 4.1 This procedure shall be applicable to Big Rock Point CHP, Radiological Services Department, Environmental Service Department and any contractual personnel assigned to collect or evaluate REMP. samples.

4.2 Any revisions to this procedure shall be reviewed against Big Rock Point Technical Specifications to verify compliance to all requirements.

4.3 Deviations from the required sampling schedule shall be documented in the Annus1 Radiological Environmental Operating Report.

4.4 Every effort shall be made to complete corrective action on mal-functioning sampling equipment prior to the end of the next sampling period.

4.5 If it is not possible to obtain the required samples, suitable alternative media and locations shall be substituted within 30 days.

hp1285-0111a-91-154 r

_ _ _ . _ _ _ _ _ _ _ _ _ _ . _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ . _ _ _ _ _ _ _ _ . _ _ .I

m PALISADES NUCLEAR PLANT Proc N3 HP 10.9 HEALTH PHYSICS PROCEDURE _ Revisica 0 Page 2 of 9 TITLE: BIC ROCK POINT EADIOLOCICAL ENVIRONMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT 4.6 Samples shall be collected, prepared and shipped for analysis in a j timely manner to preserve integrity. Other specific handling precautions for sample media are indicated in Section 5.0 as required.

l 5.0 -PROCEDURE j NOTEt Collect samples using the following methodology in accordance with schedule and location data described in Attachments 1 and 2.

l 5.1 REMP AIR SAMPLE COLLECTION 5.1.1 Precautions i

a. New filters and cartridges should be transported and handled such that potential contamination of them is minimized (ie, placed in ]

clean plastic bags, etc).

b. If an air sampling unit is discovered not operating, attempt to I find the cause and repair. If this cannot be done, replace applicable component and document on air sample collection data sheet.

c. Airflow meters shall be calibrated annually by General Meter. All inservice air meters will have affixed a valid calibration sticker / card stating date of calibration, calibration due date and initials of technician performing calibration.

l

d. Airflow meters will be : hanged out prior to the expiration of I calibration dates. Replacement air meters are available from the BRP Radiological Enviror. mental contact.

e. If air leakage is observed requiring the replacement of an airflow j meter, contact either the BRP or RSD Radiological Environmental contact within 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br /> of changeout. Document on air sample collection data sheet.

5.1.1 Prerequisites

a. Class fiber air filters

b. Absorbent cartridges for iodine sampling

c. Classine envelopes

d. REMP air sample data sheet (containing installation data)

e. Replacement air sample meters (as required) hp1285-0111a-91-154 l

l l

)

PALISADES NUCLEAR PLANT Proc W3 HP 10.9 i HEALTH PHYSICS PROCEDURE Revision 0 Page 3 of 9 TITLE: BIC ROCK PolNT RADIO!ACICAL ENVIRONMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT 5.1.3 Weekly at each sample location, perform the followingt

a. Open protective cover on air sampler and record the vacuum reading and the integrated gas meter readings onto the sample collection sheets under " Removed" column.

NOTE It is unnecessary to turn air sample unit off when changing out filter holders.

NOTE! If airflow meter must be replaced, record the meter removed data in columns provided. Under the " Remarks" column, record the meter number, date and meter reading for the new replacement airflow meter.

b. Disconnect the air filter holder and observe if vacuum gauge reading exceeds 20 inches of mercury. If vacuum does not exceed 20 inches, then inspect unit for air leakage and perform appropriate maintenance.

c. Remove filter holder to enclosed vehicle.

d. Remove and replace filters wblie inside vehicle.

NOTE Center the filter properly to prevent leakage.

e. Place particulate filter in glassine envelope or plastic and identify as per Attachment 3. ,

i

f. Identify carbon filter as per Attachment 3.

3 Reattach the filter holder. Filters and filter holder must be positioned so that the airstream first passes through the particulate filter and then through the charcoal cartridge.

h. Place hand over filter inlet to form a seal. Record maximum stable vacuum reading obtained when (by visual observation) the airflow meter is recording zero flow rate. Record vacuum reading under test condition. If vacuum is less than 20 inches of mercury and the gas meter is indicating observable flow, leakage is occurring.

Leakage must be repaired or the airflow meter / pump replaced. If the vacuum reading obtained is greater than 20 inches of mercury, then air leakage is considered nil.

l NOTE: If repair or replacement of air meter is required, repeat 5.1.3.h and record new test vacuum under " Remarks" column.

i. Remove hand and record operating vacuum on data sheet. Normal vacuum obtained will range between 1 and 15 inches of mercury. If less than 1 inch of mercury is obtained, significant filter bypass leakage may be occurring. Reposition the filters until a vacuus of hp1285-0111a-91-154

U PALISADES NUCLEAR PLANT .Prec ND HP 10.9 HEALTH PHYSICS PROCEDURE Rsvisica O Page 4 of 9-TITLE: BIC ROCK POINT RADIOLOGICAL ENVIRONMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT about 1 inch of mercury is.obtained. If the vacuum reading cannot be maintained between 1 and 15 inches of mercury, replace the-airflow meter with a spare unit.

NOTE (1) Under high moisture or dust conditions, a vacuum reading greater than 15 inches of mercury may be considered normal. These climatic conditions should be noted in the " Remarks" coluem on the sample sheet.

(2) If vacuum indicator is resting on the " peg," record 0 vacuus.- If vacuum indicator is not resting on the " pes" but is less than the first graduation on the vacuum gauge, record 1 in the vacuum column.

j. Close cover and proceed to the next station.

k. Record pertinent information, date and sign data sheet.

1. Transcribe gas meter reading and. operating vacuum to the " installed readings" columns on the sample data sheet to be used for the upcoming week's sample collection.

5.2 REMP WELL (DRINKINC) WATER SAMPLE COLLECTION - CHARLEVOII, MICHICAN 5.2.1 Prerequisites

a. Clean one-gallon polyethylene containers (labeled as per Attach-ment 3)

b. REMP Miscellaneous Data Sheet 5.2.2 Daily perform the following sample collections

a. Turn on water supply and allow water to run for approximately one minute to purge the line.

1 l

b. Draw off approximately 125 mL of tap water and add to polyethylene i container. j l I

c. Repeat Steps 5.2.2.a and 5.2.2.b daily for entire month. Note any l day's sample not taken in " Remarks" column of sample data sheet.

I

d. At end of month, seal containers.

]

i

e. Record on the Data Sheet the location, type, date, time, quantity and, under " Remarks," indicate any pertinent information (ie, j composite sample, start and finish dates, etc). Sign form in space provided.  ;

i hp1285-0111a-91-154 1

PALISADES WUCLEAR PLANT Prce ND HP 10.9-HEALTN PHYSICS PROCEDURE R:visicn 0 Page 5 of 9 TITLEt SIC ROCK POINT RADIOLOGICAL ENVIRONMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT 5.3 REMP MILK SAMPLE COLLECTION 5.3.1 Precautions Milk samples are required to be sent to the laboratory as soon as possible because of the short decay time of I-131. Any undue delay may cause analytical sensitivity requirements of the Technical Specifications to be exceeded.

5.3.2 Prerequisites

a. Two clean polyethylene one gallon containers for each sample location

b. Eight premeasured packets of sodium bisulfite preservative (one packet per gallon of milk)

c. REMP miscellaneous data sheet 5.3.3 Monthly, at each sample location, perform the followings

a. Obtain two one-gallon grab samples of raw milk and pay milk supplier.

NOTE Two clean, empty polyethylene one gallon containers may be left with milk supplier for the next month's samples when picking up the current month's samples. If problems are encountered in obtaining a sufficient quantity of milk sample, notify either the BRP or RSD Radiological Environmental contact.

b. Label containers as per Attachment 3.

c. Package and ship samples as per Attachment 4.

d. Record on Data Sheet, location, type, date, time, quantity, and under " Remarks," any pertinent information. Sign form in space provided.

5.4 REMP AQUATIC BIOTA COLLECTION NOTE: Collection to be coordinated between the Radiological Services Department RMC Section and the Environmental Services Department.

5.4.1 Precautions

a. At least one individual in the collection party is required to have a State of Michigan Collector's Permit for fish sample collection.

hp1285-0111a-91-154

PALISADES NUCLEAR PLANT Prce N3 HP 10.9 HEALTH PHYSICS PROCEDURE Revision 0 Page 6 of 9 TITLE: BIC ROCK POINT RADIOLOGICAL ENVIRoliMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT 5.4.2 Prerequisites

a. Small frog spears (plus replacement spearheads)

b. Plexiglas bottom buckets (or boxes)

c. Wire or stiff nylon brushes

d. Black " magic" markers for writing sample identification on containers

e. Cill net

f. Plastic one-liter wide-mouth bottles and tape

g. REMP Miscellaneous Data Sheets

h. 10% formaldehyde solution

i. Fillet knives

j. Scrapers (putty knives) 5.4.3 Semiannually, samples shall be collected as follows:

a. Periphyton is collected by scraping from rocks into a pail. When ,

sufficient sample is collected, excess water is gently poured off. l The partially solidified periphyton is then transferred to a liter i sample bottle. 1

b. Attached filamentous algae is collected by hand from underwater debris, rocks, obstacles, etc, and compacted into a liter bottle.

c. One liter of crayfish is collected by spearing and hand picking.

d. Bottom feeding forage fish and predator-type (game) fish are collected by gill netting. One liter of flesh is to be collected from each type of predominant fish species caught.

f. Record on Data Sheet, location, type, date, time, quantity, and, under " Remarks," any pertinent information. Sign form in space provided.

1 5.5 REMP SEDIMENT SAMPLE COLLECTION 5.5.1 Prerequisites

a. One-liter wide-mouth plastic sample bottles hp1285-0111a-91-154

m PALISADES NUCLEAR PLANT Pree W3 HP 10.9 HEALTH PHYSICS PROCEDURE Revision 0 Page 7 of 9 TITLE: BIC ROCK POINT RADIOLOGICAL ENVIRONMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT

b. Dredge or hand scoop

c. Miscellaneous Data Sheet 5.5.2 semiannually, at each sample location, Radiological Services / Environ-mental Services personnel shall collect sediment samples.

a. Record on data sheet, location, type, date, quantity, and, under

" Remarks," indicate surface area of sample and depth at which '

sample was obtained. Sign form in space provided. [

1 5.6 REMP TLD SAMPLE COLLECTION l 5.6.1 Precautions

a. Under no condition shall TLDs be routinely taken into the plant.

Site TLDs for Big Rock Point shall be placed in the lead cave located in the guard shack and the BRP Radiological Environmental contact notified immediately. -

b. Three sets of TLDs are present at each location. The packets are labeled MONTHLY, QUARTERLY and ANNUALLY to ensure proper replacement.

5.6.2 Prerequisites

a. TLDs I

b. Environmental TLD Report Sheet 5.6.3 Monthly, quarterly and annually at each sample location, perform the following NOTE Monthly TLDs are to be changed each monthi quarterly TLDs during January, April, July and October and annual TLDs during January.

-a. Upon receipt of TLDs from the laboratory contractor, all TLDs shall.

be inventoried and immediately placed in the lead cave (at offsite sample collector's residence). Note date of receipt on data sheet.

b. Field TLDs shall only be removed from the lead cave for delivery to their proper locations. All control TLDs remain in the lead cave throughout the entire exposure period.

c. Remove and replace TLDs at each sample location.

d. For any missing TLDs, perform the followingt (1) Search immediate area.

hp1285-0111a-91-154

1 l

PALISADES NUCLEAR PLANT ' Proc W3 HP 10.9 i HEALTH PHYSICS PROCEDURE Revision 0 l Page 8 of 9 I TITLE: BIC ROCK POINT RADIOLOGICAL ENVIRONMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT (2) If lost TLD is found, collect it and perform standard change-c at procedure.

(3) If lost TLD is not found, post the new TLD in proper location.

(4) Record in " Remarks" column of Data Sheet, any.of the above circumstances. j

e. Store collected field TLDs in lead cave along with contral TLDs until ready for mailing to Laboratory contractor. Mark "Do not x-ray" on TLD package.

NOTE: Transportation control TLDs are to be stored in the special lead shield i provided by laboratory contractor only after field TLDs are posted. q Make sure that the properly matchina control TLDs are returned with its 1 designated batch field TLDs. Also, ensure that laboratory contractor's i own TLD Data Sheet is completed and enclosed with shipment.

f. Record on Data Sheet, location, type, date, time and, under

" Remarks," any pertinent information. Sign form in space provided.

5.7 Be sure that all collected samples are identified and labeled as per l Attachment 3.

5.8 Complete the appropriate Sample Collection Data Sheet and distribute as follows:

1 i

White - Analytical Laboratory Yellow - BRP Radiological Environmental Contact Pink - Radiological Services Department Environmental Contact (Palisades)

Cold - Sample Collector 5.9 Obtain best available replacement for any missing sample. Notify BRP or RSD Radiological Environmental contact with description and location of the replacement sample.

5.10 Explain missing samples or malfunctioning. equipment in writing to BRP or RSD Radiological Environmental contact.

5.11 Package and ship samples according to Attachment 4.

5.12 Ensure that sampling stations are maintained and calibrated as required.

hp1285-0111a-91-154 L_ ____ _ _ _ - _ - _ _ _ - _ _ _ - _ _ _ _ _ _ _ - _ _ _ _ _

PALISADES NUCLEAR PLANT Prce N3 HP 10.9 l HEALTH PHYSICS PROCEDURE Revisica O Page 9 of 9 TITLE BIC ROCK POINT RADIOIACICAL ENVIRONMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT I

6.0 ACCEPTANCE CRITERIA Proper completion of procedure 7.0 RECORDS AND ATTACHMENTS 7.1 RECORDS 7.1.1 Distribution of Sample Data Collection Sheets as specified in Sec-tion 5.8 7.1.2 Sample Data Collection Sheets shall be retained in the Uniform File Indes under DCC number BRP 740/24*03*10/LP 7.2 ATTACHMENTS Attachment 1, " Big Rock Point Environmental Sample Collection Schedule" I

Attachment 2, " Big Rock Point Sampling Locations" Attachment 3, " Sample Identification" Attachment 4, " Sample Packaging and Shipping" Attachment 5, " Big Rock Point Sample Collection Forms" j

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hp1285-0111a-91-154

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'Prce W3 HP 10.9-Attcchment 1 Revision 0 Page 1 of 2 ,

ENVIRONMENTAL SAMPLE COLLECTION SCHEDULE Big Rock Point i

Esposure Pathway Number of Samples Collection and/or Samole and Locations

• Sample Type Frequency Airbornet i Particulate 1 - Onsite Continuous at Weekly l 3 - Within 5 miles (8 km) approximately of the site boundary 1 cfm (may be in different less due to sectors dust loading).

2 - Vicinity of com-munities having the highest calculated annual average ground level-D/Q 1 - Control Iodines Same as particulate Same as Weekly particulate W,aterborne t Lake Water 1 - Intake Daily composite Monthly 1 - Discharge To obtain a one-gallon sample Well Water 1 - Charlevoix Daily composite Monthly Municipal System 1 - Site one-gallon grab Monthly ~

sample Ingestions Milk 3 - Within a 2-7 mile Two gallon grab Monthly (3.2-11.2 km) radius sample L 1 - Control within 10-20 l miles (16-32 km)

• If samples are unavailable at the specified location, an attempt should be made to sample at an alternate location (refer to 4.5).

hp1285-0111b-91-154

_ _q Pree No HP.10.9 Attcchment 1 )

-R: vision 0 Page 2 of 2 Exposure Pathway Number of Samples Collection and/or Sample and Locations

• Sample Type Frequency 1

Fish Various game species One-liter fish Semiannually in vicinity of plant flesh Ludington control Aquatic' Biotas (Crayfish, 1 - Discharge One-liter grab Semiannually shore minnow, sample filamentous 1 - 1/4 mile north algae, peri-phyton) 1 - 1/4 mile south 1 - Nine alle pt 1 - Mt McSauba 1 - Ludington control Direct:

TLD 4 - Onsite Continuous Monthly, quarterly and 6 - Site boundary annually l 3 - Within a 3- to 5-mile (4.8-8 km) radius 3 - 10 to 50 miles (16-80 km) distant Sediment 1 - 1 to 3 miles One liter grab Semiannually east (1.6-4.8 km) sample of site 1 - Discharge 1 - Ludington (control)

(2 samples recommended) l

• If samples are unavailable at the specified location, an attempt should be made to sample at an alternate location (refer to 4.5).

hp1285-0111b-91-154

Prec W3 HP-10.9 Attcchme:c 2 Revision 0 Page 1 of 5 SAMPLINC LOCATIONS Big Rock Point Plant Sample

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I f" E a a u8 ut i  ; 6  % a 4 M 4' 42 3 & 4 '& # C Station Code Location 1 ST Big' Rock Point Nuclear X X X X X X X X Plant 2 NM Nine Mile Point, 3 Miles X X X X X X (4.8 km) E 3 CH Charlevoix, Michigan X X X X 4-1/2 Miles (7.2 km) SW 4 SL Susan Lake, 3.5 Miles X X X (5.6 km) SE 5 PT Petoskey, Michigan X X X l 10-1/2 Miles (16.8 km) E 6 BC Boyne City, Michigan X X X 12 Miles (19.2 km) SE 7 TR Traverse City, Michigan X X X 50 Miles (80 km) SSW 8 D Control (Lead Cave) X D Wilks, Charlevoix, Michigan 9 A Meteorological Tower I 10 B West Site Boundary on X Lake Michigan 11 C South Site Boundary, X Shanahan's Orchard 0.8 Miles (1.3 km) SW L2 E Southeast Boundary X 0.9 Miles (1.4 km) SSE, US-31 Near Railway Spur hp1285-0111c-91-154 l

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Revision 0 Page 2 of 5 Sample ,

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13 F First CP Co Pole in Right X of Way South of US-31 14 C Information Center Site X l 15 H Vent Shed (South Side) Site X 16 J Susan Creek Near Lake X l Michigan 17 K Discharge Canal (Fisherman) X l I

18 L Access Control X 1 19 MS Mt McSauba, PE, 3 M11ee X (4.8 km) W 20 JC J Colovich - X Maple Grove Road j Charlevoix, Michtsan 4.5 Miles (7.2 km) SE 21 DK D L Kuebler, Upper Bay X g Shore Road, Charlevoir Michigan 2.5 Miles (4 km) E i 22 RM R McCraney, Horton Bay Road X Charlevoix, Michigan 6.5 Miles (10.4 km) SE 23 BB B Bochniak, Resort Pike Road, Petoskey, Michigan X l 11.5 Miles (18.4 km) E 24 STS 1/4 Mile (0.4 km) South X X Boundary 25 STN 1/4 Mile (0.4 km) North I X Boundary 26 LP Ludington Pumped Storage X X X hp1285-0111c-91-154

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u Prce No HP 10.9 Attcchment 3 i Rcvisien 0  !

Page 1 of 2 l SAMPLE IDENTIFICATION I

NOTE: Use waterproof pen. Do not place paper labels inside containers.

1. Collected samples shall be adequately identified.

2. The plant identification shall be written on each sample container as follows: 1 Big Rock Point BRP Palisades PAL

3. The sample media type can either be written out or abbreviated on container using the below-listed sample identification codes

a. Routine Sampless j Air Particulate AP Air Iodine AI Well Water WW Lake Water LW Milk KK Drinking Water - Raw DW-RAW Drinking Water - Treated DW-TEEATED

b. Special Samples Vegetation VE Fish FI Sediment SD Periphyton PE Crayfish CF j i

Algae AL Shore Minnow SM i

hp1285-0111d-91-154 1

Prac W3 HP 10.9 i Attcchment 3 Revision 0 Page 2 of 2 SAMPLE IDENTIFICATION

5. The sample location (where collected) and collection dates are then to be written out on sample containers.

NOTE! Sample locations shall agree with Attachment 2. l i'

6. The sample container identification and data recorded on the sample collection sheet must agree.

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Proc No HP 10.9  :

Attcchment 4  !

Page 1 of 1 Revision 0 l

SAMPLE PACKACINC AND SHIPPING I i

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1. Samples shall be clearly labeled per Attachment 3.

2. All liquid, biota, fish and sediment samples shall be sealed with tape to prevent leakage.

3. Liquid samples shall be shipped separately from air particulate, air iodine filters and TLDs.

4. Sufficient packing material (eg, crumpled newspaper) shall be used to i J

avoid possible sample damage during shipment.

5. Air filters shall be packaged in glassine or plastic envelopes.

6. For TLD shipments, make sure that Laboratory contractor's own TLD data j sheet is enclosed with package.

)

7. Milk samples shall be shipped as ooon as possible. Be sure to add one packet (40 grams) of sodium bisulfits as a preservative to each sample.

8. Food products shall be shipped as soon as possible. No preservative is necessary.

9. Fish and biota samples shall be shipped with 10% formaldehyde (preservative) solution added. Only 10 milliliters per sample are required.

10. The white copy of the Collection Data Sheet shall accompany all samples j shipped to the analytical laboratory.

11. Samples shall be sent to the following address:

Teledyne Isotopes Midwest Laboratory Act C Carlson 1509 Frontage Road  !

Northbrook, IL 60062

12. All samples shall be sent to the Laboratory contractor with minimal delay after collection so as to avoid alteration of analytical sensitivity requirements. i hp1285-ollle-91-154

Pro:5 No MF 10.9 Attaciument 5 Page 1 of 3 Revision 0 BIC M POINT SAMM.E COLLECTION FORMS-

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