ML18054A722

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1988 Radiological Environ Monitoring Rept
ML18054A722
Person / Time
Site: Palisades 
Issue date: 12/31/1988
From:
CONSUMERS ENERGY CO. (FORMERLY CONSUMERS POWER CO.)
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ML18054A720 List:
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NUDOCS 8905050243
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{{#Wiki_filter:* ATTACHMENT Consumers Power Company Palisades Plant Docket 50-255 1988 RADIOLOGICAL ENVIRONMENTAL MONITORING REPORT May 1, 1989 159 Pages OC0589-0127-NL04

Palisades Nuclear Plant Annual Radiological Environmental Operating Report January through December, 1988 IC0489-0088A-HP01

I. Introduction The 1988 Palisades Nuclear Plant Annual Radiological Environmental Operating_Report provides a summary and data interpretation of the Palisades Radiological Environmental Monitoring Program as conducted during the 1988 reporting period. Reporting requirements are detailed in Technical Specifications 4.11, Table 4.11-1 thru 4.11-3, 6.9.3.1.B and Table 6.9-1. Palisades was operational during the first and second quarters of 1988 only; the Plant was off-line for the third and fourth quarters due to refueling maintenance outages. There are no remaining 1988 laboratory sample analyses pending completion for inclusion into this report. The results of all environ-mental samples collected are evaluated as follows: A.. Air iodine and particulates, TLDs (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 10.4.

The data was compared against two criterium: the first criteria is the statistical difference which indicates that sample results from near sites are greater than those from control sites, but that the difference is not 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, sediment, fish and other aquatic biota samples were evaluated using data means comparisons against an appropriate control location (if available) and Palisades Tech-nical Specification limits. II. Reportable Event A. During 1988, the second set of semi-annual fish and other aquatic biota samples required to be collected in Technical Specification Table 4.11-1 could not be obtained at Palisades. Sample collection scheduling delays and setbacks between CPCo Environ-mental Services Department and the Palisades Radiological Services Department, when Lake Michigan entered into a Fall weather pattern (inclement weather, high winds and rough water) made collecting fish and aquatic biota impossible. The missing samples included: 2 fish samples - at le.ast 2 species of fish from the vicinity of the discharge. 1 fish sample - at least 1 specie of fish from an area not influenced by the discharge (either the North or South boundary locations). IC0489-0088A-HP01 1

1 aquatic biota sample (optional) - algae collected from shoreline rocks near discharge. All required sediment samples were collected in late December. B. In order to prevent a reoccurrence of the above situation, the following measures have been instituted:

1.

Establishment of a more flexible sample collection arrange-ment between the CPCo Corporate Environmental Services Department and Palisades Radiological Services Department; including "back-up" sample collection capability in cases of schedule changes or setbacks.

2.

Selected Palisades Radiological Services personnel added to Michigan Department of Natural Resources Sample Collectors Permit (authorized user personnel) issued to Consumers Power Company.

3.

The purchase of additional sample collection equipment to be maintained at Palisades for use in fish and aquatic biota collection activities. III. Discussion and Interpretation of Results A. Air Sample 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 I-131 activity reported above minimum detectable levels. A total of 624 air samples were collected and analyzed during 1988, however 29 sample results were deleted from statistical evaluation as follows: Twelve (12) sample results-did not meet Iodine-131 LLD require-ments due to either low air sample volume flows caused by mal-functioning air meters/pumps, or a loss of power to the sampling unit. The affected sampling stations and dates were: 3-HS on 7/3/88, 11/3/88 and 11/20/88; 4-JS on 8/7/88 and 12/18/88; 8-SP on 9/11/88; 7-SD on 11/13/88 and 11/20/88; 11-KZ on 3/17/88; and 12-DG on 2/18/88, 7/6/88 and 7/27/88. Seventeen (17) sample results did not meet_ air particulate gross beta LLD requirements due to either low air sample volume flows caused by malfunctioning air meters/pumps; a loss of power to the sampling unit; or an improperly seated air particulate filter in the air sample holder. The affected sampling stations and dates were: 1-ST on 4/10/88; 3-HS on 11/13/88, 11/20/88 and 12/26/88; 4-JS on 4/17/88, 8/7/88, and 12/18/88; 8-SP on 9/11/88; 7-SD on 11/13/88 and 11/20/88; 10-GR on 3/31/88 and 9/15/88; 11-KZ on 3/17/88, 4/21/88, 8/25/88 and 9/1/88; and 12-DG on 2/18/88. IC0489-0088A-HP01 2

The deleted samples constitute 1.92% of the Iodine-131 and 2.72% of the air particulate gross beta results not used in the statis-tical evaluations. This is a much higher sample data loss than for 1987 (0.48% for both Iodine-131 and gross beta results in 1987). Technical Specification sensitivities were met on all samples other than noted. Air iodine/particulate samples are collected on a weekly basis from 12 air sampling locations. Air is metered into the sampling unit at a continuous 1 cfm flow rate through a Gelman 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 effluent releases and site-specific meteorology. B. Lake Water A total of 24 individual monthly lake water composite samples were collected from two (2) locations during 1988. Lake water samples from the Palisades Lake-in (intake) and the South Haven Municipal Water System (raw water) 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 Palisades Lake-in and the South Haven Municipal (control) locations. The lake water results were also evaluated against the Palisades Technical Specification reporting limits. Gross beta and tritium analyses are required for all lake water samples. Both the Palisades Lake-in and South Haven Municipal (raw water) samples were below the required LLDs. A monthly gross alpha analysis was also performed on the Palisades Lake-in samples for comparison data against the lake-out (discharge) sample results. Results of the gross alpha analyses were below LLD. No Palisades Technical Specification reporting limits were exceeded. Both the Palisades Lake-in and South Haven Municipal (raw water) water samples are collected daily for composite into a monthly sample. A one (1) one-gallon quantity of Palisades Lake-in sample and two (2) one-gallon quantities of South Haven Municipal (raw water) samples are sent to Teledyne Isotopes for analysis. No treatment of the water samples with preservative is required. C. Drinking Water A total of 24 individual monthly drinking water composite samples were collected from the South Haven Municipal Water System during 1988. The samples are obtained from 2 collection points: lake IC0489-0088A-HP01 3

water intake (raw) and treated water. Samples are collected daily for composite into a monthly sample. Evaluation of the drinking water analytical results was based on a data means comparison between the South Haven Municipal lake water intake (raw) and treated water as well as with the Palisades Technical Specification reporting limits. The lake water intake serves as a control. The evaluated data was also trend plotted against the Palisades Lake-in gross beta results. Both the South Haven Municipal lake water intake and treated drinking water samples require gross beta analyses. A tritium analysis is required for the treated water only. For all samples, the analytical results were below LLD for gross beta and tritium. No special or supplemental analyses were required during 1988 and nor were any Palisades ~echnical Specification reporting limits exceeded. A two-gallon quantity of each sample is sent to Teledyne Isotopes for analysis. No treatment of the water ~amples with a preserva-tive is required. D. Well Water A total of 36 individual monthly well water samples were collec.ted from 3 locations during 1988. The Palisades site well is collected daily and composited into a monthly sample; the State Park and Covert Township Park well water samples are collected as monthly grab samples only. Evaluation of the monthly well water analytical results was based on a data means comparison between the Palisades site and the State Park/Covert Township Park samples as well as with the Palisades Technical Specification reporting limits. The State Park/Covert Township Park wells serve as controls. Tritium and gross beta analyses are required for the well water samples. Analytical results were below LLD for tritium at all locations; and below LLD for gross beta at the Palisades site and Covert Township Park wells. The State Park well was reported as having 5 monthly samples slightly above the 4.0 pCi/L gross beta LLD, however the 1988 mean value for the State Park well gross beta results was only 3.8 pCi/L. The State Park well samples have traditionally had a higher gross beta level than any of the other sampled wells. This has been evaluated in previous reports as not being from power plant origin. No special or supplemental analyses were necessary during 1988 nor were any Palisades Technical Specification reporting limits exceeded. IC0489-0088A-HP01 4

Two (2) one*-gallon quant1t1es of sample per offsite well and one (1) one-gallon quantity from the on-site well are sent to Teledyne Isotopes for analysis. No treatment of the water samples with a preservative is necessary. E. Milk A total of 48 individual monthly milk samples were collected from 4 different dairy farms (locations 26-FC, 27-KK, 28-GH and 29-WS) during 1988. The milk samples are obtained as grab samples (from dairy milk holding tanks). With the exception of Sr-90, all isotopic results listed in Table 10.4-2 were less than LLD. Evaluation of the Sr-90 activity between indicator (26-FC, 27-KK, and 28-GH) and control (29-WS) locations did not exceed the SAS statistical difference level. The control location (29-WS) had the highest annual Sr-90 mean for 1988. No special or supplemental analyses were required, nor were any Palisades Technical Specification reporting limits exceeded. Milk samples are required monthly (usually.collected the 1st week of the month) from each designated location (4 total). Two one-gallon quantities of raw milk (grab sample) are obtained per sample location in order to meet analytical requirements. Each sample quantity is treated w.i th a sodium bi sulfite (40 grams per gallon) preservative prior to being sent to Teledyne Isotopes. F. TLDs - Ganuna Dose There was a total of 286 monthly, 95 collected and analyzed during 1988. (ST-18 and ST-14), one (1) quarterly (ST-24) TLDs reported missing. quarterly and 24 annual TLDs There were two (2) monthly (ST-18) and one (1) annual The following is detailed for the missing TLDs:

1.

The May monthly TLD at location ST-18 (site boundary, SE) and the September monthly TLD at location ST-14 (site boundary, ENE) were discovered*missing during the routine monthly TLD collection/changeout cycles. Search of the area revealed negative results for the TLDs. Replacements of monthly's are not available.

2.

The second quarter TLD at location ST-18 (site boundary, SE) was discovered missing at the same time as the May monthly TLD. Due to the timing of the loss, a spare replacement TLD was not posted, nor could the second quarter data be pro-rated from the monthly TLDs. IC0~89-0088A-HP01' 5

3.

The annual TLD at location ST-24 (Emergency Siren 22, 4.5 mi E) was discovered missing on 10/5/88 during the routine monthly TLD collection/change-out cycle. Search of the area for the TLD revealed negative results. On 10/6/88, a spare TLD (SP-2) was posted at location ST-24. Because the spare annual TLD was only in the field for 87 days, total exposure result was pro-rated for 365 days. The pro-rated data was included into the 1988 TLD evaluations. In addition to the above, the following TLD evaluations should also be noted:

4.

The annual TLD at ST-12 (Dowagiac, 30 mi SSE) was inadver-tently collected with the September monthly and third quarter TLDs on 10/5/88. When the error was realized, sufficient time had elapsed that could contribute to faulty results if the TLD was re-posted. A spare TLD (annual) was posted for a 4th quarter "back-up" and the collected ST-12 annual TLD was pro-rated for 365 days. The pro-rated data was included into the 1988 TLD evaluations.

5.

IC0489-0088A-HP01 The August ST-05 TLD (P. Rood, 3.5 mi ESE) had a monthly readout of 9.8 mR. This is slightly over twice the 1988 annual monthy average of 4.5 mR for that location. No specific reason(s) for the elevated result could be determined, as Palisades had been off-line since August 8 for refueling and maintenance. The August result also appears not to be an incorrect data typo nor an improperly annealed TLD badge. Both the ST-05 third quarter and annual TLDs were within their normal ranges as well. The ST-17 (ESE site perimeter) August monthly TLD did not reflect any readout increase. The August ST-05 TLD was evaluated with the other monthly results, but it is considered to be an aberrant data point. The Palisades gamma assessment program consists of 24 locations: 1 directly on site, 9 inner ring (site boundary), 10 o~ter ring (1.0 to 5.5 miles out, 3 control (30 to 55 miles out) and 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) TLDs; 4.3 mR for the outer ring (1.0 to 5.5 miles out) TLDs; and 4.2 mR for the control TLD locations. The lead cave control TLD recorded an average of 2.1 mR per month. This is consistent with actual effluent releases. The one (1) on-site TLD location (1-ST) serves as an individual reference TLD, however it was evaluated along with the inner ring (site boundary) TLDs in the SAS program. 6

G. Crops The monthly and quarterly SAS statistical TLD data evalua-tions were accomplished by comparing the inner ring TLDs (site boundary locations ST-01 and ST 13-21) and the outer ring TLDs (locations ST-02 thru ST-09, ST-23 and ST-24) against the control TLD locations (ST-10 through ST-12). The annual TLD data evaluation was done by direct comparison of data points only. No monthly or quarterly statistical differences were exceeded. In comparing the inner ring TLDs to the control TLDs; ST-11 (Kalamazoo, 35 mi SE) had the greatest monthly, quarterly and annual data means as an indicator location. When the same comparison was made between the outer ring and control location TLDs; ST-06 (R. Bus, 4.25 mi NE) had the greatest monthly TLD data means for any indicator location. Location ST-02 (Tower Hill, 5.5 mi S) had the greatest quarterly and annual data means. Background and intransit gamma exposure levels were accounted for and subtracted from the TLD data prior to statistical evaluation. Environmental gamma doses are measured monthly, quarterly and annually by placement of 3 appropriately identified TLD badges per designated location. Each Teledyne TLD badge contains a 4-zone CaS04 wafer (the wafer also includes an additional backup/reserve readout zone). Sensitivity for the multi-zone TLDs are 0.5 milliRem with a linear response of 0.1 milliRem to 1000 Rem. The collection of food crops and vegetation samples (wheri available and in season) is a requirement of the Palisades Radio-logical Environmental Monitoring Program. Two principal area crops: apples and blueberries, are regularly collected as specified in Technical Specifications. While there are no pre-_ designated/special locations where food crops are collected, samples are generally obtained from the same areas where the air monitoring stations are located within the E, SE or SSE sectors. The collection of food crops assists in verifying stack effluent deposition patterns. During 1988, 13 crop samples were collected from four locations (5 samples from 4-JS, 3.5 mi SE; 4 samples from 5-PR, 3.5 mi ESE; 2 samples from 6-RB, 4.3 mi NE; and 2 samples from 2-TH, 5.5 mi S). Evaluation of sample analytical results was direct. There was no control location used. IC0489-0088A-HP01 7

Of the isotopic analyses listed on Table HP 10.4-2, only the gross beta and Sr-90 resulted in any specific activity (slightly above LLD). All other analyses were less than LLD. The crop samples at location 2-TH had the greatest individual means for gross beta; and the crop samples at both 2-TH and 5-PR had the greatest individual means for Sr-90 activity. No Palisades Technical Specification action or reporting levels were exceeded nor were any special/supplemental analyses required during 1988. Food crop samples are required to be collected when available and in season. When collected, approximately 1 Kg of sample is placed in a sealable plastic bag for shipment to Teledyne Isotopes. No special treatment of the samples with a preservative is necessary. H. Sediment A total of 11 individual sediment samples were collected from 5 locations during 1988. Six (6) sediment samples are obtained from Palisades (discharge, t mi South boundary, t mi North boundary and South Haven Beach locations) and five (5) samples from the Ludington Control Station (North and South Jetty)

  • Evaluation of the sediment analytical results was based on a data means comparison between the.Palisades and Ludington control samples as well as the Palisades Technical Specification reporting limits.

The individual Palisades 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 location(s), then that location is identified on Table HP 10.4-2. Of the isotopic analyses listed on Table Hp 10.4-2, Sr-89 and the other gamma (non-indicative/non-parameter isotopes) category were less than LLD. All other analyses resulted in trace amounts of activity present. The Palisades site locations reported a slightly greater gross beta activity level, although the discharge location had the highest mean individual sample gross beta results. For the Sr-90 isotopic results, the discharge and Ludington Control locations reported an equal mean activity level. It should be noted that two (2) of the Ludington Control samples (collected 5/27/88) and three (3) of the Palisades locations (South Haven beach, discharge and t mile North boundary; all collected 12/29/88) had slightly elevated Sr-90 LLDs due to the analyzing of too small a sample size by the contractor laboratory. The elevated LLDs were evaluated as positive results. No Pali-sades Technical Specification action or reporting levels were exceeded, nor were any special/supplemental analyses required during 1988. IC0489-0088A-HP01 8

Sediment samples are collected semi-annually from each designated locations. A one (1) liter quantity grab sample usually is obtained off-shore. No treatment of the samples with a preserva-tive is necessary prior to shipment to Teledyne Isotopes. I. Aquatic Biota - Algae Although not specified for collection in the Palisades Radio-logical Environmental Technical Specifications, algae was available in sufficient sample quantities during 1988 to warrant collection and analysis. The algae was attached to the rock structure implacements designed to prevent high water beach erosion at Palisades. A total of three (3) individual algae samples were collected from two different locations during 1988. Normally, four (4) samples would be collected; however this could not be accomplished as explained under item II. of this report. Two (2) of the collected samples were from the Ludington Control (North and South Jetty) Station with the other sample (1) collected near the Palisades discharge. Biota samples are collected semi-annually. Evaluation of the algae analytical results was based on a data means comparison between the Palisades and Ludington Control samples as well as with the Palisades Technical Specification reporting limits. Of the isotopic analyses listed in Table HP lQ.4-2, only the gross beta and Sr-89/90 analyses resulted in any specific activity. As with the sediment samples, one (1) of the Ludington Control samples (collected S/27/88) and the one (1) Palisades Discharge sample had slightly elevated Sr-89/90 LLDs due to the analyzing of too small a sample size by the contractor laboratory. The elevated LLDs were evaluated as positive results. No Palisades Technical Specification reporting limits were exceeded. One (1) liter quant1t1es of algae are prepared for shipment to Teledyne.Isotopes by treating each sample with 10 ml of a 10% formaldehyde solution for preservation. J. Fish A total of 8 individual fish samples were collected from four (4) locations during 1988. Three (3) fish samples were obtained from Palisades (discharge, t mile South boundary) and five (5) samples from the Ludington Control Station (North and South Jetty). Normally, at least two (2) additional fish samples would have been collected at Palisades; however this could not be accomplished as explained under item II.of this report. Fish are collected semi-annually. IC0489-0088A-HP01 9

Evaluation of the fish analytical results was based on a data means comparison between the Palisades and Ludington Control samples as well as with the Palisades Technical Specification reporting limits. As with the sediment samples, the individual Palisades 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 10.4-2. Of the isotopic analyses listed on Table HP 10.4-2, only Sr-90 and gross beta were greater than LLD. Many Palisades (site) sample locations reported equal or less levels of activity than the control location. No Palisades Technical Specification reporting limits were exceeded nor were any special analyses requested for 1988. As a minimum, at least two (2) different fish species (ie, forage, .sport fish, etc) per designated 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. K. Broad Leaf Vegetation No broad leaf vegetation samples were collected from the surrounding Palisades environs during 1988. The collection of broad leaf vegetation samples serves as a backup and/or alterna-tive 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. L. Gaseous and Liquid Radwaste Effluent Composite Samples Although not a direct reporting component in the Palisades Annual Radiological 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 basis for determining isotopic dispersion and deposition patterns within the surrounding environs of Palisades. All isotopic LLD are compared to Palisades Technical Specification reporting levels. During 1988, the September monthly LLDs for Sr-89 and Sr-90 were elevated. This was a result of the contractor laboratory analyzing too small a sample size. All other isotopic LLDs were met. The elevated results were evaluated as positive values. There were no elevated LLD results for the gaseous effluent composite samples. IC0489-0088A-HP01 10

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 effluent composite sample results are based on.analyzing four (4) or five (5) weekly stack gas filters. No special sample treatment with a preservative is required prior to laboratory analysis. IV. Assessment of Palisadess Operational Environmental Impact In reviewing the 1988 Palisades' radiological environmental monitoring data and comparing it to previous operational and pre-operational data, all trending parameters continue to indicate that the operation of Palisades 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 and fish also appears to have had no lasting results. Evidence of an overall environ-mental isotopic buildup (attributable to Plant effluents) remains negligible as well. In most instances, sample analytical results were below previously established environmental background levels. IC0489-0088A-HP01 11

MJ0587-0028A-HP01 Medium Air Lake Drinking Water Well Water M1lk TLD Erops Sediment Aquatic Biota Fish Descril!tion Continuous at Approx 1 CFM 1 Gallon COlllPOS i te 1 Gallon Colllposite 1 Gallon Grab 2 Gallon Grab Continuous Grab Grab Grab Grab Palisades Nuclear Plant Annual Radiological Environmental Operating Report January I to December 31, 1988 Table HP 10.4-1 Sampling and Analysis Su11111ary Location All: Stations 1-ST thru 12-DG Intake South Haven Site, TP, SP WS, FC, GH, KK All: Stations ST-01 thru ST-24 JS, PR, RB, TH Discharge, f mi N & S Site Boundary South Haven Beach, Ludington Control Number of Samples Collected 624 12 24 36 48 286 95 23 13 '11 Disc~arge, f *i South 3 Boundary, Ludington Control Discharge, f mi N & S B Site Boundary, Ludington Control Tyl!e of Analysis Gross Beta, 1-131 Gross Beta, Gross Alpha, Tritium Gross Beta, Tritium Gross Beta, Tritium 1-131, Sr-89 and Sr-90, Cs-137, Other Ganna Ga111111a Gross Beta, Sr-89 and Sr-90 Cs-137, Other Ga1111a Gross Beta, Sr-89 and Sr-90 Cs-137, Other Ga11111a Gross Beta, Sr-B9, Sr-90 Other Ganna Gross Beta,.Sr-89, Sr-90 Other Ga11111a Frequency of Analysis Weekly Monthly Monthly Monthly Monthly Monthly Quarterly Annual In Season Semi-Annual As requested Semi-Annual I-' f\\)

Analyses Evaluated Over ' Medium or Total NUllber of Pathwal:'. Sa!!!!led Anall:'.ses Perfol'l!ed Unit of Measure11ent Air (pCi/111') 1-131 612/624 Gross Beta 607/624 Lake Water (pCi/L) Gross Alpha 12/12 Gross Beta 24/24 Tritiu*(c) 24/24 Drinking Water Gross Beta 24/24 (pCi/L) Tritium(h) 12/12 Well Water Gross Beta 36/36 (pCi/L)(g) Tritium .36/36 Milk (pCi/L) 1-131 48/48 Sr-89 48/48 Sr-90 48/48 Cs-137 48/48 Other G1111111a 48/48 Palisades Nuclear Plant Annual Radiological Environmental Operating Report January 1 to December 31, 1988 Lower Limit of Detection(a} LLD 0.07 0.01 1.0 4.0 500.0 4.0 500.0 4.0 500.0 1.0 5.0 1.0 18.0 15.0 Table HP 10.4-2 Sample Data Su111Dary All Indicator Locations Mean(b) Range(b) 460/468 LLD 458/468 0.04 (0.003-0.06) 12/12 LLD 12/12 LLD 12/12 LLD 24/24 LLD 12/12 LLD 12/12 1.5 (0.8-2.3) 12/12 LLD 36/36 LLD 36/36 LLD 36/36 3.2 (2.0-4.4) 36/36 LLD 36/36 LLD Location With Greatest Annual Mean(g} Name Mean(b) Distance and Direction Range(b) LLD H. Soderberg (5 *i S) LLD Lake Intake and South Haven Raw lake water 0.03 (0.03-0.05) locations are equal (5.5 mi NNE) LLD South Haven Raw & South Haven Treated Lakewater Locations are equal (5.5 111i NNE) LLD State Park (1 mi N) LLO LLD LLD 29-WS (W. Shine, 10 11i E) LLD LLD 3.8 (1.6-6.2) 3.6 (0.5-5.8) All Control Locations Mean(b) Range(b) Nonroutine Heasure11ents (cl 152/156 LLD None 149/156 0.02 None N/A 12/12 12/12 (0.004-0.05) None LLD LLD Not required Not required 24/24 2.9 (1.0-6.2) 24/24 LLD 12/12 LLD 12/12 LLD 12/12 3.6 (0. 5-5.8) 12/12 LLD 12/12 LLD None None None None None None None None None None None (a) Nominal Lower Limit of Detection (LLD) as defined in MASL-300 (Rev 0/73), pages D-06-01, 02 and 03; Palisades Technical {b) Mean and range based upon detectable measurements and/or vendor laboratory LLD's. Specifications Table 4.11-3 and vendor analytical capabilities. (c) Nonroutine reported measurements are defined in the Palisades Technical Specifications, Section 6.9.3.2 (d) Supplemental sample when milk is unavailable. (e) Monthly TLD results are normalized for 30 days net: Quarterly TLD results are nonnallzed for g} days net. (g) See reporting results for greatest 111ean sampling location. HI0587-002BA-HP01 (f) See TLD evaluations in report narrative. (h) Tritium analysis required for South Haven treated only.

Palisades Nuclear Plant* Annual Radiological Environ11ental Operating Report January 1 to Dece*ber 31, 1988 Table HP 10.4-Z Sa11ple Data Su111Dary Analyses Evaluated Over Lower Limit All All Medium or Total Nu11ber of of Indicator Location With Greatest Control Nonroutine Pathwa_)'. Sa11j!led Ana l_)'.ses Performed Detection{ a} Locations Annual Mean{g} Locations Measurements {cl TLD (ga11111a llR) TLD (1110nthl;i)(e) 154/284 10.0 118/248 3.7 ST-11 (Kalamazoo, 35 mi SSE) 4.7 36/36 4.Z None Inner Ring (1.Z-6.6) (3.0-5.9) (1.7-7.4) (Site Boundary) TLD (quarterly)(e) 51/9l(f) 10.0 '!9/79 10.4 ST-11 (Kalamazoo, 35 Iii SSE) 12.2 12/12 11.1 None (6.3-14.9) (9.7-13.9) (8.0-13.9) TLD (annual) 13/23 10.0 10/20 45.5 ST-11 (Ka 1 amazoo, 35 mi SSE) 53.7 3/3 46.8 None (39.4-50.6) (41.0-53. 7) TLD (ganna 111R) TLD (110nthly)(e) 156/284(f) 10.0 120/248 4.3 ST-06 (R.Bus, 4.25 mi NE) 5.1 36/36 4.2 None Outer Ring (0.9-9.8) (2.9-6.2) (1.7-7.4) TLD (quarterly)(e) 52/gl(f) 10.0 40/79 12.6 ST-02 (Tower Hi 11, 5.5 mi S) 15.2 12/12 11.1 See TLD Narrative (7.9-17.2) (11. 7-17.2) (8.0-13.9) TLD (annual) 13/23(f) 10.0 10/20 54.6 ST-02 (Tower Hi 11, 5.5 mi S) . 66.5 3/3 46.8 See TLD Narrative (45.8-66.5) (41.0-53.7) Crops (pCi/g wet) Gross Beta 13/13 1.0 13/13 1.5 2-TH (Tower Hill, 5.5 mi S) 1.7 (0.8-2.1). (J.3-2.1) Sr-89 13/13 0.025 13/13 LLD LLD None None Sr-90 13/13 0.005 13/13 LLD 5-PR (P.Rood, 3.5 11i ESE) and 0.004 None None 2-TH (Tower Hi 11, 5. 5 *i S) and (<0.002-0.006) 1-131 13/13 0.06 13/13 LLD LLD None None Other Gamna 13/13 Various 13/13 LLD LLD None None 0.5-0.18 Sedi*ent (pCi/g Gross Beta 11/11 1.0 6/6 8.9 Discharge 9.8 5/5 7.4 None dry) (6.1-12.0) (7.5-12.0) (6.6-9.1) Sr-89 11/11 0.025 6/6 LLD LLD 5/5 LLD None Sr-90 11/11 0.005 6/6 0.006 Ludington Control (120 mi N) and 0.006 5/5 0.006 See Sediment narrative ( <0.004-0. 007)Di scharge (0.004-0.013) (<0.004-0.013) Cs-137 11/11 0.18 6/6 LLD LLD 5/5 LLD None Other Gaona 11/ll Various 6/6 LLD LLD 5/5 LLD None 0.05-0.15 (a) Nolllinal Lower Limit of Detection (LLD) as defined in MASL-300 (Rev 0/73), pages D-06-01, OZ and 03; Palisades Technical Specifications Table 4.11-3 and vendor analytical capabilities. (b) Mean and range based upon detectable 11easurements and/or vendor laboratory LLD's. (c) Nonroutine reported *easure11ents are defined in the Palisades Technical Specifications, Section 6.9.3.2 (d) Supplemental sample when milk is unavailable. (e) Monthly TLD results are normalized for 30 days net; Quarterly TLD results are normalized for 91 days net. (g) See reporting results for greatest mean sa111Pling location. MI0587-0028A-HP01 (f) See TLD evaluations in report narrative. (h) Tritiu~ analysis required for South Haven treated only.

Analyses Evaluated Over Medium or Total Nullber of Pathwa.l! Sam!!led Anal.l!ses Perfonned Algae (pCi/g wet) Gross Beta 3/3 Sr-B9 3/3 Sr-90 3/3 Other Ga11111a 3/3 fish (pCi/g wet) Gross Beta 8/8 Sr-B9 8/8 Sr-go 8/8 Other Ga11111a B/8 Broadleaf(d) Gross Beta Vegetat Ion (pCi /g I-131 wet) Sr-89 Sr-90 Cs-137 Other Ga11111a Palisades Nuclear Plant. Annual Radiological Environmental Operating Report January 1 to December 31, 1988 Table HP 10.4-2 Sample Data Su11111ary Lower L1mit All of Indicator Location With Greatest Detection{ a) Locations Annual Mean{g) 1.0 1/1 3.0 Discharge 3.0 0.025 1/1 0.07 Discharge 0.07 0.005 1/1 0.048 Discharge 0.04B Various 1/1 LLD LLD 0.10-0.26 1.0 3/3 1.4 Ludington Control 1.8 (1.4-1.5) (120 111i N) (1.3-2.4) 0.025 3/3 LLD LLD 0.005 3/3 0.009 Ludington Control 0.014 (<0.005-0.016) (120 mi N) (0.002-0.020) various 3/3 LLD LLD 0.1-0.26 1.0 No Samples Collected 0.06 0.025 0.005 0.08 All Control Nonrout1ne Locations Measurements {cl 2/2 1.7 None (1. 7) 2/2 0.06 See Aquatic Biota (0.019-0.10) Narrative 2/2 0.014 See Aquatic Biota (0.005-0.023) Narrative 2/2 LLD None 5/5 1.8 None (1.3-2.4) 5/5 LLD None 5/5 0.014 None (0.002-0.020) 5/5 LLD None No Sa1111>les Collected None (a) NDlllnal Lower Limit of Detection (LLD) as defined In MASL-300 (Rev 0/73), pages D-06-01, 02 and 03; Palisades Technical Specifications Table 4.11-3 and vendor analytical capabilities. (b) Mean and range based upon detectable 111easurements and/or vendor laboratory LLD's. (c) Nonrout1ne reported llH!asure*ents are defined in the Palisades Technical Specifications, Section 6.g.3.2 (d) Supple*ental sa*ple when 111ilk ls unavailable. (e) Monthly TLD results are normalized for 30 days net; Quarterly TLD results are normalized for 91 days net. (g) See reporting results for greatest *ean sampling location. MI0587-0028A-HP01 {f) See TLD evaluations In report narrative. (h) Tritium analysis required for South Haven treated only. 1--1 VI

Palisades Nuclear Plant Annual Radiological Enviro1111ental Operating Report January l to December 31, 1988 Medium Air (pCI/*') Lake Water (pC1/L) Drinking Water (pC1/L) Well Water (pC1/L) Milk (pC1/L) nD (Ganna-mR)(4) Inner Ring (site boundary) nD ( Ganna-mR )( 4) Outer Ring (l) Sa11Ples collected monthly when in season. (Z) Two samples per location (collected semiannually) Table HP 10.4-3 High, Low and Mean Reporting Results for Greatest Mean Sampling Location Type of Analysis Gross Beta 1-131 Gross Alpha Gross Beta Tritium Gross Beta Tritium(3) Gross Beta Tritium 1-131 Sr-B9 Sr-90 Cs-137 Other Ga11111a. nD (Monthly) TLD (Quarterly) TLD (Annual) nD (Monthly) no (Quarterly) nD (Annual) Location H.Soderberg (5 mi S) LLD LLD Lake Intake and South Haven Raw Lake Water LLD South Haven Raw & Treated (5.5 mi NNE) LLD State Park (l mi N) LLD LLD LLD 29-WS (W. Shine,10 mi E) LLD LLD ST-ll (Kalamazoo, 35 mi SSE) ST-ll (Kalamazoo, 35 mi SSE) ST-ll (Kalamazoo, 35 mi SSE) ST-06 (R.Bus, 4.Z5 mi NE) ST-OZ (Tower Hill, 5.5 mi S) ST-OZ (Tower Hill, 5.5 mi S) (3) Tritium analysis required for South Haven treated only. (4) Monthly nD results are non11alized for 30 days net; Quarterly no results are normalized for 91 days net. (5) Supplemental sample when milk is unavailable. Ml 05B7-00ZBA-HPOl !!!i!! 0.05 6.2 5.8 5.9 13.9 6.2 17.z Low 0.03 1.6 0.5 3.0 9.7 2.9 ll.7 Mean 0.03 <0.07 <l.O <4.0 <500.00 <4.0 <500.00 3.8 <500.00 <1.0 <5.0 3.6 <18.0 <15.0 4.7 1Z.Z 53.7 5.1 15.2 66.5 0\\

Palisades Nuclear Plant Annual Radiological Environmental Operating Report January 1 to December 31, 1988 Table HP 10.4-3 High, low and Mean Report1ng Results for Greatest Mean Sampling location Med1u* T~~e of Anal~sis Location Crops (pCi/g w~t)(l) Gross Beta 2-TH (Tower Hill, 5.5 mi S) Sr-8g LLO Sr-90 2-TH (Tower Hill, 5.5 mi S) and 5-PR (P.Rood, 3.5 mi ESE) Cs-137 LLD 1-131 LLD Other Ga11111a LLD Sediment (pCi/g dry)(2) Gross Beta Discharge Sr-B9 LLD Sr-90 Ludington Control ( 120 mi N) and Discharge Cs-137 LLD Other Ga11111a LLD Algae (pCi/g wet) Gross Beta Discharge Sr-89

  • Discharge sr-90 Discharge Other Ganna LLD Fish (pCi/g wet)

Gross Beta Ludington Control (120 mi N) Sr-89 LLD Sr-90 Ludington Control (.120 mi N) Other Ganna LLD Broad Leaf Veg Gross Beta No samples collected (pCl/9 wet) 1-131 (5) Sr-B9 Sr-90 Other Ga11111a (1) Suples collected monthly wh~n in season. (2) Two samples per location (collected semiannually) (3) Tritiu* analysis on required for South Haven treated only. (4) Monthly TLD results are nor11alized for 30 days net; Quarterly TLD results are nor.a 1 !zed for 91 days net. (5) Supplemental sample when milk is unavailable. MI05B7 -002BA-HP01 !!.19!! 2.1 0.006 12.0 0.013 2.4 0.020 Low 1.3 <0.002 7.5* 0.004 1.3 0.002 Mean 1.7 <0.025 0.004 <0.08 <0.06 <0.05 9.8 <0.025 0.006 <0.18 . <0.05 3.0 0.07 0.048 <0.10 1.8 <0.025 0.014 <0.10

A. B.

c.

D. E. Enclosures Palisades 1988 Land Use Census Health Physics Procedure 10.10: Palisades Radiological Environmental Program Sample Collection and Shipment Procedure (with sample locations, maps, etc). Palisades 1988 (Annual) Radiological Environmental Monitoring Program Data as provided by Teledyne Isotopes Midwest Laboratory, Northbrook, Ill. Teledyne Isotopes Midwest Laboratory EPA Interlaboratory Comparison Program Results Data Graphs

l.

Palisades Air Particulate (gross beta) 1988 Trending and Palisades Air Particulate (gross beta) 1983-1988 Operational Comparison Graphs.

2.

Palisades Lake Water/Drinking Water (gross beta) 1988 Trending and Palisades Operational Comparison Graphs (gross beta); 1968-1969 (pre-op) and 1983-1988 *

3.

Palisades Well Water (gross beta) 1988 Trending and Palisades Operational Comparison Graphs; 1968-1969 (pre-op) and 1983-1988.

4.

Palisades Milk (Sr-90) 1988 Trending and Palisades Operational Comparison Graphs (Sr-90 and Cs-137); 1968-1969 (pre-op) and 1983-1988.

5.

Palisades TLD (ganuna) 1988 Trending and Palisades Operational Comparison Graphs (monthly, quarterly and annual); 1968-1969 (pre-op monthly) and 1983-1988.

6.

Palisades Sediment (gross beta) 1988 Trending and Palisades Operational Comparison Graphs; 1983-1988.

7.

Palisades Fish (gross beta) 1988 Trending and Palisades Operational Comparison Graphs (gross beta, Sr-90 and Cs-137); 1968-1969 (pre-op) and 1983-1988. IC0489-0088A-HP01 l8

ENCLOSURE A PALISADES 1988 LAND USE CENSUS OC0589-0127-NL04

To From Date Subject cc WLBeckman (Y7,.,,, HAMoor~ September 29, 1988 PALISADES PLANT-1988 LAND USE CENSUS TPNeal DCC: 950/72*10*03/LP CONSUMERS POWER COMPANY Internal Correspondence MAM88*009 The attached tables and map are the results of the Palisades Land Use Census conducted on September 9, 1988. Table 10.11-1 references the distance from Palisades to the nearest residence, garden (greater than 500 square feet), beef/dairy cattle, and goat per meteorological sector. Table 10.11-2 identi-fies the locations of the nearest residence and garden; and of all beef/dairy cattle and goats within a five (5) mile radius of Palisades per meteorological sector. Table 10.11-3 lists the critical receptor locations used in calcula-tion of the offsite doses by the GASPAR computer program. An accompanying map* illustrates Table 10.11-2. Prior to conducting the Palisades 1988 Land Use Census, both the Van Buren County Agricultural Extension Off ice and Consumers Power Company Southern Region - District Manager's Office (Kalamazoo) were contacted September 8, 1988 as required in Procedure HP 10.11. There were no significant differences between the 1987 and 1988 Land Use Census. If you have any questions, please contact me. Reviewed and Authorized ~~--~~~~ ....... *~~~~~~~~~/~D-~-~-~-~-{f<_-~~-- TPNeal, RMC Administrator Date IC0988-0193A-HP01

l 1988 PALISADES LAND USE CENSUS TABLE 10.ll-l Distance to the nearest residence, garden, dairy/beef cattle and goat ln each sector. SECTOR RESIDENCE GARDEN BEEF CATTLE DAIRY COW GOAT N >5 mi >5 mi >5 mi >5 mi >5 mi NNE 1.6 mi 3.8 mi >5 mi >5 mi >5 mi NE 1.8 mi 1.8 mi >5 mi >5 mi >5 m1 ENE

1. 3 mi 2.9 mi 2.5 m1 4.0 mi 3.8 mi E

1.0 mi 2.9 mi 3.5 m1 >5 mi >5 m1 ESE 1.0 mi 2.9 m1 3.1 m1 >5 mi >5 mi SE .9 mi 1.1 m1 3.8 m1 4.3 m1 >5 m1 SSE .75 m1 1.8 m1 >5 m1 >5 mi >5 mi s .5 m1 i.5 mi >5 m1 >5 mi >5 m1 SSW .75 mi 1.5 mi >5 mi >5 mi >5 mi IC0988-0193A-HP01

Sector NNE Ruggles Road NNE 11th Avenue NE Blue Star Hwy ENE 24th Avenue,

  • dead end ENE CR 380 (20th Ave)

ENE M-140 ENE 72nd Street ENE 72nd Street E 17th Street dead end E 26th Avenue E 72nd Street 1988 PALISADES LAND USE CENSUS TABLE 10.11-2 Verification of Items Location Description L. Kern-State Park Manager. A. Olson-11th Avenue (We't side of road). L. Swetay, Route 3, Box 133, South Haven-(East side of hwy). Trailer-West _24th Avenue, dead end at sand dune. J. Moscov-7345 CR 380, i mile East of M-140 and CR 380 intersection (South side of CR 380). Robinson, 18800 M-140, Covert (West side of road). Cecil Hodge, 16971 72nd St, 3/8 mile South of 16th Ave and 72nd St intersection (West side of 72nd St.). Harlett, 19487 72nd St, i mile South of 72nd St and CR 380 intersection (West side of 72nd St.) 17th St. - 1 mile North of 17th St and 29th Ave intersection. Brunts - 73536 26th Avenue, t mile East of 26th Avenue and M-140 intersection (South side of 26th Avenue). C Mims, 26200 72nd St, intersection of 72nd St and 26th Ave (Northwest corner of intersection). Item Residence Garden Residence Garden Residence Garden Cattle Cattle Goats Residence Garden Cattle IC0988-0193A-HP01 2 Number/Comment 1 1 1 1 1 1 3-beef 2-Dai ry *cow 7-Beef 2 1 1 2-Beef

E CR 378 (68th Avenue) ESE 7750 Street ESE 28th Avenue ESE 30th Avenue ESE 69th Street SE 7750 Street SE 7750 Street SE 34th Avenue SE 36th Avenue SSE 29th Avenue 1988 PALISADES LAND USE CENSUS TABLE 10.11-2 (Cont'd) R. Rouse, 67872 CR 378, t mile North of CR 378 and 30th Ave intersection (just outside of 5 mile limit zone). O. Ashley - Northwest corner of 7750th St and 28th Ave intersection. Waite, 76729 28th Ave i mile East of 28th Ave and M-140 intersection (South side of 28th Ave). Newell, t mile East of M-140 and 30th Ave intersection. Dairy Farm, 69th Street, t mile North of 69th Street and 34th Avenue intersection (approximately t mile outside of 5 mile limit zone). Lloyd, 28160 7750th St - t mile South of 7750 St and 28th Ave intersection (West side of 7750th St). Carl Dunson,. 30602 7750th St t mile South of 7750th St and 28th Ave intersection (West side of 7750th St). L. Burrows - t mile East of 34th Ave and H-140 inter-section (South side of 34th Ave). G. Miller, Route 1, Box 20, Covert - t mile West of 36th Ave and 72nd St intersection (South side of 36th St). L. Burrows - Route 1, Box 167, Covert - Southwest corner of 29th Ave and Blue Star Hwy intersection. Cattle Residence Garden Cattle Cattle Residence Garden Cattle Cattle Residence IC0988-0193A-HP01 3 25-Beef 1 1 1-Beef 15-Dairy Cows 10-Beef 1 1 15-Beef 1-Dairy Cow 4-Beef 1

SSE 32nd Avenue SSE CR 376 s 29th Avenue s 32nd Avenue SSW 29th Avenue dead end SSW 32nd Avenue 1988 PALISADES LAND USE CENSUS TABLE 10.11-2 (Cont'd) Howard, 77731 32nd-Avenue, Covert (South side on 32nd Avenue). Marshall - Southwest corner of CR 376 and M-140 inter-section (owner of cattle is J. Donald leasing Marshall property - at edge of 5 mile limit zone). Residence - Palisades Park; 3/4 mile West of 29th Ave. and Blue Star Hwy intersection (North side of 29th Ave). Northwest corner of 32nd Ave and Blue St~r Hwy. R. James - 29th Ave, dead end, Palisades Park. Dead end of dirt road, t mile West from 32nd Ave and Blue Star Hwy intersection

  • Garden Cattle Residence Garden Residence Garden IC0988-0193A-HP01 4

1 8-Beef 1 1 1 1

Sector SSE s ENE ENE ENE Note: Distance (Miles) 0.48 o.so 2.50 4.00 -- 3.80 1988 PALISADES LAND USE CENSUS TABLE 10.11-3 Critical Receptor Items Location/Description Site Boundary Residence, Palisades Park; 3/4 mile West of 29th Avenue and Blue Star intersection. Robinson, 18800 M-140, Covert (West side of road). Cecil Hodge, 16971 72nd Street, 3/8 mile South of 16th Avenue and 72nd Street intersection (West side of 72nd Street). Harlett, 19487 72nd Street, t mile South of 72nd Street and CR 380 intersection. Item N/A Residence/ Garden Beef Cattle Dairy Cow Goat 5

  • X/Q ( sec/m 3 ).

1.43E-06 l.OOE-06 1.0SE-07 5.29E-08

5. 85E-08
  • Based on Palisades 5-year composite meteorological data, 1978-1982.

IC0988-0l93A-HP01

residence A. garden beef cattle t dairy COWS goats

OC0589-0127-NL04 ENCLOSURE B HEALTH PHYSICS PROCEDURE 10.10 PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT PROCEDURE

PALISADES NUCLEAR Pt.ANT HEALTH PHYSICS PROCEDURE Proc Yo HP 10.10 Revi1ion 0 Page i TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT Table of Contents l.O PURPOSE Q 0 2.0 3.0 4.0 5.0 5.l 5.2 5.3

5.4 REFERENCES

PREREQUISITES PRECAUTIONS AND LIMITATIONS 9 e o PROCEDURE e e e e e e 0 e e e e e e e e 0 e e G e e e e REMP AIR SAMPLE COLLECTION

  • 0..........

REMP I.AXE (DRililCING) WATER SAMPLE COLLECTION - SOUTH HAVEN, MICHIGAN REMP WELL WATER SAMPLE COLLECTION........... REMP HILK SAMPLE COLLECTION 0 5.5 REMP AQUATIC BIOTA COLLECTION 0 ***** -o **** 5.6 REMP SEDIMENT SAMPLE COLLECTION Q 5.7 REMP FOOD PRODUCT SAMPLE COLLECTION.......... 5.8 REMP TLD SAMPLE COLLECTION * * * *

  • 6.0 ACCEPTANCE CRITERIA 0

7.0 RECORDS AND ATTACHMENTS.. 7.l RECORDS e 0 0 7.2 ATTACHMENTS 0 0 ATTACHMENTS Attachment l, "Palisades Environmental Sample Collection Schedule", "Palisades Sampling Locations", "Sample Identification", "Sample Packaging and Shipping", "Palisades Sample Collection Forms" hpl285-0ll2g-91-154 l l l l 2 2 3 4 4 5 7 7 8 9 9 9 9

PALISADES NUCLEAR PLANT HEALTH PHYSICS PROCEDURE Proc Ho HP 10.lO Revision 0 Page l of 9 TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT l.O PURPOSE 1.1 To provide methodology for collection of environmental samples in support of the Radiological Environmental Monitoring Program (REMP).

2.0 REFERENCES

2.1 Palisades Technical Specifications, Table 4.l-3(6), Section 4.ll and Table 4.ll-l and 6.9.3.2 2.2 Reg Guide 4.15(7) 2.3 10 CFR 50, Appendi% I 2.4 Nuclear Operations Department Procedure HOS, "Radiological. Environmental Monitoring" 2.5 Palisades Administrative Procedure 7.08, "Radiological Environmental Program Administrative Controls" 2.6 Radiological Environmental Monitoring Sample Shipping Manual, Tel.edyne 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 Palisades/RSD HP, 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 Palisades Technical Specifications to verify compliance to all requirements. 4.3 Deviations from the required sampling schedule shall be documented in the Annual Radiological Environmental Operating Report. 4.4 Every effort shall be made to complete corrective action on malfunc-tioning sampling equipment prior to the end of the ne%t 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. 4.6 Samples shall be collected, prepared and shipped for analysis in a timely manner to preserve integrity. Other specific handling precautions for sample media are indicated in Section 5 as required~ hpl285-0ll2a-9l-l54

PALISADES NUCLEAR PLANT HEALTH PHYSICS PROCEDURE Proc No HP 10.lO Revision 0 Page 2 of 9 TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT 5.0 PROCEDURE NOTE: Collect samples using the following methodology in accordance with schedule and location data described in Attachments 1 and 2. 5.1 REMP AIR SAMPLE COLLECTION 5.1.l Precautions s.1.2 5.1.3

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 find the cause and repair. If this cannot be done, replace appli-cable component and document on air sample collection data sheet.

c.

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

d.

Airflow meters will be changed out prior to the expiration of calibration dates. Replacement air meters are available from plant RSD Environmental contact.

e. If air leakage is observed requiring the replacement of an airflow meter, notify the Palisades RSD Radiological Environmental contact within 24 hours of changeout.

Document on air sample collection data sheet. Prerequisites

a.

Glass fiber air filters

b.

Absorbent cartridges for iodine sampling

c. Glassine envelopes
d.

REMP Air Sample Data Sheet (containing installation data)

e.

Replacement air sample meters (as required) Weekly at each sample location perform the following:

a.

Open protective cover on air sampler and record the integrated airflow meter readings on the sample data sheet under "Removed" column. Turn machine off. hpl285-0ll2a-91-154

PALISADES NUCLEAR PLANT HEALTH PHYSICS PROCEDURE Proc No HP 10.10 Revision 0 Page 3 of 9 TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROCRAM SAMPLE COLLECTION AND SHIPMENT NOTE: If airflow meter must be replaced, record the data required in 5.l.3.a as initial reading~ for the upcoming week's collection and note the change under "Remarks" on the current sample data sheet. Record installed and removed airflow meter readings in the columns provided. Record installed and removed readings of replacement airflow meter under "Remarks." NOTE: 5.2 s.2.1 5.2.2

b.

Detach filter holder from sample unit and take to enclosed vehicle.

c.

Remove and replace filters while inside vehicle. Center the filter properly to prevent leakage.

d.

Label glassine or plastic envelope as per Attachment 3 and place particulate filter in envelope.

e.

Identify carbon fil'ter as per Attachment 3.

f.

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

g.

Turn machine on. Place hand over filter inlet to form a seal. If no noticeable filter vacuum (suction) is felt or if vacuum pump motor does not labor, then significant filter bypass leakage may ba occurring. Repeat step f and/or replace filter holder if required.

h.

Close cover and proceed to the next station.

i. Record all pertinent information, date and sign data sheet.

J* Be sure to transcribe the removed airflow meter readings taken in Step 5.l.3.a to the installed readings columns on the sample data sheet to be used for the upcoming week's air sample collection. R.EMP LAKE (DRINKING) WATER SAMPLE COLLECTION-SOUTH HAVEN, MICHIGAN Prerequisites

a.

Four clean one-gallon polyethylene containers (labeled as per )

b.

REMP Miscellaneous Data Sheet Monthly perform the following sample collection:

a.

Leave four containers with the Plant Superintendent at the South Haven Municipal Water Treatment Plant. hpl285-0ll2a-9l-l54

PALISADES NUCLEAR PLANT HEALTH PHYSICS PROCEDURE Proc Mo HP 10.10 Revision 0 Page 4 of 9 TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT NOTE: 5.3 5.3.l 5.3.2 NOTE: 5.4 5.4.l New water sample containers should always be left at the South Haven water treatment plant upon pickup of end-of-month composite samples.

b.

Instruct the Plant Superintendent to add approximately 300 mL per day of raw water to container labeled "RAW" and approximately 300 mL per day of treated water to container labeled "TREATED."

c.

Return at end of month to collect containers. verification that Step 5.2.2.b was carried out. deviations in "Remarks" column of data sheet. Obtain verbal Note any

d.

Record location, sample types (raw and treated) on sample data sheet. Enter "Finish" in "Remarks" column. Sign and date data sheet. REMP WELL WATER SAMPLE COLLECTION Prereguisites

a.

Six clean one-gallon polyethylene containers

b.

REMP Miscellaneous Data Sheet Monthly perform the following sample collection:

a.

Turn on water supply (or begin pumping water) and allow water to run for approximately one minute to purge the lines.

b.

Fill two clean one-gallon polyethylene containers with well water from each sample location. During the winter months the State and Township Park wells may be out of service. When this occurs, note the unavailability of the water samples and document on sample data sheet.

c.

Label containers per Attachment 2.

d.

Record on data sheet location, type, date, quantity and under "Remarks" any pertinent information. Sign form in space provided. REMP HII.IC SAMPLE COLLECTION Precautions

a.

Milk samples are required to be sent to the laboratory as soon as possible because of the short half-life of I-131. Any undue delay may cause analytical sensitivity requirements of the Technical Specifications to be altered. hpl285-0ll2a-91-154

PALISADES NUCLEAR Pt.ANT HEALTH PHYSICS PROCEDURE Proc No HP 10.10 Revision 0 Page 5 of 9 TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT 5.4.2 5.4.3 NOTE: s.s NOTE:

b. Obtain best available replacement sample for any missing milk sample(s).

Identify new sample location(s) and notify Palisades RSD Radiological Environmental contact within 24 hours.

c.

If milk samples are unavailable, then samples of three different kinds of broad leaf vegetation grown nearest to Palisades in each of two different offsite locations of the highest predicted annual average ground level D/Q (SE or SSE sectors near site), and one sample of each kind of similar broad leaf vegetation grown 15-30 km distant from Palisades in the least prevalent wind direction (SSW or S sectors) may be*used as replacement samples. The new sample locations shall be identified and the REMP procedures revised within 30 days to reflect sampling changes. Prerequisites

a.

Two clean polyethylene one-gallon containers for each sample location

b.

Eight pre-measured packets of sodium bisulf ite *preservative (one packet per gallon)

c.

REMP Miscellaneous Data Sheet Monthly at each sample location perform the following:

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

Two clean, empty.polyethylene one-gallon containers may be left with milk supplier for the next month's milk samples when picking up current month's samples. If problems are encountered in obtaining a sufficient quantity of milk sample, notify the Palisades RSD Radio-logical 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, quantity and under "Remarks" indicate any pertinent information. Sign form in space provided. REMP AQUATIC BIOTA COLLECTION Collection to be coordinated between Radiological Services Department RMC Section and the Environmental Services Department

  • hpl285-0112a-91-154

PALISADES NUCLEAR PLANT HEALTH PHYSICS PROCEDURE Proc No HP 10.10 Revision o Page 6 of 9 TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT 5.5.l Precautions 5.5.2 5.5.3

a.

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

b.

If logistical problems prevent use of a boat to set gill nets from the lake side of Palisades, then the nets can be set offshore from the site boundary (by wading). Notify security prior to using offshore wading method for beach access. Prerequisites

a.

Boat

b.

Gill nets (of varying size mesh)

c. Plastic one-liter wide-mouth bottles
d.

REMP Miscellaneous Data Sheet

e.

10% formaldehyde solution

f.

~illet knives

g.

Black "magic" felt markers writing for sample identification on containers Semiannually samples shall be collected as follows:

a.

The fine mesh gill net is placed in the proximity of the discharge to collect small forage fish. One liter of fish flesh is to be collected for each species caught.

b.

The intermediate and larger mesh gill nets are set at the north/south site boundaries to capture larger forage fish and predator-type (game) fish. One liter of flesh is to be collected from each type of fish species caught.

c.

Label all containers as per Attachment 3.

d.

Record on data sheet location, type, date, quantity and under "Remarks" indicate any pertinent information. Sign form in space provided. hpl285-0ll2a-91-154

PALISADES NUCLEAR PLANT HEALTH PHYSICS PROCEDURE Proc No HP lO.lO Revision O Page 7 of 9 TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT 5.6 REMP SEDIMENT SAMPLE COLLECTION 5.6.1 Prerequisites 5.6.2 5.7 5.7.1 5.7.2 NOTE:

a. One-liter wide-mouth plastic sample bottles
b.

Dredge or hand scoop

c.

Miscellaneous Data Sheet Semiannually at each sample location Palisades RSD/Environmental Ser-vices Departmental personnel shall collect sediment samples.

a.

Record on data sheet location, type, date, quantity and under "Remarks" indicate surf ace area sampled and depth at which sample was obtained. Sign form in space provided. REMP FOOD PRODUCT SAMPLE COLLECTION Prerequisites

a.

Sample containers

b.

Miscellaneous Data Sheet Monthly during the harvest season, food samples shall be collected as follows:

a.

Sample selections of the following crops shall be processed: Strawberries Blueberries Grapes Apples Peaches Pears Turnips Cauliflower Cabbage - outer leaves only Broccoli Collard greens As per Technical Specification Table 4.11-l, blueberries and apples must be collected. Other crop samples can be collected on availability.

b.

Approximately one kilogram (2.2 lb) of each sample type should be collected. Samples are not to be washed, shaked or cleaned.

c.

Samples should not be collected from a single source, but at random from the entire orchard or field.

d.

Label all containers as per Attachment 3

  • hpl285-0ll2a-91-154

PALISADES NUCLEAR PLANT HEALTH PHYSICS PROCEDURE Proc No HP lO.lO Revision 0 Page 8 of 9 TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT 5.8 5.8.1 5.8.2 NOTE: NOTE:

e.

Record on data sheet location, type, date, quantity and under "Remarks" note any unusual conditions. Sign form in space provided. REMP TLD SAMPLE COLLECTION Prereguisites

a.

TLDs

b.

TLD Data Sheet Monthly, quarterly and annually at each sample location perform the following: Monthly TLDs are to be changed each month; 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 shall be iuunediately 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 following:

l.

Search immediate area.

2.

If lost TLD is found, collect it and perform standard change out 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.

e.

Store collected field TLDs in lead cave along with control TLDs until ready for mailing to laboratory contractor. Mark "Do not x-ray" on TLD package. Transportation control TLDs are to be stored in a special lead shield provided by laboratory contractor.after the field TLDs are posted. Be certain that designated transportation control TLDs are included with the correct TLD package b~ing mailed to laboratory contractor. hpl285-0112a-91-154

PALISADES NUCLEAR Pt.ANT HEALTH PHYSICS PROCEDURE Proc No HP lO.lO Revision 0 Page 9 of 9 TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM SAMPLE COLLECTION AND SHIPMENT Also ensure that laboratory contractor's own TLD data sheet is completed and enclosed with shipment.

f.

Record date TLD~ are shipped and sign th~ data sheet. 5.9 Be sure that all collected samples are identified and labeled as per. 5.10 Complete the appropriate Sample Collection Data Sheet and distribute as follows: 5.11 NOTE: 5.12 5.13 6.0 7.0 7.1

7. l. l 7.1.2 7.2 White - Analytical Laboratory Yellow - not required Pink - Radiological Services Department Environmental Contact (Pali sades)

Cold -_Sample Collector Obtain best available replacement sample for any missing sample. Notify Palisades RSD Radiological Environmental contact with descrip-tion and location of the replacement sample. Obviously some samples are not replaceable (TLDs, air samples, etc); however, water, milk, crop samples, etc, should be. Document any missing samples or malfunctioning equipment on sample data collection sheets. Package and ship samples according to Attachment 4. ACCEPTANCE CRITERIA Pro'per completion of procedure RECORDS AND ATTACHMENTS RECORDS Distribution of Sample Collection Data Sheet as per Section 5.10. Sample data collection sheets shall be retained in the Uniform File Index under DCC number: PAL 950/24*03*10/L ATTACHMENTS, "Palisades Environmental Sample Collection Schedule", "Palisades Sample Locations", "Sample Identification", "Sample Packaging and Shipping", '"Palisades Sample Collection Forms" hpl285-0ll2a-91-154

Exposure Pathway and/or Sample Airborne: Particulates Iodines Waterborne: Lake Water Drinking Water Well Water Sediment ENVIRONMENTAL SAMPLE COLLECTION SCHEDULE Palisades Nuclear Plant Number of Samples and Locations* l - Onsite 8 - Within a 10 km Radius 3 - 25 to 89 km Distant Same as Particulates Sample Type Continuous at approximately l cfm (may be less due to dust loading) Same as particulates Proc No HP 10.10 Attachment l Revhion 0 Page l of 2 Collection Frequency Weekly Weekly 1 - Intake Daily composite Monthly l - Discharge to obtain a two-gal lon sample l - S Haven Municipal System - Raw 1 - S Haven Municipal System - Treated 1 - Site Two-gallon grab Monthly l - State Park sample l - Township Park l - Within 152.4 m of One-liter grab Semiannually discharge (500 ft) sample 1 - Between North boundary and State Park beach l - 0.8 km South of discharge l - 8.9 km North 1 - Ludington control (2 recoamended)

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

hpl285-0ll2b-9l-l54

Ezposure Pathway and/or Sample Ingestion: Milk Food Products Fish and Invertebrates Direct: TLD Number of Samples and Locations* 3 - From 5 to 13 km l - Control from 15 to 30 km l - Each of two principal fruit crops (blueberries and apples). 2 - Species in vicin-ity of plant dis-charge l - Ludington control l - On site 10 - Site boundary 9 - Within 12 km radius 3 - Control stations Sample Type Two-gallon grab sample Two-pound grab sample One-liter fish flesh Continuous Proc No HP 10.10 Attachment l Revision 0 Page 2 of 2 Collection Freguency Monthly At time of harvest In season or semiannually

Monthly, Quarterly and Annually
  • If samples are unavailable at the specified location, an attempt should be made to sampl~ at an alternate location (refer to 4.5).

hpl285-0ll2b-91-154

PALISADES SAMPLINt LOCATIONS AND MAPS QJ (JI i:: I QJ ""w -0 <ti <a 0 Q.......

I

"" u Station Code Location < w 1 ST Palisades Nuclear Plant x x 2 TH Tower Hill Farms x x Intersection of 48th Ave and 80th Street, Coloma, MI 5.5 Miles (8.9 Km) S 3 HS Herbert Soderberg x x 48th Ave, Covert, Michigan 5.5 Miles (8.9 Km) s 4* JS Jerry Sarno x x 36197 M-140 Covert, Michigan 3.5 Miles (5.6 Km) SE 5 PR Paul Rood x x 72723 County Road 378 Covert, Michigan 3.5 Miles (5.6 Km) ESE 6 RB Richard Bus x x 73rd Ave South Haven, Michigan 4.25 Miles (7.3 Km) NE 7 SD Sherman Dairy x x 72238 County Road 388 South Haven, Michigan 7 Miles (11.3 Km) NNE 7a SN35 Emergency Siren 35 4.75 Miles (7.7 Km) NNE 8 SP Van Buren State Park. x x 1 Mil:e ( 1.6 Km) N

  • TLD 22 is a control in lead cave at Location 4-JS.

hp0186-0348g-91-154 1 Samo e QJ QJ w w <ti <ti 3 3 QJ ...:s: ...:s: ca QJ ....J 3

c x

x x x x x Proc No HP 10.10 Revision l Page 1 of 6 w i:: QJ (JI e <ti

c.

..c:: w 0 -0 Q (JI 0 QJ ....J C,J en e... Cr.. a:i x* x x x x x x x x x x

PALISADES SAMPLIN~ LOCATIONS AND MAPS Q) en c: I Q) w.u "O <1' <1' 0 c......

l w u w

Station Code Location < l.J 9 TP Covert Township Park x x l.S Miles (2.4 Km) SSW 10 GR CPCO Region Office x x Grand Rapids, Michigan SS Miles (88.7 Km) NNE 11 KZ CPCO Region Off ice ' x x Kalamazoo, Michigan 3S Miles (S6.4 Km) SSE 12 DG Dowagiac, Michigan x x 30 Miles (48.4 Km) SSE 13-21 ST-Perimeter of Palisades 23 SN2S Emergency Siren 2S 3 Miles (4.8 Km) ENE 24 SN2l Emergency Siren 22 4.S Miles (6.4 Km) E 25 SH Sou.th Haven, Michigan 5.5 Miles (8.9 Km) NNE 26 FC Frank Crnkovich 12th Avenue South Haven, Michigan 1.5 Miles (12.1 Km) NE 27 KX Kenneth Kemp 70th Avenue South Haven, Michigan 8 Miles (12.9 Km) NE hp0186-0348g-91-154 s l amp e w w Q) Q) l.J l.J <1' <1' 3 3 Q) ~ ~ - <1' Q) ....l 3 x x x x x en Proc No HP 10.10 Revision 1 Page 2 of 6 l.J c: Q) e <1'

c.

~ 0 "O Q cn 0 w Q) ....l u en e-o ~ x x x x x j x x x

PALISADES SAMPLING LOCATIONS AND MAPS ~ Cll c I ~ "'u "1:1 t1S t1S 0 Cl....... ~

2

"' u

  • .-4....

Station Code Location <u 28 GH Glenn Hessey 65000 26t~ Ave Bangor, Michigan 6 Miles (9.7 Km) E 29 WS Wi 11 iam Shine 60364 M-43 West Bangor, Michigan 10 Miles (16.l Km) E 30 STN 1/2 Mile (0.8 Km) N of Discharge 31 STS l/2 Mile (8.0 Km) s of Discharge 32 LP Ludington Pumped Storage 120 Miles (193.2 Km) N hp0l86-0348g-91-154 s 1 amo e ~ ~ u u t1S t1S 3 3 ~ .!Ill .!Ill t1S ~ ..J 3 ~ x x Proc No HP 10.10 Revision 1 Page 3 of 6 u c ~ Cll E! t1S

c.....

..c: u 0 "O Q Cll 0 ~ ..J u en c--- c... cc I x x x x x x x

\\ \\ \\ \\ \\ \\ \\ \\.. \\ ~ \\ r '\\ ~ \\ ~ \\ hp0186-0348g-9l-l54 SITE ENVIRO~ENTAL TLD STATIONS Proc No HP 10.10 Revision l Page 4 of 6 I J( 1

hp0186-0348g-91-154 OFFSITE ENVIRONMENTAL TLD LOCATIONS AND SAMPLE COLLECTION POINTS Not Shown: (Control Lo'cations) Proc No HP 10. 10 Revision l Page 5 of 6 I Grand Rapids ( 55mi NNE) Kalamazoo (35mi SSE) Dovagiac (30mi SSE) Control TLD placed in lead cave at ~.locationro 'EZ!'~illia~ Sli1ne (WS-lOmi E)

hp0186-0348g-9l-154 LUDINGTON CONTROL LOCATION SAMPLING STATIONS Ludi:i~1on F-umped Sfaro9e Project t N Mll,.£S RESERVOIR Pree No HP 10.10 Revision l Page 6 of 6 z ' l J

SAMPLE IDENTIFICATION Proc No HP 10.10 Revision 0 Page l of 2 NOTE: Use waterproof pen. Do not place paper labels inside containers *.

1.

Each sample shall be clearly identified prior to packaging for shipment.

2.

The plant name shall be written on sample container using the following identification: 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 Samples: Air Particulates AP Air Iodine AI Well Water WW Lake Water LW Milk MK Drinking Water Raw OW-RAW Drinking Water Treated OW-TREATED

b.

Special Samples: Vegetation VE Fish FI Sediment SD Periphyton PE Crayfish CF Algae AL Shore Minnow SM hpl285-0112d-91-154

SAMPLE IDENTIFICATION Proc Vo HP lO.ll Revision 0 Page 2 of 2

4.

The date and location where sample was collected (as per Attachment 2) shall be written out on sample container prior to packaging.

5.

The sample container identification and data recQrded on the sample collection sheet must agree

  • hpl285-0ll2d-9l-154

SAMPLE PACKAGING AND SHIPMENT

1.

Samples shall be clearly labeled per Attachment 3. Proc No HP 10.10 Revision 0 Page 1 of 1

2.

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

3.

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

4.

Sufficient packing material (ie, crumpled newspaper) shall be used to avoid possible sample container damage during shipment.

5.

Air filters shall be pack.aged in glassine or plastic envelopes.

6.

For TLD shipments, make sure that Laboratory contractor's own TLD data sheet is enclosed with pack.age.

7.

Milk samples shall be shipped as soon as possible. Be sure to add one packet of sodium bisulfite (40 grams) as preservative to each gallon sample prior to shipping.

8.

Food products shall be shipped as soon as possible after collection.

9.

Fish and biota samples are to be shipped with a 10% formaldehyde solution added (preservative). Only 10 milliliters is required per sample. Samples should be shipped as soon as possible after processing.

10.

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

11.

Samples shall be sent to the following address: Teledyne Isotopes Midwest Laboratory Att: 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

  • hpl285-0112e-91-154

IST 2TH 3HS ,.JS SPR 6RB 7SD ISP 9TP I OGR 11 KZ 12DG PALISADES SAMPLE COLLECTION FORMS PALISADES PLAU Proc No HP 10.10 Revision 0 Page l of 3 FORM------ REVIS IOI ___ _ EllVIROMMEllTAL NOllTOR OPERABILITY CHECK

  • SAMPLE COLLECTION DATE METER FLOW TEST REPLACEMEIT METER QQC SERIAL SERIAL o.?:.

. GAS METER READ I llG 110. AS FOUllO AS LEFT 110. CALll.* SAMPLE -'C ""'C c(Q "'"' REMOVED INSTALLED REMOVED FLOW --- o-CAL.DUE ~i 3i TIME ( Ft3) (Ft3) DATE (SEC/Ft3)

  • NOTE: FOR STATIOIS WITH REPLACED METER. IF GAS METER TEST ANO REPAIR CARO (FORM 116) IS NOT INCLUDED WITH THIS FORM, MARK AS "110 CAL CARO".

hpl285-0ll2f-91-154 LEAK (CFM) FLOW LEAK ACCURACY VOL. CAL.DUE ( SEC/Ft3) (CFM)

  • DATE ACCEPTABU (FT3)

CCM4EllTS TEST PERFORMED BY:------- DATE:---- REVIEWED BY: DATE:-----

IAWl.I T-hpl285-0112f-91-l54 PALISADES SAMPLE COLLECTION FORMS Proc No HP lO.lQ Revision 0 Page 2 of 3 Ca*---------- Pl.MT '::',. :-1 s-c.~l~l-an_eou_1---::llM-:":"l-o=-109--=-1 ca--=-1 "'l:En~v-:1-ron_mn......,.t-a""I ~s-p I as OAT9 Tl.. AMOUNT IUlllAlllCI

PALISADES SAMPLE COLLECTION FORMS PALISAD~S MO..,Tltl Y ENVIRONMENTAL lLO ~EPORT ST Proc No HP 10.10 Attachment S Revision 0 Page 3 of 3 Ill T~* S1**~ *'

  • ---=...;..::_:: ~:~-F-H*-----T-1

--+-I -------1 1--~-----...;,;=-1-----"----+.---i.l-----;1-------------1 ,_.;..;ST-=.2*.;...._ ____ _E?_i_J ___ __;__ I *--+' ----

  • -~ST~;~~ ----=s*-~* :

---r-__ ~:!------+l"----------------1 ~l~7* ____ ___;S~~JS~'--~--,.~-\\~_.1 1 _________ ~~~~ mG S!. I ~~---- II I I _ST;5 ST _1 STI ST I ....J!!l' ____ s_T--!----+----~l-----+-------ij--------------------1 l 5~8 l ST1; I------+----+-----------------~ _:,~~~~~~--~----~:~;-:--1-;.'~~~~~~~~~~~-=-; __ -i.l-----1-----------------1 ST_1~--------~ST,__-l-------L..------+'----t:* ___ ---!---------------~

  • -=-: -=--~-=--=--=--=-:~""""T.__-_-++i-=--=--=--=-:-=--=--=--=--;-t-=--=--=--=-:1-=--=--=--=-:i-=--=--=--=--=--=--=--=--=--=--=--=--=--=--=--=--=-~

~:::!..;~..... ?~~~~~~~~::.!;.:"-'~~.... 1 ...... -_-_-_-:_..J,._!~~~~-=.,..;~~~~~:1~~~~~:1~-~~~~~~~~~~~~~~~~~~~~~~ ._J~T].,__ ___ _:.:.HS::_~l ______ ,_I ____

_ _ -i-----i-'-----------------~

--l~t------'~__.1 ______ :;,_ _____ ! ----~i-----1-----------------~ ._1!~~------~~=---+---!--'-----;'~---1,_*----+-------------------1 ___lll.O _______ ~G~R--+---~'---~-----------.1--------------------1 i I _iT.11~--------K~Z--~----....,.......----+---~---+------------------1 I I ,--+----+,--+,--------~ hpl285-0112f-91-154

ENCLOSURE C PALISADES 1988 ANNUAL RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM DATA AS PROVIDED BY TELEDYNE ISOTOPES MIDWEST LABORATORY OC0589-0127-NL04}}

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