AECM-86-0113, Station,1985 Annual Radiological Environ Operating Rept
| ML20203N490 | |
| Person / Time | |
|---|---|
| Site: | Grand Gulf  |
| Issue date: | 12/31/1985 |
| From: | Kingsley O MISSISSIPPI POWER & LIGHT CO. |
| To: | Grace J NRC OFFICE OF INSPECTION & ENFORCEMENT (IE REGION II) |
| References | |
| AECM-86-0113, AECM-86-113, NUDOCS 8605050449 | |
| Download: ML20203N490 (139) | |
Text
{{#Wiki_filter:_ _ ._. . __ _ _. _ . . 1 l 4 i a GRAND GULF NUCLEAR STATION i f 1985 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT ) 8605050449 851231 PDR ADOCK 05000416 R PDR J20AREOR850306
PREFACE The Annual Radiological Environmental Operating Report (AREOR) presents the data obtained through the' analyses of enviro-nmental samples collected for the Grand Gulf Nuclear Station (GGNS) Operational Radiological Environmental Surveillance Program l for the period January 1, 1985 through December 31, 1985. The AREOR fulfills the requirements of GGNS Technical Specifications
; 6.9.1.6 and 6.9.1.7.
The analytical contractor for GGNS in 1985 was Teledyne l Isotopes Midwest Laboratories, formerly Hazleton Environmental Sciences. Teledyne has been the analytical contractor since January 1, 1984. i 11 J20AREOR850306
TABLE OF CONTENTS i PAGE PREFACE..................................................... 11 LIST OF TABLES.............................................. vi LIST OF FIGURES............................................. vii SECTION TOPIC
1.0 INTRODUCTION
...................................... 1-1 1.1 Purpose and Design Criteria of the Radiological Environmental Surveillance Program...................................... 1-1 1.2 Dose Pathways Associated with GGNS........... 1-2 1.3 History of Operation and Present Status...... 1-3 2.0 RADIOLOGICAL ENVIRONMENTAL SURVEILLANCE PROGRAM... 2-1 2.1 Air Particulates and Radiciodine............. 2-1 2.2 Thermoluminescent Dosimetry (TLD)............ 2-2 3 2.3 Milk ....................................... 2-3 2.4 Water ....................................... 2-4 2.5 Vegetation................................... 2-5 2.6 Sediment ................................... 2-6 2.7 Fish ....................................... 2-7 2.8 Special Samples............................. 2-7 2.9 Annual Land Use Census....................... 2-7 3.0 ANALYTICAL PROCEDURES & COUNTING METHODS......... 3-1 3.1 Analytical Program & Methodology............ 3-1 3.2 Analytical Detection Limits and Count Rate Errors........................... 3-1 3.3 Air Particulates............................ 3-1 3.4 Radioiodine.................................. 3-2 34 5 Cistern Water............................... 3-2 J20AREOR850306 - 111
TABLE OF CONTENTS (cont'd) i i SECTION TOPIC PAGE 3.6 Surface Water................................ 3-3 3.7 Groundwater.................................. 3-3 3.8 M11k......................................... 3-3 3.9 Sediment ..................................... 3-4 3.10 Vegetation................................... 3-4 3.11 Fish and Meat................................. 3-4 3.12 Thermoluminescent Dosimeters (TLDs)........... 3-4 4.0 RESULTS AND DISCUSSION............................ 4-1 4.1 Air Particulates and Radioiodine............. 4-1 4.2 Ambient Radiation Levels (Gamma Dose By TLD).. 4-2 4.3 M11k......................................... 4-3 4.4 Water........................................ 4-3 4.5 Vegetation.................................... 4-5 4.6 Sediment...................................... 4-6 4.7 Fish......................................... 4-8 4.8 Special Samples.............................. 4-8 4.9 Land Use Census............................... 4-9 4.10 Exceptions to the Environmental Surveillance Program.......................... 4-10 4.10.1 TLDs............................... 4 5.0 RADIOLOGICAL ENVIRONMENTAL SURVEILLANCE PROGRAM
SUMMARY
........................................... 5-1 5.1 1985 Program Results Summary.................. 5-1 3 J20AREOR850306 - iv
TABLE OF CONTENTS (cont'd) SECTION TOPIC PAGE. 6.0 QUALITY CONTROL DATA.............................. 6-1 6.1 Crosscheck Program Results................... 6-1 1 7.0 1985 SAMPLING AND ANALYSIS RESULTS................ 7-1 7.1 Data for 1985................................ 7-1 J i I a i i 4 d J20AREOR850306 - y
-LIST OF TABLES TABLE NO. TITLE PAGE 2-1 Air Sample Collection Sites.................. 2-9 2-2 TLD Locations................................ 2-10 2-3 Milk and Water Sampling Locations............ 2-16 2-4 Vegetation, Fish and Sediment Sampling Locations.................................... 2-17 3-1 Analytical Program........................... 3-6 3-2 Maximum Values for the Lower Limits of Detection (LLD).............................. 3-7 2
4-1 Direct Radiation Dose........................ 4-11 4-2 1984/1985 Land Use Census Changes............ 4-12 4-3 1985 Land Use Census Data Sheets............. 4-14 5-1 Radiological Surveillance Program Summary (1985)....................................... 5-2 7-1 1985 Sampling and Analysis Results........... 7-2 7-2 AP&L Vegetation Analysis Results............. 7-58 f i i J20AREOR850306 - vi'
LIST OF FIGURES FIGURE NO. TITLE PAGE 2-1 Sample Collection Sites (5-mile map)........ 2-18 , 2-2 Sample Collection Sites (10-mile map)....... 2-19 2-3 Sample Collection Sites (General Area Map).......................... 2-20 4-1 1985 Census Nearest Residences............. 4-19 4-2 1985 Census Garden Locations............... 4-20
'J20AREOR850306 - vii
a..mo em~-.ommem~A_m.h s-.4.im- 4 -- - - - - .n .a. --4a SECTION
1.0 INTRODUCTION
1-1 J20AREOR850306 1
INTRODUCTION Grand Gulf Nuclear Station (GGNS), located in Claiborne County, Mississippi, consists of one operating boiling water reactor rated at 1250 MWe and a similar unit under construction. The site is on the east bank of the Mississippi River, approxi-4 mately 25 miles south-southwest of Vicksburg, Mississippi, and 37 miles north-northeast of Natchez, Mississippt. Grand Gulf 4 Military Park borders a portion of the north side of the property, and the community of Grand Gulf is approximately 1.5 miles to the north. The town of Port Gibson is approximately 6 miles southeast of the site. Two lakes, Hamilton Lake and Gin Lake, are located in the western portion of the site. 1.1 PURPOSE AND DESIGN CRITERIA 0F THE RADIOLOGICAL ENVIRONMENTAL SURVEILLANCE PROGRAM Grand Gulf Nuclear Station has been designed to keep radioactive releases as low as reasonably achievable. The quantities of radionuclides released to the environment due to the operation of GGNS are expected to be insignificant as a source of potential exposure. The purposes of the Radiological Environmental Surveillance Program are: o To measure radiation levels and their variations in envircamental media in the area surrounding the plant o To yield average values of radiation levels and concentrations of radioactive material in various media of the environment
, o To evaluate environmental procedures, equipment, and techniques J20AREOR850306 1
o To detect what effect, if any, operation of GGNS will have on the radiation levels and concentrations in the environment around GGNS.
.The design criteria for the Radiological Environmental Surveillance Program are:
o To analyze the important pathways for anticipated types and quantities of radionuclides released from the station into the surrounding environment o To consider the possibility of a buildup of long-lived radionuclides in the environment and identify physical and biological sites of accumulation that may contribute to human exposures o To consider the potential radiation exposure to important plant and animal life in the environment surrounding GGNS , o To correlate levels of radiation and radioactivity in the environment with radioactive releases from station operation. 1.2 DOSE PATHWAYS ASSOCIATED WITH GGNS The most significant environmental dose pathways from a nuclear power station are direct dose from gaseous effluent and thyroid dose due to the ingestion of milk. GGNS operations are expected to have little, if any, impact on these pathways due to the remote location of the station and the absence of milking animals within 5 miles. Also, since the first use of Mississippi River water as drinking water is more than 200 miles downstream of GGNS, the dose from this pathway is expected to be minimal. J20AREOR850306 2
1.3 HISTORY OF OPERATION AND PRESENT STATUS GGNS Unit I received a Low-Power Operating License on June 16, 1982. Fuel loading began on July 1, 1982 and was completed on August 6, 1982. Initial criticality was achieved on August 18, 1982. Low-power testing began on September 25, 1983 and was discontinued on November 8, 1983 with 995.3 hours of operation at less than 5 percent power recorded for Unit 1. Low-power testing was resumed on April 22, 1984 and ccmpleted shortly thereafter. The Full-Power Operating License was granted on August 31, 1984, and commercial operation began on July 1, 1985. The following list summarizes significant dates associated with the operation of Unit 1: o Low-Power Operating License June 16, 1982 o Initial Criticality August 18, 1982 o Began Low-Power Testing September 25, 1983 o Discontinued Low-Power Testing November 8, 1983 o Resumed Low-Power Testing April 22, 1984 o Full-Power Operating License August 31, 1984 o Startup After Full-Power License September 5, 1984 o First Synchronization October 20, 1984 o Commercial Operation July 1, 1985. J20AREOR850306 3
1 GGNS Unit 2 is in a construction phase and was approxi- ; f mately 33.8% complete as of December 31, 1985. The minimal Unit 2 construction activities occurring in 1985 were for the purpose of protecting the original investment. Preoperational Study The Preoperational Radiological Environmental ,
\
Surveillance Program was initiated in July 1978. It was continued until GGNS received its Low-Power Operating License for Unit 1 on June 16, 1982. The background data gathered [! during the Preoperational Program was included in the 1982 Annual Radiological Environmental Operating Report. 1982 Annual Radiological Environmental Operating Report (AREOR) GGNS Unit I received a Low-Power Operating License on June 16, 1982. During 1982 Unit 1 did not enter a power ascension mode. Therefore, the results of the Operational Environmental Surveillance Program from June 16, 1982 to December 31, 1982 are actually an extension of the preoperational program data. Thedatawaspresentedinl Tables 8 through 12 of the 1982 AREOR. , 1983 AREOR Unit 1 of GGNS saw 995.3 hours of low-power operation between September 25 and November 8, 1983. Based on the i results of the Radiological Environmental Surveillance Program, GGNS had no effect on the radiation levels in the environs surrounding the site. J20AREOR850306 4 -
1984 AREOR A comparison of the 1984 Radiological Environmental Surveillance Program results with those of previous years showed no changes. The 1984 radiation monitoring levels did j not exceed the background levels obtained in the f Preoperational Program. No harmful effects or evidence of irreversible damage were detected by 1984 Radiological i Environmental Surveillance Program monitoring activities. l, GGNS Technical Specifications were revised on August 29, ! i- 1984 to more accurately reflect the as-built plant and to i i i i provide greater agreement with standard nuclear power plant ' t F technical specifications. The revisions which affected the Radiological Environmental Surveillance Program are 3 summarized below: o Required air sampling locations are now based on t particulate deposition rates ir. stead of atmospheric dispersion rates. This added locations AS-6 and -8 and , ' deleted AS-4 and -9 from the 5 locations required by ' technical specifications. o Fish sampling requirements have been broadened to include any available commercial or recreational species. o An additional vegetation sampling site is now required :
; in Meteorological Sector R. '
i o Iodine analysis of vegetation samples is now required. i
'I J20AREOR850306 5 v --~ . , y ,_. - .,, _ - _ _ ~ , _ . - _ , , , - - - . - , , - , - , , , . .,.,-,,-.,s - ,
e%. .
~. . -. . - -
I
./
c o Land use census requirements were expanded to include determination of the nearest resident, milk animal and garden in each of the 16 meteorological sectors instead of just the nearest resident, garden and milk animal ' locations. , o TLD placement is no longer required in meteorological sectors which are inaccessible. Full implementation of the revised technical specification a requirements began in September 1984. 1985 AREOR
- The required operational testing of GGNS was completed during the first half of 1985. Commercial operation of GGNS 4
began on July 1, 1985. This was the first year that GGNS had substantial operational activity. Radiological environmental sample results for 1985 were ! carefully reviewed by Environmental Surveillance Program personnel for significant changes. Slight increases above back-ground levels were noted.in sediment sample results from the GGNS barge slip. This occurrence is discussed in Section 4.6. Other sample results were essentially at preoperational levels with no significant changes. Based on the review of 1985 sample results, Environmental Surveillance Program personnel concluded that the operation of GGNS had no adverse radiological impact on the surrounding environment. o , L r
+
J20AREOR850306 6
SECTION 2.0 RADIOLOGICAL ENVIRONMENTAL SURVEILLANCE PROGRAM
+o*
O J20AREOR850306 1
2.1 AIR PARTICULATES AND RADI0 IODINES The GGNS Environmental Surveillance Program utilizes eleven continuous air monitors to provide beta, gamma and radioiodine activity measurements in the airborne exposure pathway. The locations of these monitors range from 0 to 18 miles, as identified in Figures 2-1 through 2-3 and Table 2-1. Five of the air samplers are used to satisfy the requirements of GGNS Technical Specification 4.12.1. Placement of the five required monitors are as follows: o Three near the SITE BOUNDARY in areas of the highest D/Q values o One in a community that has the highest D/Q value (Port Gibson) o One in a control location (Vicksburg). The remaining six samplers are located in areas which will provide additional data for the Radiological Environmental Surveillance Program. The samplers are placed in weatherproof houses approximately one meter above the ground. A 2-inch glass fiber filter is located in the intake line of the vacuum pump with a 2 x l-inch charcoal cartridge located directly downstream. Flows are adjusted to approximately 1.25 cubic feet per minute. Filters and cartridges are changed weekly and analyzed for gross beta and radiciodine activity, respectively. In addition, the filters are composited quarterly and analyzed for gamma-emitting radionuclides. J20AREOR850306 1
2.2 THERM 0 LUMINESCENT DOSIMETRY (TLD) Ambient radiation in the environment surrounding GGNS is measured with 91 TLDs (lithium fluoride dosimeters, 1/8" x 1/8" x 0.035" chips, TLD-100, Harshaw Chemical Company). ,. Maps showing the location of the environmental TLDs are provided as Figures 2-1 through 2-3. Each dosimeter has five lithium fluoride chips sealed in a plastic protective holder. The holder is suspended approximately one meter above the ground at each location. The dosimeters are collected quarterly, with notations made concerning location, exposure period, and any abnormal conditions such as moisture and damage. The 91 TLD locations are defined in Table 2-2. The criteria used in selecting their locations are summarized below: o GGNS Technical Specification 4.12.1 requires 40 of the 91 TLDs to be positioned as outlined below: An inner ring of 16 stations in the general area of the site boundary with one TLD in each meteorological sector An outer ring of 16 stations in the 3 to 5 mile range with one TLD in each meteorological sector 8 TLDs located in special interest areas such as l population centers and residences or utilized as ~ controls, o Permanent TLD stations are established on the protected area fence surrounding Unit 1. This requires 24 of the 91 TLDs. I o The remaining 27 TLDs are located in areas ranging from l 0-15 miles away from the GGNS site. These TLDs are used to gather supplemental and supporting data for determining direct radiation dose. l J20AREOR850306 2
1
)
Recapping, the TLD locations may be categorized as follows: i No. of Locations o Technical Specifications requirement
- Inner Ring 16 Outer Ring 16 Population Centers & Controls 8 o Protected Area Fence 24 o Supplemental Data (0-15 miles) 27 Total 91 2.3 MILK Milk samples are collected in the vicinity of GGNS for the purpose of measuring radioactivity via the ingestion exposure pathway. GGNS Technical Specifications require semimonthly milk sampling at three indicator locations within eight kilometers of the site and one control location (15-30 kilometers distant) when animals are on pasture, monthly at other times.
No milk animals are available within eight kilometers of GGNS. A control sample is collected routinely from the Alcorn State University Dairy to establish background data. In previous years, milk samples have occasionally been collected from three area farmers (Figure 2-2, Table 2-3) outside the eight kilometer range. However, in 1985 milk samples were not available at these locations. Collected milk is divided and analyzed for Iodine-131 and gamma-emitting radionuclides. 9 J20AREOR850306 3
l l 2.4 WATER Water samples are collected in the vicinity of GGNS for the measurement of radioactivity in the waterborne exposure pathway. Samples are collected in clean, labelled 2.5-gallon containers. The containers are rinsed with the sample media prior to collection. Cistern water is sampled monthly at two locations, one near the site (Trimble Cistern) and the other at a control location (Willis Cistern) (Figure 2-1, Table 2-3). Cistern water is analyzed for gross beta, Iodine-131 and gamma-emitting radionuclides. In addition, a quarterly composite is analyzed for tritium. Groundwater is sampled at three locations. The locations fulfilling the Technical Specifications are the source nearest the site (Grand Gulf Military Park (GGMP) Well) and the control (Port Gibson City Well). The other location (Lake Bruin State Park) provides GGNS with additional data (Figures 2-1 and 2-2, Table 2-3). Ground-water is collected and analyzed quarterly for gamma-emitting radionuclides and tritium. Surface water samples from the Mississippi River are collected monthly at a point upstream and downstream of the plant discharge (Figure 2-4, Table 2-3). They are analyzed monthly for gamma-emitting radionuclides and a composite is analyzed quarterly for tritium. J20AREOR850306 4
l An additional surface water sample is taken from the GGNS Discharge' Basin. Samples are composited monthly from , samples taken at hourly intervals with an automatic sampler. This sample is analyzed for gamma-emitting radionuclides monthly and a composite analyzed quarterly for tritium. ! 2.5 VEGETATION Broadleaf vegetation samples are collected in the vicinity of GGNS for the purpose of measuring radioactivity
! via the ingestion exposure pathway. Three samples of i
broadleaf vegetation grown nearest each of two different
- offsite locations with the highest anticipated annual average ground-level D/Q are required when milk samples are not
] available within five kilometers of the site boundary. The i second offsite sampling location was not required until the GGNS Technical Specifications were revised on i August 29, 1984. ! Environmental Surveillance Program personnel meet this i requirement by maintaining two gardens inside the SITE BOUNDARY. These sampling locations (Figure 2-1, Table 2-4) i , provide a more conservative assessment of doses due to the potential ingestion of contaminated vegetation than would be provided by offsite sampling locations. Control samples of each of the similar types of onsite vegetation are also obtained 15-30 kilometers from the site. l A control vegetation sample location was established at Alcorn State University (Sector K, 17 km) in 1984. t i ! J20AREOR850306 5 i
. - _ , - - _ - ~ _ . _ - _ . , _ - . . - , - _ . - _ _
The preferred source'of broadleaf vegetation is green-leafy vegetables suitable for human consumption. If such vegetables are not available, samples of any vegetation with relatively broad-leaves on which airborne radioactive material might be deposited are sampled. The raw samples are then analyzed for gamma-emitting radionuclides and Iodine-131. 2.6 SEDIMENT Sediment samples are collected semiannually at the following locations (Figure 2-1, Table 2-4): o River shoreline where the plant effluent is discharged (Barge Slip) o Downstream of the barge slip in the vicinity of-the Hamilton Lake Outfall o Upstream from the influent of GGNS discharges (Upper Grand' Gulf Landing). The only sediment sample required by GGNS Technical Specifications is the downstream location. Sediment samples are collected in the shallow water near the shoreline from the top one-inch layer of sediment. Any foreign objects are discarded and the samples are placed in a-sample container with location and date noted. The samples are then analyzed for gamma-emitting radionuclides including Cesium-137. l J20AREOR850306 6
2.7 FISH Fish are collected semiannually from two locations. The control fish sample is collected in the Mississippi River about 1000 yards upstream from the GGNS barge slip. The indicator sample is collected approximately 6000 feet downstream from the barge slip. A minimum of 500 grams (wet weight) of eviscerated fish is collected from each location (Figure 2-1, Table 2-4) and analyzed for gamma-emitting radionuclides. 2.8 SPECIAL SAMPLES Special samples are occasionally taken from sampling media or locations which are not part of the routine Environmental Surveillance Program. Sample media may include sediment, water, milk, fish, meat and vegetation. Special samples are collected to provide supplementary data and to address areas of special interest. Deer meat is a special sample which is periodically obtained from deer harvested on or adjacent to the GGNS site. The meat is then analyzed for gamma-emitting radionuclides, particularly Iron-59 and Zinc-65. 2.9 ANNUAL LAND USE CENSUS As required by GGNS Technical Specification 3.12.2, Environmental Surveillance Program personnel conduct an Annual Land Use Census. The purpose of the census is to J20AREOR850306 7
identify changes in the uses of land in the unrestricted areas surrounding GGNS which would require modifications to the Radiological Environmental Surveillance Program or the Offsite Dose Calculation Manual (ODCM). The most important criteria during the census are to determine the location in each of the 16 meteorological sectors of the nearest: o Residence o Animal milked for human consumption o Garden of greater th'an 50 m2 (500ft2) producing broad-leaf vegetation.
. l l
J20AREOR850306 8
TABLE 2-1 AIR SAMPLE COLLECTION SITES AIR SAMPLE NUMBER LOCATION
*AS-1 PG Southeast of GGNS at the Port Gibson City Barn (Sector G Radius 5.5 miles)
AS-2 61N North Northeast of GGNS, on Hwy 61 south across from the Yokena Church (Sector B Radius 13 miles)
*AS-3 61 VA North Northeast of GGNS on Hwy 61 south at the Vicksburg Airport (Sector B Radius 18 miles)
AS-4 GJOE Southwest of GGNS, next to Glodjo property on Waterloo Road (Sector L Radius 0.9 miles) AS-5 TC South of GGNS behind old MP&L Training Center building. (Sector J Radius 0.4 miles)
*AS-6 RS Northeast of GGNS, south of Grand Gulf Road (Sector C Radius 0.5 miles) *AS-7 MT North of GGNS, located next to the Meteorological Tower (Sector A Radius 0.8 miles) *AS-8 WR East of GGNS, located at Maggie Jackson's trailer on Waterloo Road near the Eastern Site Boundary (Sector E Radius 0.5 miles)
AS-9 GGMP North of GGNS located in Grand Gulf Military Park (Sector A Radius 1.5 miles) AS-10 NLT West Northwest of GGNS, located at Newellton, Louisiana (Sector P Radius 12.5 miles) AS-ll STJ West Southwest of GGNS, located at St. Joseph, l Louisiana ! (Sector M Radius 13.0 miles)
*GGNS Technical Specification requirements J
J . J20AREOR850306 9
TABLE 2-2 TLD LOCATIONS TLD NO. LOCATION SECTOR MILE M-00 Maintained in Lead Shield During the Exposure Period
*M-01 REA Pole-East of Entry Gate at E 3.5 Lake Claiborne M-02 REA Pole Left of Windsor Ruins Entry Gate L 7.0 M-03 REA Pole-East Side Highway 61 P.G. H 7.0 Country Club Entrance M-04 MP&L Pole-Highway 547 North Side G 6.5 Between Twin Power Poles M-05 North of Highway 18 Approximately F 9.0 5 Miles East of U. S. Highway 61 M-06 REA Pole-East of Willows Beyond D 10.0 MMB Church, MS Highway 462 *M-07 Port Gibson City Barn, AS-1 G 5.5 M-08 West Side Big Black River South C 8.5 Entrance *M-09 Oak Tree Hanger-South Warner Tully D 3.5 Camp *M-10 Entrance Gate Grand Gulf Military Park R 1.5 M-11 Highway 61, 3 Miles North of Big Black C 10.5 River at Twin Tower M-12 Highway 61 at AS-2-61 North Yokena B 13.0 M-13 Highway 61 Letourneau Hill, West B 15.0 Side of Road *M-14 Highway 61 AS-3-61VA at Casket B 18.0 (CONTROL) Company M-15 Barge Slip (South Edge) P 1.5 *M-16 AS-7-MET Tower A 0.8 I
- Technical Specifications requirement J20AREOR850306 10 l
TABLE 2-2 (cont'd) TLD LOCATIONS TLD NO. LOCATION SECTOR MILE M-17 AS-6-RS Grand Gulf Road C 0.5
*M-18 Railroad Crossing Eastern Site Boundary F 0.5 M-19 Behind Burn Pit on Fence at Eastern E 0.5 Site Boundary M-20 Eastern Site Boundary Behind F 0.5 Hazardous Waste Storage Area M-21 AS-5-TC Training Center J 0.4 M-22 100 Yards South of RR Entrance G 0.5 on West Side M-23 50 Yards North of County Road / Heavy Q 0.5 Haul Road Intersection on Power Pole M-24 Upper Grand Gulf Landing R 2.2 *M-25 Hamilton Lake Boat Launch N 1.0 M-26 Hamilton Lake Outfall N 1.5 *M-27 South Point Site Boundary 200 Yards M 1.5 along Property Line *M-28 AS-4-GJOE, Glodj o Residence L 0.9 M-29 In sharp curve of Waterloo Road to K 1.5 Waterloo Plantation *M-30 Arnold Acres Trailer Park Entrance J 1.1 M-31 Rotating Duplicate M-32 Rotating Duplicate *M-33 Newellton, Louisiana Water Tower P 12.5
- Technical Specifications requirement J20AREOR850306 11 l
TABLE 2-2 (cont'd) l l TLD LOCATIONS TLD NO. LOCATION SECTOR MILE M-34 Levee at End of Country Road at R 8.0 Point Pleasant, Louisiana M-35 Mor Landing - Lake Yucatan Q 8.0
*M-36 Curve on 608, Point Nearest GGNS at P 5.0 Power Pole M-37 Winter Quarters Home N 8.0 *M-38 Lake Bruin State Park Second Pole M 9.5 *M-39 St. Joseph, Louisiana, Aux, Water M 13.0 Tank *M-40 International Paper Road, Approximately M 5.0 5 miles from Site *M-41 Heavy Haul Road-J Pipe on Concrete P 1.0 Block *M-42 Heavy Haul Road North Iron Gate Q 1.0 *M-43 Gin Lake Entrance R 1.2 *M-44 Truck Bypass on Grand Gulf Road C 0.5 *M-45 Visitor Center Gate East Side D 0.5 *M-46 Power Pole Across from Grand Gulf / E 1.0 Waterloo Roads Intersection *M-47 Bridge 0.6 Mile Past Rodney Road / L 5.2 Greenwood Road Intersection, North Side *M-48 Property Line Fence, 0.4 Mile on K 4.8 Greenwood Road on West Side *M-49 Fork in Weathers Road H 4.5 *M-50 Panola Hunting Club Entrance Sign B 5.5
'
- Technical Specifications requirement J20AREOR850306 12
I l l I , TABLE 2-2 (cont'd) TLD LOCATIONS TLD NO. LOCATION SECTOR MILE
*M-51 Power Pole, 0.5 Mile on Gravel Road C 4.8 to Big Black on West Side
*M-52 Power Pole, Waterloo Road Marked with K 1.0 White Paint
*M-53 Arnold Acres Property Fence, Past Old H 1.1 Trailer Park
*M-54 Bottom of Curve Past Arnold Acres G 1.0 s *M-55 Behind Bonner's Beauty Shop at MSBH D 5.0 Air Sampler
*M-56 Highway 61 South at "All Creatures G 5.0 Veterinary Hospital"
*M-57 Highway 61 North Behind the Welcome F 4.5 to Port Gibson Sign
*M-58 Big Bayou Pierre Bridge, Southeast End E 5.0
*M-59 Off Levee at Winter Quarters Hunting N 5.1 Camp M-60 Rotating Duplicate M-61 Protected Area Fence by Vehicle P Onsite i Entrance Gate M-62 Protected Area Fence, Northeast Corner N Onsite i
MP&L Parking Lot M-63 Protected Area Fence, Middle MP&L N Onsite Parking Lot M-64 Protected Area Fence, Southeast Corner M Onsite MP&L Parking Lot i; M-65 South Protected Area Fence Behind MP&L L Onsite Warehouse i
- Technical Specifications requirement 1
J20AREOR850306 13
TABLE 2-2 (cont'd) TLD LOCATIONS TLD NO. LOCATION SECTOR MILE M-66 South Protected Area Fence Across From K Onsite Cooling Tower M-67 South Protected Area Fence, East End J Onsite M-68 East Protected Area Fence Across From H Onsite Chlorination Tank M-69 East Protected Area Fence Near G Onsite Electric Bus M-70 North Fence Behind Turbine Building F Onsite M-71 133' Railway Bay C Onsite M-72 133' Railway Bay B Onsite M-73 Corner of Fence Outside Control P Onsite Building M-74 Midway of North Fence P Onsite M-75 Fence Corner in Front of A Onsite Maintenance Shop M-76 Southeast Corner SSW Basins A Onsite M-77 Protected Area Fence Beside R Onsite Maintenance Shop M-78 Outside Vault in Administration Building Q Onsite M-79 Middle of Wall in Central Records Q Onsite M-80 Wall in Central Records, Old Library Q Onsite Location M-81 Inside Administration Building, Q Onsite i 2nd Floor, Northeast Wall M-82 Tech Support Area Q Onsite
- Technical Specifications requirement ,
l 4 J20AREOR850306 14
TABLE 2-2 (cont'd) TLD LOCATIONS TLD NO. LOCATION SECTOR MILE M-83 Tech Support Secretary's Office Q Onsite M-84 Security Island P Onsite M-85 Rotating Duplicate
*M-86 Bechtel Gate North Site Boundary B 0.5 M-87 Intersection of Rodney Road & J 3.5 Transmission Line
*M-88 River Mile Marker 409.5 A 4.2
*M-89 Middle Ground Island R 4.4
*M-90 Across from Middle Ground Island Q 3.5
*M-91 Transmission Line by Pond J 4.5 1
l
- Technical Specifications requirement O
i J20AREOR850306 15
TABLE 2-3 MILK & WATER SAMPLING LOCATIONS MILK SAMPLES Alcorn State University
- Southwest of GGNS (Sector K, Radius 10.5 miles)
Rosco Johnson Farm Southeast of GGNS (Sector G, Radius 9 miles) Hazetta Warren Farm In Louisiana West Northwest of GGNS (Sector N, Radius 8.5 miles) Mack Bell Farm East of GGNS (Sector E, Radius 8.0
.iles)
CISTERN WATER Trimble Cistern
- East of GGNS at the Trimble Tenant House (Sector E, Radius 0.5 miles)
Willis Cistern
- The C. E. Willis house East Northeast of GGNS across from the Shiloh Baptist Church (Sector D, Radius 6 miles)
GROUNDWATER PGWELL* Port Gibson Well - Taken at Port Gibson City Water Lift Station (Sector G, Radius 5.0 miles) GGMPWELL* Grand Gulf Military Park - Taken from faucet at the Grand Gulf ! Military Park (Sector A, Radius 1.5 miles) Lake Bruin Taken from faucet at the bath house in Lake Bruin State Park, Louisiana (Sector M, Radius 9.5 miles) SURFACE WATER Upstream
- Approximately 4500 ft upstream of the GGNS barge slip to allow adequate mixing of the Mississippi
, and Big Black Rivers (Sector Q)
- Downstream
- Approximately 5000 ft downstream of GGNS barge slip, near Radial Well #1 (Sector N) ,
. Discharge Basin
- West of GGNS, 0.5 miles (Sector P)
- Technical Specifications requirement i
J20AREOR850306 16
TABLE 2-4 VEGETATION, FISH & SEDIMENT SAMPLING LOCATIONS VEGETATION ^ Broadleaf Vegetation
- South of GGNS Near the training center (Sector J, 0.4 miles)
Adjacent to Meteorological Tower (Sector R, 0.8 miles)
; Vegetation Control
- Alcorn State University (Sector K, 10.6 miles) j FISH SAMPLES Fish, Commercial or Downstream of the discharge point in
- Recreational the Mississippi River Important Species
- l Upstream of Discharge Point uninfluenced by Plant Operations i SEDIMENT SAMPLES 1
SED HAM
- Downstream of the GGNS outfall in
{ the vicinity of the boat landing ! near Hamilton Lake outlet { (Sector N) l SED BAR Barge Slip j (Sector Q) SED CONT Collected upstream from barge slip l at Upper Grand Gulf Landing
- (Sector R)
!
- Technical Specification requirement 1
i i J20AREOR850306 17
. -. .~ a. . 6.e .. a a ,.m 2e. _ , 4 a ,h.a __.__,=4 a . .e=w,.a m -
I T n i O.4 Cr4 _. _-- - - ~ ' ,
.. ~
' ,i , \ - , , .
! r 4 !! [ 3 >.,%i - q xu'b xs . + e / dk i!!!$$h 7y p Til D.o .S'$eq d l ~ l i
, i I
l;
~ M6 -{;& ?, % ';.')T' Jji
\, r'
~~' - ; \
, (j,,,,Q%% 3 'D l..! LR - -
,p ?
' 'rj s-p ,.
*x < 'i. ' , ,) *.
-) 's _T'-" ~
h% 3 ) l - ( j' N
.c. -
{* v{ 't ) , l
},.! ,
j a g- . Y. f x . l y) Q
,. I.y w N 3~ N ~s / ,
p
) , e s s
}
; x !
gy 7 m . .. m _e em c.s - 3 c'
~
8- ' l, a
,f [ O v
n
~
w.
+ /;gj t
~~
i sr' ' p-
,) }"
Q
. ,w_ ~
s, , . l N
; g N
i*.%$ i \ ! I
~~
y K"m .i - e ,o +0h
,! Jg((
! C/ 4[ f y y',, , ]
, q'
~/jv ff l ,
e 1 7 /# .. >u t. s 1 %_ . < %,a i
/
\f 4 5 \ 0
~
'W
~
s .,. g N , \ L % i t h
'tN 8
M l ,r ya v
'\f rg /
os,/ J N y - 2 l > (gf. 'D ,, _4 )
- i,
.\'c
)
\,
lI n 18 Q. ll l
} }. '
) pr -
A- ss - 7r.
/
n,
\
a\c/ . . ~'Lm 6 .- ( p i c > , ) -
- ) - e U. 9 '\ q - x ,
I~ Nn
~ j u'J 8 ?
n'4 . 3% -
-/
. a s
'~ ^ . c y ~.
f % J - n yh ,,/ %
- a.m s
u
/ n >
i/'J 'lr r e i a 2 7,, 3.3 N / ',j s7 / ?h
- I
, \
- *. ,\ .
l ' ~ ~ ' m y3 _ R_.. .f "_ px - - vs 1 4 ^ rl.- 7, '
~ g'
' \
I a e dt "
/ cp A r G-e N '!
3 O
~
% s.
', 'T 'h ,
i O o Ox h ,./ r
~
f i[ / [ ~ ihit4.K' [~'i ej 33 /~ . r# .xX 1 Qv<'% Q 7 onn ./ p.ll ,g 2
-z ).%<' - .~ ,
s i, . y j. ^- i u , w i . 3 1!: i\ \g, q f\
- ,, s '
y , \8 mav g al.,iClv7. s ,f
!! l. l
'n
~, Q } %. 'i( ,-s ,
Q v f rjl 'n = ' s j-;' < v 1
, w {f ~
s Qs a
\y o ~' ':b -
jk h ;. ._
I If 1 I DELHI \ h ' w
, iguR
- CL 3 Cn50N yOnEMA
(
\
l u,6CA W ' E ecmVST AL SeptNGS l i 4 , R J eHAZLEHURIT 9 l j
%FAVE,TE / wEssoN pEmmtDAY RIDGECR vlDAL
'))
- eMOOgMAVEN N
/
s ~
\ ,
nouas 2-3 CENERAL AREA W LE GEND
- 4. * % '""""~
. O^'".'Loe,1*
$ ,s p
gr.ALL .a C,, ..n P 1 l 2-20
SECTION 3.0 ANALYTICAL PROCEDURES AND COUNTING METHODS J20AREOR850306 1
3.1 ANALYTICAL PROGRAM AND METHODOLOGY Samples are analyzed for the various radioactive components by standard radiochemical methods. Those methods are equal to and in most cases identical with those of the USDOE (HASL Procedures Manual, HASL-300, Health and Safety Laboratory, U. S. Atomic Energy Commission, 376 Hudson Street, New York, New York 10074), or those of the U. S. I Department of Health. The analytical program is summarized in Table 3-1. 3.2 ANALYTICAL DETECTION LIMITS AND COUNT RATE ERRORS In environmental radiological analyses the dominant known uncertainty is usually the sample count rate. Error terms given in this report are based on this factor since all other analytical uncertainties are calculated by standard methods and are reported at the 95 percent (2 sigma) confidence level. Analytical data for samples for which concentrations are less than the Lower Limit of Detection (LLD) are preceded by the symbol " < ". The sample types, analyses performed and units of the measurements along with the corresponding required LLD,'.are presented in Table 3-2. 3.3 AIR PARTICULATES Gross beta concentrations are measured with low back-I ground gas flow proportional counting systems with anti-coincidence background suppression after the short-lived naturally occurring radon and thoron daughters have decayed. J20AREOR850306 - 3 ,1
The filters are counted long enough to ensure that the required sensitivity (LLD) is met. The required LLD is 0.01 pCi/m 3 for gross beta based on about 300 m / 3 week of air volume. Gamma isotopic analyses of the quarterly composite samples are performed with a Ge(Li) or GeHP detector with required LLDs as listed in Table 3-2. 3.4 RADIOIODINE The charcoal cartridges used are of the TEDA-impregnated type. The samples are analyzed for I-131 gamma-spectroscopically using Ge(Li) or GeHP detectors. The required LLD is 0.07 pCi/m 3, 3.5 CISTERN WATER Gross beta analysis of cistern water is performed by evaporation of a measured aliquot of the sample, digestion, planchetting of the processed sample and radiometric assay by low-level beta counting. The required LLD is 4 pCi/ liter. Iodine-131 analysis is based on anion exchange removal of the I-131 from a known sample volume. The iodine is
- eluted from the resin with Na0Cl which also oxidizes it to the iodate. The iodate is reduced to iodine with hydroxylamine in 3N nitric acid solution. The iodine is i extracted into carbon tetrachloride, reduced to iodide with sodium bisulfite, extracted into water and precipitated as PdI .
2 The sample is filtered, dried, weighed and beta counted. The required LLD is 1 pCi/ liter. J20AREOR850306 2
Gamma isotopic analysis is performed by taking a measured aliquot of the sample and counting it in a standard geometry in a high resolution (GeLi or GeHP) gamma spectrometer long enough to meet the required LLDs in Table 3-2. Tritium analyqis is performed on the quarterly composite of the monthly samples. This composite sample is analyzed by liquid scintillation technique. 3.6 SURFACE WATER Monthly samples are analyzed by gamma spectrometry as described in Section 3.5 under Cistern Water. The quarterly composite sample of the monthly collections is analyzed for tritium by the scintillation technique described in Section 3.5 under Cistern Water. 3.7 GROUNDWATER Quc-Serly samples are analyzed for gamma-emitting radionuclides and tritium as described in Section 3.5 under Cistern Water. 3.8 MILK I-131 analysis is performed on the monthly milk samples. The method used is the same as given in Section 3.5 under Cistern Water. Gamma isotopic analysis is performed as described in Section 3.5 under Cistern Water. J20AREOR850306 3
1 i ! 3.9 SEDIMENT Sediment samples are oven-dried and then sieved (if 4 required) to remove stones and/or other large pieces of material. An appropriate sized and weighed aliquot is then transferred into a standard geometry container and counted in a high resolution Ge(Li) or GeHP gamma spectrometer for a long enough period to achieve the required LLDs listed in
! Table.3-2.
3.10 VEGETATION l A measured amount of cut or mashed sample is transferred into a standard geometry container and counted in a high resolution Ge(Li) or GeHP gamma spectrometer for a long enough period to meet required LLDs listed in Tab 1' 3-2. 3.11 FISH & MEAT 1 , A measured amount of fillet and/or cut sample is - i transferred into a standard geometry container and counted in a high resolution Ge(Li) gamma spectrometer for a long enough time to meet the required LLDs listed in Table 3-2.
- 3.12 THERM 0 LUMINESCENT DOSIMETERS (TLDs)
Environmental radiation doses are measured using badges , comprised of five chips sealed in plastic protective holders 4 having a density of about 50 mg/cm2 . The TLD chips are 1/8" , ; x 1/8" x 1/32" LiF (thallium activated) known commercially
\
as Harshaw TLD-100. The chips are selected to provide uniform responses. Prior to installation, the chips are annealed by a standard cycle of 60 minutes at 400*C followed l l l 1 : l I J20AREOR850306 4
i
- by 2 hours at 100*C and immediate cooling to ambient temperature by placing the tray containing the annealed chips on an aluminum block.
After exposure the chips are pre-annealed for 10 minutes at 100*C and are read on a Harshaw 2000P reader. The system employs a preheat cycle which removes low temperature peaks and integrates and digitizes only the light output in a selected temperature range. The dose is calculated from the average light output for the five readings. Control badges are used to detect any unusual exposure to the badge which might occur during shipment. The LLD for environmental TLDs is 1 mrem / quarter. i e J20AREOR850306 5
TABLE 3-1 ANALITICAL PROGRAM SAMPLE PARAMEIER FREQUENCY ANALYSIS Air Particulates Weekly Cross Beta (1) Quarterly Gama Isotopic Airborne Iodine Weekly Iodine-131 Themolminescent Quarterly Rad.iation Dose Dosimetry (TID) Milk Monthly (2) Iodine-131 Gama Isotopic Broadleaf Vegetation Monthly (3) Iodine-131 Ga ma Isotopic Sediment S miannually Gama Isotopic Groundwater Quarterly Gama Isotopic Quarterly Tritim Cistern Water Monthly Iodine-i31 Gama Isotopic Gross Beta Quarterly Conposite Tritim Surface Water Monthly (4) Ganma Isotopic Quarterly Cmposite Tritita Fish Smiamually Gama Isotopic Meat Annually ra ma Isotopic (1) If gross beta activity of any filter is found to be greater than ten times the yearly mean of gross beta for the control (ASf3) then a game isotopic analysis is performed on the filter. (2) Twice a month when animals are on pasture. (3) Broadleaf vegetation sanpling is performed monthly when available and when milk sanpling is not performed within 5 km. , (4) The conposite discharge basin water saple is utilized for gama isotopic analysis. J20AREOR850306 6 __
TABLE 3-2 MAXINUM VALUES FOR THE LOWER LIMITS OF DETECTION (LLD)**D Airborne Particulate Broad Leaf Water or Gas Fish Milk Vegetation Sediment Analysis (pCi/1) (pci/m3 ) (pci/kg, wet) (pC1/1) (pCi/kg, wet) (pCi/kg. dry) Gross beta 4 1 x 10 -2 NA NA NA NA d H-3 2000 NA NA NA NA NA Mn-54 15 NA 130 NA NA NA Fe-59 30 NA 260 NA NA NA Co-58,60 15 NA 130 NA NA NA Zn-65 30 NA 260 NA NA NA f Zr-95 30 NA NA NA NA NA Nb-95 15 NA NA NA NA NA c l I-131 1 7 x 10 ~2 NA 1 60 NA Cs-134 15 5 x 10 -2 130 15 60 150 i Cs-137 18 6 x 10 -2 150 18 80 180 j Ba-140 60 NA NA 60 NA NA La-140 15 NA NA 15 NA NA i i 3-7 i
TABLE 3-2 (cont'd) MAXIMUM VALUES FOR THE LOWER LIMITS OF DETECTION (LLD) TABLE NOTATION
- Acceptable detection capabilities for thermoluminescent dosimeters used for environmental measurements are given in Regulatory Guide 4.13.
b Table 4.12-1 indicates acceptable detection capabilities for radioactive materials in environmental samples. These detection capabilities are tabulated in terms of the lower limits of detection (LLDs). The LLD is defined, for purposes of this guide, as the smallest concentration of radioactive material in a sample that will yield a net count (above system background) that will be detected with 95% probability with only 5% probability of falsely concluding that a blank observation represents a "real" signal. For a particular measurement system (which may include radiochemical separation): 4.66 s LLD = E - V 2.2 - Y - exp(-Aat) l where LLD is the "a priori" lower limit of detection as defined above (as pCi per unit mass or volume). (Current literature defines the LLD as the detection capability for the instrumentation only, and the MDC, minimum detectable concentration, as the detection capability for a given instrument, procedure, and type of sample.) s b is the standard deviation of the background counting rate or of the counting rate of a blank sample as appropriate (as counts per minute) E is the counting efficiency (as counts per disintegration) ! V is the sample size (in uni t of mass or volume) , 2.22 is the number of disintegrations per minute per picocurie l Y is the fractional radiochemical yield (when applicable) A { is the radioactive decay constant for the particular radionuclide At is the elasped time between sample collection (or end of the sample collection period) and time of counting The value of s used in the calculation of the LLD for a particular measurement syItem should be based on the actual observed variance of the background counting rate or of the counting rate of the blank samples (as appropriate) rather than on an unverified theoretically predicated variance. , I
\
3-8 l
TABLE 3-2 (cont'd) MAXIMUM VALUES FOR THE LOWER LIMITS OF DETECTION (LLD) TABLE NOTATION (Continued) Typical values of E. V, Y and at should be used in the calculation. It should be recognized that the'LLO is defined as an a priori (before the " fact) limit representing the capability of a measurement system and not as a posteriori (after the fact) limit for a particular measurement. Occasiona1Ty background fluctuations, unavoidable small sample size, the presence of inter-faring nuclides, or other uncontrollable circumstances may render these LLDs unachievable. In such cases, the contributing factors should be identified and described in the Annual Radiological Environmental Operating Report pursuant to Specification 6.9.1.6. , C LLD for drinking water samples. If no drinking water pathway exists, the LLD of gamma isotopic may be used. d If no drinking water pathway exists, a value of 3000 pCi/1 may be used. 3-9
I SECTION 4.0 RESULTS AND DISCUSSION J20AREOR850306 1
4.1 AIR PARTICULATES AND RADIOIODINE Air particulate and Iodine-131 results for 1985 were similar to those obtained in previous years for the Operational Program. Results were also comparable to those obtained in the Preoperational Program. This indicates that the airborne exposure pathway has not been affected by the operation of GGNS and that airborne concentrations continue to be at background levels. The gross beta particulate data obtained during 1985 remained at low levels. The levels were in the range expected for this type of medium. The gross beta concentrations for the indicator loca-3 tions were in the range of 0.008 to 0.046 pCi/m with an 3 average value of 0.022 pCi/m and for the control location were in the range of 0.007 to 0.039 pCi/m3 with an average of 3 0.02 pCi/m . Measured levels were in the range expected for this type of medium. Analysis results for individual filters are provided in Table 7-1, 1985 Sampling and Analysis Results. Airborne Iodine-131 concentrations were less than 0.07 pCi/m 3 for all samples received. Analysis results are presented in Table 7-1. The gamma spectrometry data for the quarterly composites of air particulates is also presented in Table 7-1. Results were below the LLDs for this analysis. J20AREOR850306 1
4.2 AMBIENT RADIATION LEVELS (GAMMA DOSE BY TLD) Gamma radiation dose in 1985 was measured with thermoluminescent dosimeters (TLDs) on a quarterly schedule. Three TLD locations showed a significant difference in mean yearly dose rates when compared to 1984 data. Locations M-68, M-69 and M-70 showed mean yearly increases over their 1984 dose rates as summarized below: Location 1984 Dose 1985 Dose Increase % Increase (mR/Qtr) (mR/Qtr) (mR/Qtr) M-68 16.6 30.2 13.6 81.9 M-69 13.6 34.2 20.6 151.5 M-70 13.2 39.0 25.8 195.4 M-04 Control 20.9 20.3 N/A N/A TLDs M-68, M-69 and M-70 are located on the protected area fence facing the Radwaste Building. The protected area fence TLDs are used to calculate direct radiation dose to the public. As reported in the Semiannual Radioactive Effluent Release Report (SRERR) dated February 26, 1986, the direct radiation dose to the public in 1985 was 8.3 mrem. This was within the limits specified by GGNS Technical Specification 3.11.4. However, it was the first year an increase above background had been observed. Table 4-1 summarizes annual direct radiation dose since 1983. Increased processing and shipping of radwaste in 1985 were responsible for the increased dose rates observed at TLD J20AREOR850306 2
locations M-68, M-69 and M-70. Continued operation of GGNS will result in higher activity in the waste being processed. This in turn will continue to cause individual TLDs to read significantly higher than the average. A more detailed discussion of this anomaly is provided in the SRERR dated February 26, 1986. Other than those mentioned above, there was no significant difference in 1985 dose rates when compared to control values or those from previous years. The 1985 data is presented in Table 7-1. 4.3 MILK No milk samples were available in 1985 within eight kilometers of the GGNS site. Milk samples from the optional locations at the Johnson, Warren and Bell farms were also unavailable in 1985. Only milk samples from the Alcorn control location could be collected and analyzed for Iodine-131 and gamma emitters. Iodine-131 and gamma isotopic concentrations for Alcorn milk samples were below the LLDs. This is generally consistent with data from previous years. The data is presented in Table 7-1. 4.4 WATER Environmental Surveillance Program personnel sampled cistern water, surface water and groundwater as required during 1985. Analysis results were similar to those reported for previous years, with the exception of tritium in Discharge Basin surface water. J20AREOR850306 3
Cistern Water Cistern water samples were collected from two locations and analyzed for gross beta, Iodine-131 and gamma-emitting radionuclides. The gross beta concentrations for the indi-cator location were in the range of 0.8 to 3.4 pCi/l with an average value of 1.9 pCi/1. The control location was in the range of 0.8 to 2.6 pCi/l with an average of 1.3 pCi/1. Measured levels were in the range expected for this type of medium. The I-131 and gamma-emitting radionuclides concentra-tions were below the LLDs. Tritium measurements were made on quarterly composites. Tritium levels were equal to or less than the LLD and were in the range expected for this type of medium. Data collected for cistern water is provided in Table 7-1. Surface Water Surface water samples were collected monthly and analyzed for gamma-emitting radionuclides. Quarterly composites were analyzed for tritium. Gamma isotopic concentrations were below the LLDs for upstream, downstream and Discharge Basin samples. J20AREOR850306 4
Tritium levels for Discharge Basin surface water ranged from 420 pCi/1 to 520 pCi/1 with an average value of 470 pCi/1. The second quarter of 1985 was the first time that tritium was detected in Discharge Basin surface water at GGNS. This activity was attributable'to increased plant operating levels and radwaste discharges in 1985. Tritium levels for upstream and downstream Mississippi River locations were equal to or less than the LLD. Data is presented in Table 7-1. Groundwater Groundwater samples were collected quarterly and analyzed for gamma-emitting radionuclides and tritium. The gamma-emitting radionuclides and tritium levels were below the LLDs. The data is presented is Table 7-1. 4.5 VEGETATION Vegetation samples were collected in 1985 from two onsite locations (Sector J and R) and a control location at Alcorn University. These samples were analyzed for gamma-emmitting radionuclides and I-131. The analysis of October 14, 1985 vegetation samples was performed at the Arkansas Power & Light (AP&L) Environmental Laboratory rather than at the primary contractor Teledyne Isotopes. The October 14 samples sent to Teledyne were lost in shipping, but a duplicate set had been sent to AP&L. J20AREOR850306 5 I
l l Analysis results from AP&L were similar to those received from Teledyne for other vegetation samples. Gamma isotopic and Iodine-131 concentrations measured by both Teledyne and AP&L were below the required LLDs. Results from previous years were also at very low to non-detectable levels. Analysis results from Teledyne and AP&L are included as Tables 7-1 and 7-2, respectively. 4.6 SEDIMENT Sediment samples were collected at least semiannually in 1985 and analyzed for gamma-emitting radionuclides as required by the GGNS Technical Specifications. Sample results from the downstream location, required by GGNS Technical Specifications, and the upstream control were at or below the 3 LLDs. These results were consistent with previous sample results obtained during preoperational and operational sampling. Sediment samples were also collected from the GGNS barge slip. Results from barge slip sediment samples showed a very slight increase over previous sample results. The average and maximum values for barge slip sediment samples were as follows: Radionuclide LLD (pCi/q) Avg. (pCi/g) Max. (pCi/g) Cesium - 134 0.15 < 0.15 < 0.15 Cesium - 137 0.18 0.19 0.24 Cobalt - 58 0.15 0.34 1.05 Cobalt - 60 0.15 0.40 0.69 Manganese - 54 0.15 1.15 2.62 J20AREOR850306 6
Samples collected from the barge slip location in previous years have been below the required LLDs. Liquid radioactive effluents from GGNS are mixed with the cooling tower blowdown and discharged into the Mississippi River via the barge slip. Considering the predicted annual average concentrations of radionuclides in liquid plant effluents for two unit operation (F'inal Environmental Report, Table 5.2.1), an increase in ! radionuclides in the barge slip sediment is understandable. As reported in past Semiannual Radiological Effluent Release Reports (SRERRs) cobalt and manganese radionuclides have been present in GGNS effluents, but Cesium-137 has not been identified in SREERs. Possibly Cesium-137 was below the required LLD (5 x 10-7 pCi/ml) and was not detected. However, none of these radionuclides were detected in dis-charge basin composite water samples, confirming that GGNS is meeting all specified release limits and parameters. The presence of these radionuclides in barge slip sediments may be attributable to build up of very small amounts of sediment over a period of time. The effluent water velocity decreases in the barge slip and this would promote settling of small particles. Radionuclide concentrations at the levels detected in barge slip sediment are not a threat to human health or the environment. Concentrations are well below the unrestricted
. release limits described in 10CFR20, Appendix B, Table 2, Column 2. Barge slip monitoring will continue to document J20AREOR850306 7
sh changes which may occur, but no further actions to address this occurrence are planned or necessary. 4.7 FISH Fish samples were collected semiannually and analyzed for gamma-emitting radionuclides. The gamma isotopic levels were below the LLDs, as has been the case in previous years. The data is presented in Table 7-1. 4.8 SPECIAL SAMPLES Twenty-four special samples were collected during the year and analyzed for gamma-emitting radionuclides. This includes six special samples from Outfall 007 that were also i analyzed for gross beta concentrations in addition to gamma-emitting radionuclides. Analysis results for special samples were below the LLDs for gamma-emitting radionuclides. However, Outfall 007 gross beta results ranged from 2.2 pCi/l to 4.8 pCi/1 with an average value of 3.4 pCi/1. These results are similar to the gross beta concentrations found in indicator location cistern water samples. This would be expected because one of the main components of Outfall 007 effluent is natural runoff. The data is presented in Table 7-1. Descriptions of the special samples collected are provided below: o Outfall 015 - Twelve samples of sewage plant effluent were analyzed from January through December 1985. o Outfall 007 - Six samples of Outfall 007 effluent were analyzed from June through November 1985. 4 J20AREOR850306 8
o Sediment - Five sediment samples were collected at the influent end of Sediment Basin B from August through December 1985. o Venison - A venison sample was collected November 25, 1985 at the Bucksnort Hunting Camp (Sector N, 1.8 miles). 4.9 LAND USE CENSUS The method used for conducting the 1985 Land Use Census was as follows: (1) Environmental Surveillance Program (ESP) personnel conducted field surveys in each meteorological sector out to five miles in order to locate the nearest resident, milk animal and garden. (2) Telephone confirmation was used in several instances when persodal contact could not be made. (3) As a result of these surveys, the following information was obtained/ confirmed in each meteorological sector: o nearest residence and owner's name & address o nearer unoccupied residence o nearest garden and approximate size o nearest milking animal (4) ESP personnel determined the locations of the nearest residence in each meteorological sector and the nearest garden in each meteorological sector and marke,d them on maps. Nearest residence is marked with an asterisk and nearest garden is marked with a square. These maps are included as Figures 4-1 and 4-2. (5) ESP personnel compared the 1985 Census results to 1984 Census results. The results of the 1985 Census are outlined below: o There were no milk animals located in any meteorological sector in the 5-mile zone surrounding the plant. , l , o The nearest residences in meteorological ! sectors A, D, G and L has changed since the l 1984 Census. I l l J20AREOR850306 9
o The nearest garden in meteorological sectors F and R has changed since the 1984 Census. o There were no gardens located by the 1985 Census in meteorological sectors A, L, M, N, P and Q in the 5-mile zone. Although some minor changes occurred from 1984 to 1985, I there was no need to modify the Environmental Surveillance Program. Also, there was no location identified which yielded a calculated dose or dose commitment greater than those currently being calculated. However, administrative changes to the ODCM were necessary and these are reflected in the GGNS Offsite Dose Calculation Manual, Revision 7, Tables 2.2-3 and 2.3-1. The 1984/1985 Land Use Census changes are summarized in Table 4.2. The 1985 Land Use Census data sheets are presented in Table 4-3. In conclusion, the results of the 1985 Land Use Census indicated the land uses in the zero to 5-mile area surround-ing GGNS have remained basically the same as those reported in the 1984 Annual Land Use Census. 4.10 EXCEPTIONS TO THE ENVIRONMENTAL SURVEILLANCE PROGRAM 4.10.1 TLDs o Seven TLDs required by GGNS Technical Specifications were lost in the field during 1985. These losses were caused by vandalism and Mississippi River flood waters. TLD losses of this type are characteristic of other TLD programs and actions to prevent such losses have been ineffective. The 1985 TLD recovery rate was approximately 96% and is comparable with other TLD programs. J20AREOR850306 10
l i I TABLE 4-1 i DIRECT RADIATION DOSE
- Year 1st Qtr 2nd Qtr 3rd Qtr 4th Qtr Annual Total l I 1983 1 0.0 0.0 0.0 0.0 1 0.0 l l 1984 1 0.0 0.0 0.0 0.0 1 0.0 l l 1985 l 0.0 3.0 5.3 0.0 l 8.3 1
t
- Calculated as described in the GGNS ODCM and reported in the Semiannual Radioactive Effluent Release Reports. Limits are 25 mrem to total body and 75 mrem to the thyroid.
J20AREOR850306 11
Table 4-2 1984/1985 Land Use Census Changes ctor Parameter 1984 Data
- 1985 Data
- Reason for Change
- A Nearest Occupied C. Roddy E. McGee The sector & distance Residence 2.1 1.5 were misreported in the 1984 Census due to an oversight.
A Unoccupied 1.5 None The 1984 unoccupied Residence residence was a mobile home which has been moved A Garden W. Hatcher None No gardens planted in 4.8 this sector in 1985 B Unoccupied 1.6 None No unoccupied Residence residence closer than 1.2 C Unoccupied 6.7 None There is no unoccupied Residence residence closer than 1.1 D Unoccupied 5.8 None There is no unoccupied Residence residence closer than 4.3 0 Occupied R. Moore E. Ryals New house built by Residence 4.4 4.3 Ms. E. M. Ryals F Garden D. Cupstid F. Barron Garden location changed 7.0 7.0 from D. Cupstid to F. Barron but distance from GGNS remained the same i o Distances in in kilometers J20AREOR850306 12
Table 4-2 (cont.) 1984/1985 Land Use Census Changes Sector Parameter 1984 Data
- 1985 Data
- Reason for Change
- G Occupied C. Buckner G. Barron Rental house belongin6 Residence 3.4 3.1 to Buckner is occupied by Barron J Occupied B. Cassell B. Cassell Distance was Residence 4.6 3.8 recalculated K Occupied J. Cassell J. Cassell Distance was Residence / 4.6 3.8 recalculated Garden L Occupied P. Moseley D. O. Glodjo Glodjo is permanent Residence 1.4 1.4 resident at 1.4 N Unoccupied 2.4 2.6 Recalculated distance Residence to nearest unoccupied residence (Bucksnort Cap)
P Occupied 7.2 7.8 Recalculated distance to Residence nearest occupied residence (G. Parker) Q Unoccupied N/A 6.4 10 unoccupied trailers Residence located at Miss. Hunting Cap on Ia. side of river R Garden B. Roddy MP&L Garden An MP&L garden is now 2.3 1.2 being maintained in Sector R (2nd highest D/Q) i 1
- Distances in in kilometers J20AREOR850306 13 ;
j
TABLE 4-3 1985 LAND USE CENSUS PARAMETER SECTOR A SECTOR B SECTOR C SECTOR D I. Nearest a. Distance (km) 1.5 1.2 1.1 4.3 Occupied b. Name Elizabeth McGee Prince Dotson Lanell Frazier Ethel May Ryals Residence c. Address Rt 2, Box 391 Rt. 2, Box 147 P. O. Box 33 Rt. 2, Box 371 Port Gibson, MS Port Gibson, MS Port Gibson, MS Port Gibson, MS
- d. Number of Occupants 1 7 3 4 II. Nearer a. Distance (km) None None None None Unoccupied Residence III. Nearest a. Distance (km)
Milk b. Owner's Name None None None None Animal c. Address IV. Nearest a. Distance (km) 1.4 1.1 4.4 Broad b. Owner's Name None Prince Dotson Lanell Frazier Richard Moore Leaf c. Address Rt. 2, Box 147 P. O. Box 33 Rt. 2. Box 373 Garden Port Gibson, MS Port Gibson, MS Port Gibson, MS
- d. Garden Size (m2) 50 50 50 V. Census Comparison:
- a. Is the nearest occupied residence in the same location as last census? N0 YES YES N0
- a. Is the nearest milk animal in the same location as last census? N/A N/A N/A N/A 4
- c. Is the nearest broadleaf garden in the same location as last census? N/A YES YES YES J20 CENSUS 850923 4-14
TABLE 4-3 (cont'd) ' 1985 LAND USE CENSUS 1 PARAMETER SECTOR E SECTOR F SECTOR G SECTOR H l I. Nearest a. Distance (km) 0.9 7.0 3.1 1.8 l Occupied b. Name Maggie Jackson Dykes Cupstid Guy Barron John Nichols Residence c. Address Rt 2, Box 149 Rt. 2, Box 156 P. O. Box 415 General Delivery Port Gibson, MS Port Gibson, MS Port Gibson, MS Port Gibson, MS
- d. Number of Occupants 1 3 1 2 II. Nearer a. Distance (km) None None None None Unoccupied Residence III. Nearest a. Distance (km)
Milk b. Owner's Name None None None None Animal c. Address I IV. Nearest a. Distance (km) 1.3 7.0 3.4 5.2 Broad b. Owner's Name Hiram Wells Fred A. Barron C. B. Buckner Anderson Walker-Leaf c. Address Rt. 2, Box 146 Rt. 2, Box 150B Rt. 2, Box 416A Rt. 1, Box 414 Garden Port Gibson, MS Port Gibson, MS Port Gibson, MS Port Gibson, MS
- d. Garden Size (m2) 100 4000 1000 (Grapes) 200 g
V. Census Comparison:
- a. Is the nearest occupied residence
- in the same location as last census? YES YES N0 YES
- a. Is the nearest milk animal in the j same location as last census? N/A N/A N/A N/A
- c. Is the nearest broadleaf garden in the same location as last census? YES N0 YES YES J20 CENSUS 850923 4-15
TABLE 4-3 (cont'd) 1985 LAND USE CENSUS PARAMETER SECTOR J SEri:R K SECTOR L SECTOR M I. Nearest a. Distance (km) 3.8 3.8 1.4 Occupied b. Name Bill Cassell Jim Cassell D. O. Glodjo None Residence c. Address Rt 2, Box 404 Rt. 2, Box 403 Rt. 2, Box 401 Port Gibson, MS Port Gibson, MS Port Gibson, MS
- d. Number of Occupants 4 3 2 II. Nearer a. Distance (km) None None None None Unoccupied Residence III. Nearest a. Distance (km)
Milk b. Owner's Name None- None None None Animal c. Address IV. Nearest a. Distance (km) 0.6 3.8 Broad b. Owner's Name MP&L (Environ) Jim Cassell None None Leaf c. Address P. O. Box 756 Rt. 2, Box 403n Garden Port Gibson, MS Port Gibson, MS
- d. Garden Size (m2) 2500 1000 V. Census Comparison:
- a. Is the nearest occupied residence in the same location as last census? YES YES NO N/A
- a. Is the nearest milk animal in the same location as last census? N/A N/A N/A N/A
- c. Is the nearest broadleaf garden in the same location as last census? YES YES N/A N/A J20 CENSUS 850923 4-16
V TABLE 4-3 (cont'd) 1985 LAND USE CENSUS PARAMETER SECTOR N SECTOR P SECTOR Q SECTOR R I. Nearest a. Distance (km) 7.9 2.3 Occupied b. Name None Gary Parker None Buddy Roddy Residence c. Address Hwy 608 Rt. 2, Box 390 Newe11 ton, LA Port Gibson, MS
- d. Number of Occupants 5 4 l II. Ner**r a. Distance (km) 2.6 6.4 1.4 Unoccupied (BucksnortCamp) None (Miss. Hunting) (Met. Tower)
Residence Camp (on Yucatan) Trailer III. Nearest a. Distance (km) Milk b. Owner's Name None None None None Animal c. Address IV. Nearest a. Distance (km) 1.2 ,i Broad b. Owner's Name None None None MP&L Environ.
- Leaf c. Address P. O. Box 756 Garden Port Gibson, MS
- d. Garden Size (m2) 2500 V. Census Comparison:
} a. Is the nearest occupied re Mance in the same location as last unsus? N/A YES N/A YES i i
- a. Is the nearest milk animal in the same location as last census? N/A ft/A N/A N/A 4
- c. Is the nearest broadleaf garden in the same location as last census? N/A N/A N/A N0 i
J20 CENSUS 850923 4-17
TABLE .4-3 1985 LAND USE CENSUS VI. Remarks: Census conducted by: 7/I mSighature
) 9 /24 /8 5 Date VII, Review:
- a. Comparison of previous and present locations:
[ ] No differences [X] Differences [ ] Significant [X] Insignificant
- b. Calculations:
[X] Not required /- 2 -8
% Required Completed: da-- 9 /49/F5 Sidnature Date VIII. Reviewed / Approved: /2 //7 /#s Supervisor, Environmental Services Date J20 CENSUS 850923 4-18
4 T
?e t
,' %l[U .
y, i g l
!, J
, 2
- iunih!illi i l, llllCO);l'I*oaoa / s
*-" e s' !, -iql / -'
f; i! b .e> l
, (, ,
f i l e,
's f
~~.,_.s ,/ f' .' - K' ; l.
s i ft g w .
- s. .
N <173 s , . . t n g, / (;.[e l N s -v '.- / r .[,, cc
~ ~) s n s , )
4 T' ~,b #
/ lI b
- 's~2&s ,
/[.
c 1 '1 s . ( /. _ . ' ,J 3 s 3 e
.]
> ~5 Q y R ~,4'~',' ',, .gy yl i% lg})l2 9.D,y'}J
- m. - -> ~ . q - - 2]
Q ^ k ;- y ' ,' 4 QL '. 3 y U . k,T',Q> 7 i~
~tb
^ . <
\
; ,/ b N @~ /
'r .- ) k u . [/, 'N l '
G'Y [ ,3 'h%c IJ c '?
' M y , '3, ', ;,c ,n,n ~ - > -
r m ,p, r\ /g , ' e'%,Q 5 x> , l y ; ' jy g w
~
,\i .'
( y i ,Y := ~ f n -, - [Ag ..s f "; ,- I 1l1 fj ,
, , \
~~
s'
~
N ^
, i
- . sr ~' %; ,
' )I' d ,'_f , > -i , - - t '
s
) } r
'i
[T7
,' ~'
y m '
< 'l1 7 _ / [v.] .
'c.
~-
c s q v p ') Y'~% * *-
',. f $ 4 h
/ m .
e ~ - r ___l ., , g n ; . a ts r a.gr K,, c' ;s't , c - yn.. y jQ.q m p i , t y p-s a ~ l i i N
\
g i # i '
. . -: i! N N i i
% . N x
i !! r 4
..v .
ks_._; fA) s _ e g r -
; s a: \,
k-j
.- . s
[ ,, --
/ j ~
'(
'~ '
7- ' , J.n c
.7
)ws,e<\s <-> t s
/ g
.,5 " f'
. E \ .' .
~.-
L, .e,s,
,i j) i b'! %f' 'O
/ I '
-~
( > ( ' y: y -l o,y ,q [1 r ( v w
'd \ ysi ! ,-
+ -
( s'.. ... 1 I {
I 4 GJ 6.4 3 e4 Es.
~
~-s >
'l*
ggg 8 - TN As h' -
\ l !I g N
! M f l yl l l,l 7 lll k "~. '
* / \ t 33 f"
- l l t lOO } ;l12 4 o a o e f wagj .-s; ~ <
ggN
~~ ' 'l
'k p.* m \g
~
j f'
'j '
, ?l
,%- s t /
m 1 ( .l' ; ss,2
%- %r..-
- i.
/
N / 7 n'rx 46 -w x s.s>
~
8
< 11 5
/ v- - -y 1
- l. p \ ~~>\ J ~
\ ) l l
?
m,)- ,1 J, [f
' '~ ' k r , I '
} %., I' , ~ , -
+ l
'f . Q
\\J ' 'aP s '
%s m@ , t ,
i s s e
,,v ,. -
; M .;n.Pfx6,g% _ - -
^ '
wj't % . ,gg m, /
, I ,
, ew ' %,s , u c Tih._- s s vc 'N J' z -C .' h, m'~ (. e.', - 1 )!
,- p t 3'
' , ^\s .
I \ 8 , ~, ,- ~,., .% ,, ,. , f. . (
' y}N H
s
, y s 'p h '
't g' g 1 '"
*Y
[ g
/ss %
S : . 1 t 1 1
\, ,,
- }~o,/'~ -
Z w
/ \ ',.f, \ 1
'. u, i.t - g h ;~ f I
; i
, , , ~
sp : ,, -
$ " '~
~
- ' {,t ,ik_. : ,
m. r np
, ,n+ s . -
bg , 4 f*+;{
\
3 Y r
~
_, 3 , y
; k.d c [g L ,
Q _. -
,.' y.
?
6 3 c' 7.;
,4
/' .
s[
~
- ,s ', b I
( %' J
. ,,, .s s fe% s -
\ g y N l
g , * ' , '- I! '\ , i I ' s 'x .i k,_ 4r
.> ~ ..<
u
- N;\ ,(, .r' (s
~
I g, ,
; \ h1 s
f a A j lI 4 ,[' s , e N s l
,, +
s , e,
/, q q
s 1 ( (>. - [ ,. 'N b r'
/ sy>
. s ,-
1)3/k ' e
?\.- t M s (v w t
,--.nf u
+
=
uq ie ! . *( n-w a , ,.
.,,\
f_ .K n .i.^ ) . 1 [ -
\x\,,/x s -
i , N.) ( $.' , N . l l l i
- - . . - _ . . . . , . . - - -. - , - - . - . . . . .. - - . - . . , . . . - ~ . - - - . . , _ .
SECTION 5.0 RADIOLOGICAL ENVIRONMENTAL SURVEILL'sNCE PROGRAM
SUMMARY
I '?
', in l
l l l J20AREOR850306
5.1 1985 PROGRAM RESULTS
SUMMARY
The results of the Radiological Environmental Surveil-lance Program for 1985 are summarized in Table 5-1. Table 5-1 includes only the sampling locations required by
' GNS Technical Specifications.
, These required locations are identified in Section 2.0. Also, Table 5-1 does not include duplicate sample results.
Indicator and control locations are as designated by the GGNS Technical Specifications. For determining the g ranges and means for indicator and control locations, values reported as less than were not used. 5.
\
1 J20AREOR850306 1 v
Table 5-1 ENVIROWlENTAL RADIOLOGICAL MONiiONING PROGRMI SUP91MY Name of Facility kand Gulf helear Station Ducket eso. 50-416 _ Location of Facility Claiborne, Mississippi Neporting Period January - December 1985 (County, State) Indicator Location with Highest Control Saaple Type and Locations Annual Mean Locations senseer of Type ilumber of Mean (F C Mean (t) Mean (F) en-routine (9 tits) Analysesa LLDb Range Locationd Range Range Mesultse Air Particulates G8 260 0.006f 0.022 (204/208) AS-1 Port Gibson 0.022 (51/52) 0.020 (51/52) 0 f (pCl/m3) (0.008-0.046) City darn (0.006-0.046) (0.001-0.039) (Sector G, 5.5 al) i AS-7, Met Tower 0.022 (52/52) (Sector A, 0.8 al) (0.010-0.043) ' AS-8, Jackson's 0.022 (49/52) Traller (0.006-0.038) (Sector E, 0.5 al) G5 20 Cs-134 0.05 (LLO - - (LLD 0 Cs-137 0.06 (LLO
- - (LLO O Other Gaassas 0.06 (LLO l - - (LLO O 4
Airborne lodine 1 (pCl/m3) I-131 259 0.079 (LLO * - - <LLO O
- 1 TLD (Inner Ring) Gaasna 62 1. 0 16.1 (62/62) . M-53, Sector H 20.6 (4/4) None 0 (mR/Qtr.) (4.8-27.1) ;
1.1 at (13.0-27.1) TLO ((hter Ring) Gasona 62 1. 0 16.7 (62/62)
- M-50, Sector 8 24.6 (4/4) kne 0 (mR/Qtr. ) j (2.2-38.4) 5.5 el (18.0-38.4)
TLO (Control) Gaassa 4 : None M-14 at AS-3 20.0 (4/4) 20.0 (4/4) 0 (Sector 8, 18 mi) (adt/Qtr. ) l 1.0 (19.3-20.8) (19.3-20.8) , TLO(Special Gaassa 25 1. 0 17.2 (25/25) M-09, Sector 0 20.9 (2/4) None
' 3.5 al, Warner Interest Areas) (11.3-25.1) (16.1-25.1)
(mR/0tr.) Tully Camp l l
. l ,
s 5-2
- . . _ ~ ~ Table 5-1 (continued) ENVIRO
- ENTAL NAD10 LOGICAL MON 11URING PH0 GRAM
SUMMARY
Name of Facility Grand Gulf Nue' ear Station Docket No. 50-416 location of Facility Claiborne, Mississippi Neporting Period January - December 1985 (County, 5 tate) Indicator Location with Highest Control Sanple Type and Locations Annual Mean Locations Nusber of Type Number of Mean (F) Mean (F) Non routine Analysesa Mean(FjC (Units) LLlh Range Locationd Range Range Nesultst Cistern Water GB 24 0. 6 1.9 (9/12) Trim Cist. East of 1.9 (9/12) 1.3 (12/12) 0 (pCi/1) ( 0. 8-3. 4 ) GGN5 at Trimble (0.8-3.4) (0.8-2.6) Tenant House (Sector E 0.5 mi) 1-131 24 1. 0h (LLD - - <LLD 0 H-3 8 330 <LLD - -
<LLD 0 G5 24 Mn-54 15 <tLO - - (LLD 0 Fe-59 30 <LLD - - (LLD 0 Co-58 15 (LLD - -
<LLD 0 Co-60 15 <LLD - -
<LLD 0 Zn-65 30 <LLD - - <LLD 0 Zr-95 30 <LLD - -
(LLD 0 Nb-95 15 (LLD - - %LD , O Cs-134 15 (LLD - i
, [LL.9 0 Cs-137 18 <LLD - -
<tLU 0 Ba-140 60 (LLD - -
<LLD 0 La-140 15 (LLD - -
<LLD 'O "
\ s a
Surface Water H-3 12 330 470 (3/12) Discharge Basin. 470 (3/4) (LLD 0 (pCi/I) (420-520) West of GGNS (420-520) (Sector P 0.5 mi) ' E M ,
<tLD
* -54 15 s [ - - <LLD 0 Fe-59 30 <tLD - 1 - (LLD 0 Co-58 15 '<LLD - - (LLD 0 s
Co-60 15 <LLD - - <tLD 0 5-3
, . . - . _ _ -m_. - _ _ . . . - - _ . . .. _ . . - . _ _ _ . - - . __ . . . _ . _ . . . . . . _ _ , _ . . _-_ _ . _ . . .
.i j Table 5-1 (continued)
ENVINOW4(NTAL RADIOLOGICAL MONITORING MUGN#1 SLM4RY. Name of Fac t i t ty Grand Gulf Nuclear Station Docket No. 50-416 Location of Facility Claiborne. Mississippi Reporting Perloo January - Decemoer 1985 (County. 5 tate)
. Indicator Location with Highest Control Sample Type and Locations Annual Mean Locations Number of Type Number of Mean (F)c Mean (F) Mean (F) Non -rout ine (Units) Analysesa (L pb RangeC Locationd Range Range Resultse Surf ace Water Zn-65 30 (LLD - - <LLD 0 ) , (pCl/I) i (continued) Zr -95 30 <LLD - - (LLD 0 Nb-95 15 1 <LLD - - <LLD 0 Cs-134 15 <LLD - - <LLu 0 C5-137 18 <tLD - - (LLD 0 Ba-140 60 (LLD - -
(LLO O La-140 15 <LLD - - <LLD 0 Well Water H-3 8 330 (LLO - -
<LLD 0 (pct /1)
GS 8-Mn-54 '15- <LLD. - - (LLu 0 Fe 59 30 <LLD - - (LLD o t, Co-58 15 <LLD - - (LLu o ] Co-60 15 (LLD' - - (LLO U 2n-65 30 (LLD - - (LLu U Zr-95 30 ' <LLD - -
<Ltu o Nb-95 15 ,(LLD - -
<tLD 0 Cs-134 15 (LLD - - <LLD U
- Cs-137 18 (LLD - -
<LLO O i
8a-140 60 <LLD - - <ttu o
- La -140 15 (LLD - - (LLU 0 5-4
Table 5-1 (continued) ENVIRUtt4[NTAL RADIOLUblCAL MUNiiUHlNG PRUuRAM 5tPsiARY Name of Facility Grand Gulf Nuclear Station Docket No. 50-416 Location of Facility Claiborne, Mississippt Neporting Period January - December 1985 (Lounty State) Indicator Location with Highest Lontrol Samp le Type and Locations Annual Mean Locations Number of Type humber of Mean (F)C Mean (f) Mean (F) ison-rout ine (thtts) Analysesa LLDb HangeC Locationd Range Range Nesultse Milk 1-131 24 1. 0 None - - <LLD 0 (pCi/l) GS 24 Cs-134 15 None - - <LLO O Cs-137 18 None - - <LLD 0 Ba-14J 60 None - - (LLD 0 La-140 15 None - - (LLD 0 Vegetation 1-131 99 0.060 <LLD - - <LLD 0 (pCi/g wet) gg GS Cs-134 0.060 <LLD - - (LLO O C5-137 0.080 (LLD - - (LLO O Uther Gammas 0.080 (LLD - - (LLD 0 Fish G5 4 Mn-54 0.13 <LLD - - (LLD 0 Fe-59 0.26 <LLD - - <LLD 0 Co-58 0.13 <LLD - -
<tLD 0 Co-60 0.13 <LLD - - (LLD 0 Zn-65 0.26 <LLD - - <LLD 0 Cs-134 0.13 <LLD - - (LLD 0 Cs-137 0.15 <LLD - - <LLD 0 5-5 s
Table 5-1 (continued) ENVlW0 MENTAL RADIOLOGICAL MONITURING PROGHAM StM4ANY Name of Fac t i t ty Grand Gulf Nuclear Station Docket No. 50-416 Location of Facility Claiborne, Mississippi Reporting Period January - December 1985 (Lounty, State) Indicator Location witn Highest Control Sanple Type and Locations Annual Mean Locations Nesber of Type Number of Mean (F)C Mean (F ) Mean (F) Non-rout ine (Units) Analysesa LLDb RangeC Locationd Nange Range Hesultse Bottom Sediments G5 7 (pCl/g dry) K-40 -- 15.0 (5/5) Sed Bar, Barge 15.1 (3/3) 13.0 (2/2) 0 (13.3-16.1) Slip (Sector Q) (13.3 16.1) (10.b-15.4) Mn-54 0.15 1.62 (3/5) Sed Bar, Barge 1.62 (3/3) <LLU 2 (0.60-2.62) Slip (Sector Q) (0.60-2.62) Co-58 0.15 0.49 (3/5) Sed Bar, Barge 0.49 (3/3) <LLU 0 (0.17-1.05) Slip (Sector Q) (0.17-1.05) Co-60 0.15 0.49 (3/5) Sed Bar, Barge 0.49 (3/3) <tLD 0 (0.23-0.69) Slip (Sector Q) (0.23-0.69) Cs-134 0.15 (LLD - -
<LLu 0 Ct-137 0.18 0.22(2/5) Sed Bar, Barge 0.24 (1/3) (LLD 0 (0.19-0.24) Slip (Sector Q) .
- G8 = Gross beta; G5 = gama scan.
C LLD = Nominal lower limit of detection based on 4.66 sigma error for background sample. Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated n parenthses (O. d
' Locations are specified (1) by name and code and (2) distance, direction, and sector relative to reactor site.
Non-routine results are those which exceed ten times the control station value. If no Control station value is availaole, the
, result is considered nonroutine if it exceeds ten times the preoperational value for the location.
Four (4) resulti have t been excluded in the determination of LLD f or gross beta. Higher than normal LLDs (U.164. U.305, 0.470, and 0.038 pCi/mJ) resulted f rom low volumes due to pump malfunctions. 9 Four (4) results have been excluded in the determination of LLD for I-131. Higher than normal LLDs (1.04, 2.36, b.06, and 0.32 D pCl/mJ) resulted f rom low volumes due to pung malfunctions. Une (1) result has been excluded in the determination of LLD for I-131. A higher tnan normal LLO (2.4 pt.4/I) resulted f rom a delay in counting. 5-6
d SECTION 6.0 QUALITY CONTROL DATA J20AREOR850306 1
6.1 CROSSCHECK PROGRAM RESULTS The results of Teledyne Isotopes Midwest Laboratory Crosscheck Program are provided in Table 7-1, 1985 Sampling and Analysis Results. Table 7-1 is Teledyne's January through December Monthly Progress Report for GGNS. Appendix A of this report contains the results obtained through Teledyne's participation in the EPA Crosscheck Program and the International Intercomparison of Environmental Dosimeters. Results for duplicate samples of water, milk, fish and vegetation media submitted by GGNS to Teledyne are also included in Table 7-1. These results may be found under the individual headings and are identified by the suffix (GG) accompanying the laboratory code. J20AREOR850306 1
O SECTION 7.0 1985 SAMPLING AND ANALYSIS RESULTS 1 l I J20AREOR850306 1
7.1 DATA FOR 1985 Table 7-1, 1985 Sampling and Analysis'Results, presents data obtained by Teledyne Isotopes on samples analyzed from i January 1 through December 31, 1985. The data was furnished by the analytical contractor, Teledyne Isotopes, as the January through December 1985 Monthly Progress Report. Table 7-2, AP&L Analysis Results, presents data obtained by the Arkansas Power & Light Environmental
! Laboratory for replicate vegetation samples collected on October 14, 1985. The original October 14 samples were lost during shipment to Teledyne Isotopes.
Data presented in Tables 7-1 and 7-2 is reasonably ) comparable to that encountered in previous years and is indicative of what is expected in environmental media of this type. A few of the media, such as. sediment and Discharge Basin surface water, contained very slight amounts of radio-activity attributable to the operation of GGNS. However, no I release limit or reporting level was exceeded. l s 1 J i J20AREOR850306'- 7-1
m TABLE 7-1 1985 SAMPLING AND ANALYSIS RESULTS J20AREOR850306 2
WTELEDYNE ISOTOPES MIDWEST LABORATORY 1500 FRONTAGE RD. NORTHBROOK, IL 600624197 (312)564 4700 1985 ANNUAL REPORT TO MISSISSIPPI POWER AND LIGHT COMPANY RADIOLOGICAL ENVIRONMENTAL SURVEILLANCE PROGRAM FOR GRAND GULF NUCLEAR STATION PORT GIBSON, MISSISSIPPI PREPARED AND SUBMITTED BY TELEDYNE IS0 TOPES MIDWEST LABORATORY PROJECT N0. 8020 i 4 proved by: -
/// /A., Date: _.?. [/7/74
" ~
@L.'G.Huebner General Manager Distribution: G. O'Dee Smith (1 copy)
R. R. Jackson (1 copy)
MISSISSIPPI POWER AND LIGHT i TABLE OF CONTENTS Section , Pg Li s t of Ta b l e s . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . iii 4
- 1. 0 INTRODUCTION ................................................. 1 1
- 2. 0 LISTING 0F MISSED S AM PLES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2 Appendices A. Interlaboratory Intercompari son Resul ts . . . . . . . . . . . . . . . . . . . . . . A-1 B. Data Reportin tentiens ................................... B-1 4
I L l ) 1 11
. ~ . ._ ._ _ . . . _ _ _ _ , - . _ _ , - _ , _ . . _ .. . _ , . . _ . . _ _ _
MISSISSIPPI POWER AND LIGHT LIST OF TABLES No. Title Pajgt 1 Airborne Particulates and Iodine-131, Locations AS - 1, AS - 2, a n d AS - 3 . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . 3 2 Airborne Particulates and Iodine-131, Locations AS-4, AS-5, and AS-6 ..................................... 5 3 Airborne Particulates and Iodine-131, Locations AS - 7, AS - 8, a n d AS - 9 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7 4 Airborne Particulates and Iodine-131, Locations AS - 10, a n d AS - 11 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 9 5 Airborne Particulates, Quarterly Composites of Weekly Collections .............................................. 11 6 Gamma Radiation, as Measured by TLDs, Required by Technical Specifications ................................. 13 7 Gamma Radiation, as Measured by TLDs, Not Required by 7
- Technical Specifications ................................. 16 i 8 Cistern Water ................................................. 18 9 Su rf a c e W a t e r . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 20 10 Di s c h a r ge B a s i n Water . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 22 11 Well Water .................................................... 23 12 Bo t t om Se d i me n t s . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 24 13 Milk .......................................................... 25 14 Bro ad Le af Ve ge t a t i on . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 26 15 Fish .......................................................... 32 16 Heat .......................................................... 33 17 Sp e c i a l S a mp l e s . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 34 Su mm a ry Ta b l e s . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 36 i
l iii
=
, # - ., , ~ , _ . - ,.
MISSISSIPPI POWER AND LIGHT
- 1. 0 INTRODUCTION The following constitutes the current Monthly Progress Report for the Radio-logical Environmental Monitoring Program conducted at the Grand Gulf Nuclear Station, Port Gibson, Mississippi. Results of completed analyses are pre-sented in the attached tables. Missing entries indicate analyses that are not completed and the results will appear in subsequent reports.
Data obtained in the program are well within the ranges previously encountered in the program and to be expected in the environmental media sampled. None of the media sampled during 1985 contained radioactivity attributable to the operation of Grand Gulf Nuclear Station. For all gamma isotopic analyses, spectrum is computer scanned from 80 to 2048 Ke V. Specifically included are Mn-54, Co-58, Fe-59, Co-60, Zn-65, Zr-95, Nb-95, Ru-103, Ru-106, I-131, Ba-La-140, Cs-134, Cs-137, Ce-141, and Ce-144 Naturally occurring gama-emitters, such as K-40 and Ra daughters, are fre-quently detected but not listed here. Data listed as "<" are at the 4.66 sigma level, others are 2 sigma. Unless noted otherwise, the less than value ("<") reported under "Other Gammas" is for Co-60 and may be higher or lower for other radionuclides. All concentrations, except gross beta, are decay corrected to the time of collection. Deviations from Scheduled Sampling and Corrective Actions Taken All samples were collected within the scheduled period unless noted otherwise in the Listing of Missed Samples. i i
)
1 i
MISSISSIPPI POWER AND LIGHT
- 2. 0 LISTING OF MISSED SAMPLES Expected Collection Sample Type Location Date Reason TLDs M-04 1st Qtr.1985 Missing in field.
M-09a 1st Qtr.1985 Missing in field. M-11 1st Qtr.1985 Missing in field. M-13 1st Qtr.1985 Missing in field. M-43a 1st Qtr.1985 Missing in field. M-87 1st Qtr.1985 Missing in field. Air Particulate AS-2 03-05-85 Meter down. Air Iodine AS-2 03-05-85 Meter down. TLDs M-Ola 2nd Qtr.1985 Missing in field. M-09a 2nd Qtr.1985 Missing in field. M-24 2nd Qtr.1985 Missing in field. M-25a 2nd Qtr.1985 Missing in field. M-34 2nd Qtr.1985 Missing in field. M-57a 2nd Qtr.1985 Missing in field. Air Particulate AS-2 06-04-85 Meter down. Air Iodine AS-2 06-04-85 Meter down. Air Particulate AS-5 08-06-85 Meter down. Air Iodine AS-5 08-06-85 Meter down. TLDs M-22 3rd Qtr.1985 Missing in field. M-24 3rd Qtr.1985 Missing in field. M-65 3rd Qtr.1985 Missing in field. TLD M-89a 4th Qtr.1985 Missing in field, a Technical Specifications requirements. 1 l 2 \
1 MISSISSIPPI POWER AND LIGHT Table 1. Airborne Particulates and Iodine-131a Collection: Continuous $ weekly exchange Units: 10-4 pCi/m Required LLD: Gross Beta - <1.0; I-131 - <7.0 AS-1 AS-2 AS-3 (C) Collection Volyme Gross Volume Gross Volyme Gross Date Beta (md) Beta (m3) Beta (m3) 01-08-85 301 3.910.5 301 3.Si0.5 303 3.3i0.5 01-15-85 358 3.310.4 355 3.510.4 355 2.9t0.4 01-22-85 354 1.110.4 356 1.3i0.4 356 0.710.3 01-29-85 357 1.5i0.3 371 2.4i0.3 361 0.910.3 02-05-85 36 0 1.210.3 34 3 1.410.3 344 0.910.3 02-12-85 357 2.010.4 357 2.3i0.4 357 2.010.4 02-19-85 358 1.4i0.3 295 1. 0i0. 3 358 1. Di0. 3 02-26-85 315 1.610.3 356 1.6i0.3 355 1.110.3 03-05-85 364 1.0i0.3 NSb -- 359 0.910.3 03-12-85 355 1.210.3 356 1.110.3 355 0.710.3 03-19-85 36 0 1.910.4 355 2.010.4 354 1.210.4 03-26-85 348 1.710.4 352 1.6i0.4 354 1.510.4 04-02-85 358 2.410.4 362 2.410.4 362 2.410.4 1st Qtr. mean i s.d. 1.9i0.9 2.0f0.8 1.5i0.9 04-09-85 362 1.7i0.4 358 1.8i0.4 358 1.410.4 04-16-85 361 2.410.4 354 2.310.4 353 2.0i0.4 04-23-85 352 2.510.4 361 2.3i0.4 361 2.310.4 04-30-85 353 2.0f0.4 352 2.310.4 353 2.Di0.4 05-07-85 363 1.910.4 362 1.9i0.4 361 1.810.4 05-14-85 351 2.310.4 351 0.7i0.4 351 <0.6 05-21-85 355 2.210.4 351 1.6i0.4 355 1.4i0.4 05-28-85 361 3.010.4 361 1.310.4 362 2.210.4 06-04-85 350 2.210.4 NSb .. 358 2.410.4 06-11-85 359 2.3i0.4 344 2.710.4 353 2.810.4 06-18-85 355 2.210.4 341 2.0i0.4 361 1.910.4 06-25-85 349 2.4i0.4 351 2.310.4 351 2.210.4 07-02-85 357 2.7f0.4 247c 2.410.4 359 2.3i0.4 2nd Qtr. mean i s.d. 2.310.3 2.0i0.5 2.li0.4 a Iodine-131 concentrations arc <7.0 x 10-2 pCi/m3 unless noted otherwise. NSb = No sample; pump inoperative. c Pump ran for only 116.3 hours. 3
MISSISSIPPI POWER AND LIGHT Table 1. (continued) AS-1 AS-2 AS-3 (C) Collection Volyme Gross Volyme Gross Volume Gross Date (m3) Beta (m3) Beta (m3) Beta 07-09-85 359 1.310.4 355 0.710.3 355 1.210.4 07-16-85 355 2. 0i0. 4 355 2.110.4 361 2.110.4 07-23-85 351 2.010.4 351 2.lio.4 350 1.8i0.4 07-30-85 359 2.110.4 356 2.4i0.4 356 1.910.4 08-06-85 356 3.0i0.4 36 0 2.410.4 357 2.5i0.4 08-13-85 357 2.6i0.4 356 2.510.4 355 2.610.4 08-20-85 353 1.810.4 361 1.510.3 362 1.7i0.4 08-27-85 364 2.810.4 358 3.210.4 355 2.810.4 09-03-85 356 2.510.4 350 2.210.4 352 1.810.4 09-10-85 36 6 1.210.3 363 1.210.3 357 1.2i0.3 09-17-85 34 2 2.710.4 34 4 2.810.4 34 4 2.810.4 09-24-85 358 2.310.4 351 2.010.4 358 1.8i0.4 10-01-85 359 2.210.4 348 2.410.4 350 2.310.4 3rd Qtr. mean i s.d. 2.210.5 2. li0. 7 2.010.5 10-08-85 36 9 2.910.4 461 3.210.3 36 4 2.410.4 10-15-85 353 2.110.4 359 2.410.4 361 1.7i0.4 10-22-85 358 0.810.3 36 3 1.310.3 36 1 1.4t0.4 10-29-85 348 0.910.3 361 1.010.3 36 2 1.010.3 11-05-85 36 7 2.0i0.4 343 2.3i0.4 343 2.010.4 11-12-85 36 4 3.2i0.4 361 3.6i0.4 361 3.li0.4 11-19-85 350 1.110.3 36 0 1.Si0.4 359 1.210.3 11-26-85 355 4.310.5 356 4.010.5 355 3.4i0.4 12-03-85 348 2.210.4 348 2.0i0.4 348 2.010.4 12-10-85 363 4.510.5 377 8.810.6 80b 2.511.4 12-17-85 351 3. 0i0. 4 296 3.210.5 297 3.110.5 12-23-85 285 4.6i0.5 397 5.3i0.4 308 3.910.5 12-31-85 12c <16.4 419 2. 9i0. 4 421 2. Di0. 4 4th Qtr. mean i s.d. 2.6fl.4 3.212.0 2.310.9 a Iodine-131 concentrations are <7.0 x 10-2 pCi/m3 unless noted otherwise. Low volume due to blown fuse. c Low volume and elevated LLO due to punp malfunction. l l l 4 _,_,_J
MISSISSIPPI POWER AND LIGHT i 1 - 4 f Table 2. Airborne Particulates and Iodine-131a Collection: Continuous weekly exchange l 10-2 pCi/m3
; Units:
Required LLD: Gross Beta - <1.0; I-131 - <7.0 i AS-4 AS-5 AS-6 Gross Volume Gross Volyse Gross i Collection Volgme 8 eta. Beta Date (m3) 3 eta (m3) (m3) 317 4.li0.5 317 4.2t0.5 316 3.8*0.5 l 01-08-85 3.4*0.4 i 01-15-85 345 3.2*0.4 347 3.6*0.4 345 354 1.1*0.4 354 1.4i0.4 354 1.2*0.4 ! 01-22-85 2.6*0.4 01-29-85 356 0. 8*0. 3 357 1.1*0.3 356 l 1.0f 0. 3 02-05-85 36 0 1.3i0.3 360 1.4t0.3 359 1 357 2.2*0.4 357 2.1i0.4 357 2.0f0.4 1 02-12-85 1.4*0.3 02-19-85 358 1.3*0.3 358 1.4*0.3 358 02-26-85 355 1.2i0.3 355 1.4*0.3 355 1.1*0.3 03-05-85 359 1.0t0.3 359 1.1*0.3 359 0.8i0.3 1~ 03-12-85 354 1.210.3 354 1.5*0.4 354 0.9i0.3 ; 03-19-85 363 2.0f0.4 363 2.0i0.4 356 1.6*0.4 348 1.210.4 348 1.6*0.4 355 1.710.4
! 03-26-85 2.4*0.4 04-02-85 361 3.3*0.4 360 2.7t0.4 360 1st Qtr. mean i s.d. 1.811.1 2.0i1.0 1.8tl.0 i
04-09-85 379 1.8 0.4 357 2.0t0.4 357 1.310.4 04-16-85 361 2.6*0.4 363 2.6*0.4 364 1.9*0.4
. 04-23-85 351 2.9i0.4 350 2.5*0.4 350 2.1*0.4 04-30-85 353 2.6i0.4 353 2.3*0.4 355 1.9i0.4 1.9*0.4 4
- 05-07-85 365 2.5i0.4 363 2.5i0.4 363 05-14-85 350 2.3*0.4 351 2.6i0.4 352 1.9i0.4 1
05-21-85 355 2.1*0.4 355 1.4*0.4 356 1.4i0.4 ' 2.4*0.4 05-28-85 360 2.7*0.4 360 2.9*0.4 360 06-04-85 358 2.4t0.4 358 2.1*0.4 358 2.0f0.4 ' 06-11-85 351 3.0*0.4 353 3.0*0.4 350 2.3t0.4 06-18-85 364 2.110.4 363 1.9*0.4 364 1.7*0.4 l 06-25-85 351 2.6*0.4 351 2.5*0.4 352 2.0t0.4 07-02-85 357 2.8*0.4 357 2.3*0.4 286 2.7*0.4 l 2.5*0.4 2.4i0.4 2.0*0.4 l s 2nd Qtr. mean i s.d. l a Iodine-131 concentrations are <7.0 x 10-2 pC1/m3 unless noted otherwise. i I i i
. 5
I MISSISSIPPI POWER AND LIGHT l Table 2. (continued). AS-4 AS-5 AS-6 Collection volgme Gross Volgme Gross Volgme Gross Date (mJ) Beta (m3) Beta (m3) Beta 1 07-09-85 359 1.2*0.3 360 1.4*0.4 361 1.210.3
, 07-16-85 348 2. Ot0. 4 350 1.8i0.4 349 .1. 610.4 07-23-85 352 2. 0i0. 4 358 1.9t0.4 360 1.50.4 07-30-85 361 2. 3i0. 4 353 2.1*0. 4 352 1.4i0.4 08-06-85 358 2.210.4 NSa -- 358 2.310.4 08-13-85 357 2.210.4 357 3. 0t0. 4 356 2.310.4
- 08-20-85 334 1.610.4 333 1. Si0. 4 330 1.6i0.4 08-27-85 356 3.210.4 358 2.610.4 358 2.110.4 09-03-85 357 2.210.4 362 2.310.4 357 2.0t0.4 09-10-85 36 0 1.010.3 354 1.2i0.3 354 1.3*0.4
- 09-17-85 349 2.210.4 355 2.6i0.4 356 2.6*0.4 1 09-24-85 358 2.210.4 358 2.1*0.4 358 2.010.4 4
10-01-85 353 1.9i0.4 353 2.6i0.4 357 2. Oi0. 4 3rd Qtr. mean i s.d. 2. 0i0. 5 2.110.5 1.810.4 10-08-85 36 0 2.210.4 36 0 2.310.4 36 0 2.4i0.4 10-15-85 355 1.8i0.4 356 2.110.4 355 2.2*0.4 10-22-85 359 1.010.3 36 0 0. 9i0. 3 300 1.010.4 10-29-85 350 1.010.3 351 1.310.4 349 1.320.4 11-05-85 372 2.Oi0.4 371 2.310.4 367 1. 8i0. 4 11-12-85 349 3.110.4 349 3.610.4 351 3.210.4 11-19-85 358 1. 0t0. 3 358 1. 6i0. 4 358 1.210.3 11-26-85 354 3.210.4 354 4. 010. 5 354 3.4i0.4 i 12-03-85 353 1.410.4 353 2.110.4 350 1.8i0.4 i 12-10-85 361 3.310.4 362 4. Oi0. 4 362 4.010.4 12-17-85 353 2.810.4 352 3.4i0.4 351 3.010.4 12-23-85 307 3. 6i0. 5 307 4. Si0. 5 307 4.210.5 12-31-85 411 1. 9i0. 4 411 2. 4i0. 4 410 1.7*0.4 4th Qtr. mean i s.d. 2. 2i0. 9 2.611.1 2.411.1 l a Iodine-131 concentrations are <7.0 x 10-2 pC1/m3 unless noted otherwise. NS = No sanple; meter down. i i l 6
MISSISSIPPI POWER AND LIGHT Table 3. Airborne Particulates and Iodine-131a Collection: Continuous $ weekly exchange Units: 10-2 pCi/m Required LLD: Gross Beta - <1.0; 1-131 - <7.0 AS-7 AS-8 AS-9 Collection Volyme Gross Volyme Gross Volume Gross Date Beta (m3) Beta (mJ) Beta (m3) 01-08-85 316 4.0i0.5 317 3.8i0.5 315 3.810.5 01-15-85 347 3.5*0.4 346 3.3i0.4 348 3.3i0.4 01-22-85 354 1.0i0.3 354 1.1i0.3 354 1.1*0.3 i 01-29-85 356 2.4i0.4 357 2.410.4 356 2.410.4 02-05-85 36 0 1. Di0. 3 359 1.410.3 36 0 1.210.3 02-12-85 356 2.1i0.4 357 2. 0i0. 4 356 4.8i0.4 02-19-85 358 1.210.3 358 1.4i0.3 359 1.210.3 02-26-85 356 1.310.3 355 1.410.3 355 1.2i0.3 03-05-85 359 1.0i0.3 359 0.8i0.3 360 0.7*0.3 03-12-85 353 1.210.3 354 1. 0f 0. 3 352 1.1*0.3 03-19-85 356 1.8i0.4 363 2.110.4 357 1.710.4 03-26-85 294 2.0i0.4 347 1.710.4 355 1.5i0.4 04-02-85 360 2.7*0.4 36 0 2.5i0.4 360 2.4i0.4 1st Qtr. mean i s.d. 1.9tl.0 1.910.9 2.0il.2 04-09-85 357 1.6i0.4 358 1.4i0.4 357 1.8i0.4 04-16-85 364 2.6i0.4 36 3 2.Si0.4 36 4 2.3i0.4 04-23-85 349 2.310.4 350 2.510.4 350 2.Si0.4 4 04-30-85 354 1.710.4 328 2.0f0.4 353 1.6i0.4 05-07-85 363 2.310.4 355 2.310.4 363 2.4i0.4 05-14-85 352 1.810.4 352 2.210.4 352 2.0f0.4 . 05-21-85 355 1.7i0.4 353 1.310.4 356 1.710.4 4 05-28-85 361 2.5i0.4 360 2.7*0.4 359 2.410.4 06-04-85 358 2.6i0.4 358 2.5i0.4 359 2.410.4 1 06-11-85 351 2.8i0.4 353 2.SiO.4 347 2.6i0.4 06-18-85 36 4 1.6i0.4 206b 3.210.7 357 1.910.4 06-25-85 352 2.4i0.4 351 2.3i0.4 350 2.7i0.4
- 07-02-85 358 2. 5*0. 4 358 2.410.4 359 2.110.4 j 2nd Qtr. mean i s.d. 2.210.4 2.3i0.5 2.2i0.4 lLowvolumeduetoblownfuse.Pump Iodine-131 concentrations ran for 97.0 hours. are <7.0 x 10-2 pC1/
7
i l l MISSISSIPPI POWER AND LIGHT l Table 3. (con.tinued) . AS-7 AS-8 AS-9 Gross Volqme Gross Volume Gross Collection Volume Beta Beta Date (m3) 8 eta (m3) (m3) 1.410.4 358 1.310.4 364 1.410.4 07-09-85 361 1.810.4 07-16-85 354 2.010.4 348 1.910.4 347 1.810.4 36 0 1.910.4 298 2.210.4 07-23-85 354 2.0i0.4 352 1.910.4 348 2.110.4 07-30-85 351 2.810.4 08-06-85 358 3.010.4 357 2.810.4 358 356 2.210.4 295 2.710.4 354 2.110.4 08-13-85 1.6i0.4 08-20-85 128b 1.810.9 348 1.7*0.4 332 2.810.4 359 2.2i0.4 354 2.310.4 00-27-85 347 2.410.4 09-03-85 355 2.410.4 355 2.4i0.4 36 0 354 1.110.3 6c <30.5 351 1.4*0.4 09-10-85 2.5*0.4 09-17-85 356 2.910.4 4d <47.0 356 358 2.210.4 40e <3.8 358 2.010.4 09-24-85 2.510.4 10-01-85 357 2.310.4 472 2.710.3 354 2.110.6 2.2i0.5 2.110.4 3rd Qtr. mean i s.d. 10-08-85 36 0 2.710.4 36 0 2.410.4 36 0 2.7i0.4 355 2.010.4 355 2.110.4 355 2.010.4 10-15-85 1.2i0.3 10-22-85 359 1.010.3 358 1.110.3 36 0 350 1.010.3 351 1.110.4 354 1.210.4 10-29-85 2.510.4 11-05-85 366 2.2i0.4 36 8 1.Bi0.4 366 3.610.4 352 3.3i0.4 351 3.710.4 11-12-85 351 358 1.010.3 358 1.310.3 358 1.410.4 11-19-85 4.210.5 11-26-85 354 3.810.4 355 3.6t0.4 356 350 2.310.4 356 1.910.4 349 2.110.4 12-03-85 4.410.4 12-10-85 361 4.310.5 373 3.St0.4 366 351 3.310.4 36 0 2.8i0.4 351 3.210.4 12-17-85 4.610.5 12-23-85 307 4.210.5 318 3. 6i0. 5 307 410 1.910.4 431 2.0f0.4 408 2.310.4 12-31-85 2.6tl.2 2.310.9 2.711.2 4th Qtr. mean t s.d. a Iodine-131 concentrations are <7.0 x 10-2 pCi/m3 unless noted otherwise. Low volume due to loss of electricity; pug ran for 60.1 hours. c Elevated LLD and low volume due to blown fuse. Pug ran for 2.6 hours. Pump ran for 1.8 hours.
- Elevated LLDand Elevated LLD and lowlow volume volume due due to to blown blown fuse. fuse.
Pug ran for 18.8 hours. Unit replaced on 09-24-85. 8
MISSISSIPPI POWER AND LIGHT Table 4. Airborne Particulates and Iodine-131a Collection: Conginuous$ weekly exchange Units: 10- pCi/m Required LLD: Gross Beta - <1.0; I-131 - <7.0 AS-10 AS-11 Collection Gross Volyme Gross Volgme Beta Date (m ) Beta (m3) 01-08-85 356 3.3*0.4 358 1.5i0.4 01-15-85 357 1.Si0.3 357 1.810.3 01-22-85 356 1.2i0.4 356 0.9i0.3 01-29-85 357 1.110.3 357 1.li0.3 02-05-85 357 1.210.3 357 1.410.3 02-12-85 356 2.310.3 354 2.410.4 02-19-85 358 2.0i0.3 357 2.0i0.3 02-26-85 356 1.310.3 357 1.410.3 03-05-85 355 0.810.3 357 1.210.3 03-12-85 356 1.3i0.3 357 1.110.3 03-19-85 356 0.9*0.4 357 0.7*0.3 03-26-85 357 0.7i0.3 356 0.6i0.3 04-02-85 356 0.810.3 356 0.910.3 1st Qtr. mean i s.d. 1.41.7 1.310.5 04-09-85 358 0.6i0.3 357 <0.5 04-16-85 358 1.Di0.4 356 0.910.4 04-23-85 356 2.910.4 356 2.8i0.4 04-30-85 355 2.210.4 355 1.Si0.4 05-07-85 357 1.Si0.4 357 1.2*0.4 05-14-85 346 1.210.4 358 <0.6 05-21-85 369 1.9i0.4 355 1.7i0.4 05-28-85 354 2.910.4 357 2.210.4 06-04-85 355 2.4i0.4 356 2.110.4 06-11-85 359 2.9i0.4 358 3.Di0.4 06-18-85 356 2.4i0.4 355 2.210.4 06-25-85 356 2.8i0.4 356 2.610.4 07-02-85 357 2.7i0.4 286 3.310.5 4 2nd Qtr. mean i s.d. 2.110.8 2.1i0.8 a Iodine-131 concentrations are <7.0 x 10-2 pCi/m3 unless noted otherwise. 9
_ .~.
~.-
MISSISSIPPI POWER AND LIGHT Table 4. (continued) AS-10 AS-11 Gross Volume Gross Collection Volume Beta Date (md) Beta (mJ) 357 1.4i0.4 347 1.6i0.4 07-09-85 2.0f0.4 07-16-85 357 2.2i0.4 357 356 3.li0.4 356 1. 3i0. 3 07-23-85 <2.8 356 3.110.5 73b 07-30-85 1.110.4 08-06-85 358 1.li0.4 357 355 1.210.3 354 1.110.3 08-13-85 1.810.4 08-20-85 353 1.9i0.4 352 08-27-85 358 2.810.4 357 2.4i0.4 09-03-85 356 2.810.4 357 2.2i0.4 09-10-85 356 1.410.4 357 1.7i0.4 357 2.510.4 356 2.310.4 09-17-85 356 2.2i0.4 357 1.910.4 09-24-85 2. 0f 0. 3 10-01-85 356 1.610.3 357 2.110.7 1.810.4 3rd Qtr. mean i s.d. 10-08-85 355 3.2i0.4 357 2.710.4 10-15-85 359 3.210.3 357 3.210.3 10-22-85 356 1.210.3 357 0.9i0.3 10-29-85 357 1.410.4 357 1.410.4 11-05-85 357 2.510.4 357 2.210.4 11-12-85 358 4.0i0.4 356 3.610.4 11-19-85 355 1.810.4 357 1.110.3 11-26-85 358 4.0f0.4 357 3.910.4 12-03-85 36 1 2.510.4 357 2.4i0.4 i 12-10-85 354 4.0i0.4 357 4.210.4 l 2.710.4 12-17-85 355 3.3i0.4 357 12-23-85 307 3.910.5 309 3. 7t0. 5 12-31-85 416 2.510.4 404 2.210.4 4th Qtr. mean i s.d. 2.9tl.0 2.6fl.1 a Iodine-131 concentrations are <7.0 x 10-2 pCi/m3 unless noted otherwise. Low volume and elevated LLD due to pump malfunction; pump ran for 34.2 hrs. 10 _. _ _ _ _ _ _ _ _ _ _ _ _ _ __ _ _ _ . ~ _ _ _ __ _ _
~
^ MISSISSIPPI POWER AND LIGHT Table 5. Airborne Particulates Collection: Quarterly composites of weekly collections Units: pCi/mJ Volume Other Location Lab Code (m3) Cs-134 Cs-137 Gmunasa Required LLD 0.05 0.06 0.06 1st Quarter,1985 l AS-1 GAP-1265 4545 <0.05 <0.06 <0.06 AS-2 1266 4159 <0.05 <0.06 <0.06 AS-3 (C) 1267 4573 <0.05 <0.06 <0.06 AS-4 1268 4587 <0.05 <0.06 <0.06 AS-5 1269 4589 <0.05 <0.06 <0.06 AS-6 1270 4585 <0.05 <0.06 <0.06 AS-7 1271 4525 <0.05 <0.06 <0.06 AS-8 1272 4586 <0.05 <0.06 <0.06 AS-9 1273 4587 <0.05 <0.06 <0.06 AS-10 1274 4633 <0.05 <0.06 <0.06 AS-11 1275 4636 <0.05 <0.06 <0.06 2nd Quarter,1985 AS-1 GAP-1431 4628 <0.05 <0.06 <0.06 AS-2 1432 4133 <0.05 <0.06 <0. 06 AS-3(C) 1433 4636 <0.05 <0.06 <0.06 AS-4 1434 4655 <0.05 <0.06 <0.06 AS-5 1435 4634 <0.05 <0.06 <0.06 AS-6 1436 4567 <0.05 <0.06 <0.06 AS-7 1437 4638 <0.05 <0.06 <0.06 AS-8 1438 4445 <0.05 <0.06 <0.06 AS-9 1439 4626 <0.05 <0.06 <0. 06 AS-10 1440 4636 <0.05 <0.06 <0.06 AS-11 1441 4562 <0.05 <0.06 <0.06
- See Introduction.
11
MISSISSIPPI POWER AND LIGHT Table 5. Airborne Particuistes (continued) Volume Other Lab Code (m3) Cs-134 Cs-137 Gammasa Location Required LLD 0.05 0.06 0.06 3rd Quarter,1985 GAP-1528 4277 <0.05 <0.06 <0.06 AS-1 1529 4262 <0.05 <0.06 <0.06 AS-2 1530 4263 <0.05 <0.06 <0.06 AS-3(C) <0.06 <0.06 AS-4 1531 4249 <0.05 1532 3899 <0.05 <0.06 <0.06 AS-5 1533 4249 <0.05 <0.06 <0.06 AS-6 l 1534 4055 <0.05 <0.06 <0.06
- AS-7 AS-8 1535 3182 <0.05 <0.06 <0.06 1536 4180 <0.05 <0.06 <0.06 AS-9 AS-10 1537 4275 <0.05 <0.06 <0.06 AS-11 1538 3980 <0.05 <0.06 <0.06 4th Quarter,1985 AS-1 GAP-1701 4223 <0.05 <0.06 <0.06 AS-2 1702 4801 <0.05 <0.06 <0.06 1703 4320 <0.05 <0.06 <0.06 AS-3(C) <0.06 AS-4 1704 4642 <0.05 <0.06 AS-5 1705 4644 <0.05 <0.06 <0.06 AS-6 1706 4574 <0.05 <0.06 <0.06 AS-7 1707 4632 <0.05 <0.06 <0.06 AS-8 1708 4695 <0.05 <0.06 <0.06 AS-9 1709 4641 <0.05 <0.06 <0.06 AS-10 1710 4648 <0.05 <0.06 <0.06 AS-11 1711 46 39 <0.05 <0.06 <0.06 I
a See Introduction. I 1
'1 I
I i 12
MISSISSIPPI POWER AND LIGHT Table 6. Gamma Radiation, as Measured by TLDs Required by Technical Specifications Inner Ring, Within Two (2) Mile Radius a 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Date Annealed: 12-18-84 03-19-85 06-18-85 09-24-85 Date Read: 05-29-85 07-22-85 10-30-85 01-22-86 Location Average mR/ Quarter Mean i s.d. M-16 19.411.2 17.9i0.8 13.6fl.2 14.9i0.5 16.412.7 M-18 21.411.9 11.710.8 17.9*1.2 14.8i0.4 16.414.2 M-25 16.511.0 NDb 22.lil.6 15.2i2.3 17.913.7 M-27 20.111.2 25.812.5 21.4*1.3 14.7tl.6 20.Si4.6 M-28 19.811.6 17.711.5 22.8tl.0 15.210.6 18.913.2 M-30 19.011.0 14.4fl.5 16.611.2 15.510.1 16.412.0 M-41 9.911.0 4.810.8 12.410.8 11.210.5 9.6f3.3 M-42 13.9tl.1 8.410.9 11.8i0.5 11.610.4 11.4i2.3 M-43 NDb 17.310.6 16.2il.2 13.0i0.5 15.5i2.2 M-44 15.6tl.5 7.811.0 12.911.0 11.8tl.0 12.013.2 M-45 17.410.8 10.0i0.9 15.9i0.8 14.911.0 14.613.2 M-46 13.4*l.3 9.910.9 17.710.5 17.Dil.1 14.513.7 M-52 22.011.8 11.810.9 17.410.8 19.010.6 17.614.3 M-53 17.511.5 24.6f3.2 27.112.3 13.0*1.4 20.6t6.5 M-54 18.910.8 10.811.0 17.110.6 15.711.9 15.613.5 M-86 22.111.2 17.8tl.1 24.111.1 15.610.5 19.9i3.9 Mean i s.d. 17.813.5 14.0i6.1 17.914.4 14.612.0 16.114.5
- Required by Technical Specification 3.12.1.
ND = No data; TLDs lost in the field. 13
n .. .. MISSISSIPPI POWER AND LIGHT ;[ Table 6. Gamma. Radiation, as Measured by TLDs (continued) Outer Ring, Within Six (6) Mile Radius a 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Date Annealed: 12-18-84 03-19-85 06-18-85 09-24-85 Date Read: 05-29-85 07-22-85 10-30-85 01-22-86 Location Average mR/ Quarter Mean i s.d. M-36 18.111.1 10.510.8 19.3tl.5 16.012.6 16.0i3.9 M-40 #
- 19.811.2 16.2il.3 19.911.5 14.311.0 17.612.8 M-47 16.711.0 10.811.3 17.310.6 13.511.6 14.613.0 M-48 20.911.2 15.210.8 19.Sil.6 16.Si2.4 18.012.6 M-49 18.911.6 23.211.5 21.410.7 15.4i0.8 19.713.4 M-50 18.811.4 38.411.2 23.4tl.4 18.0il.3 24.619.5 M-51 20.811.8 18.9tl.4 22.Sil.5 21.3i2.0 20.911.5 M-55 23.611.4 14.611.4 20.611.0 16.411.1 18.814.1 M-56 19.011.8 11.910.7 20.111.4 18.311.0 17.3i3.7 M-57 15.312.0 NDb 21.511.2 15.8i0.8 17.Si3.4 M-58 21.511.1 14.011.5 22.411.3 16.0tl.1 18.5i4.1 M-59 17.911.4 8.911.1 19.4tl.2 13.3i0.4 14.914.8 M-88 10.811.3 9.110.8 17.611.3 11.411.7 12.213.7 M-89 2.2il.1 6.710.6 14.010.4 NDb 7.616.0 M-90 8.2il.0 9.111.0 20.410.9 13.7*1.2 12.815.6 M-91 11.111.1 9.911.0 18. 0t0. 7 16.li2.3 13.813.9
, Mean i s.d. 16.515.7 14.517.9 19.812.3 15.7f2.4 16.7i5.4 1 a Required by Technical Specification 3.12.1. No data; TLDs lost in the field. i l l 14
MISSISSIPPI POWER AND LIGHT n Table 6. Gamma. Radiation, as Measured by TLDs (continued) Special Interest Areasa 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Date Annealed: 12-18-84 03-19-85 06-18-85 09-24-85 Date Read: 05-29-85 07-22-85 10-30-85 01-22-86 , Location Average mR/ Quarter Mean i s.d. Population Centers or Residences M-01 22.211.9 NDb 19.511.1 18.712.6 20.111.8 M-07 21.011.3 14.611.4 16.310.6 15.410.7 16.8i2.9 M-09 NDb NDb 25.7*1.4 16.112.1 20.916.8 M-10 17.711.3 11.311.1 15.311.3 13.510.5 14.412.7 M-33 18.511.7 14.111.0 21.611.2 13.411.4 16.9i3.9 M-38 20.011.4 13.911.1 22.510.8 18.4i0.3 18.713.6 M-39 18.8 1.3 12.111.2 16.910.7 12.710.6 15.li3.2 Mean i s.d. 19.711.7 13.211.4 19.7i3.8 15.512.4 17.2i3.7 CONTROL M-14 20.011.5 19.311.5 20.111.0 20.8i0.9 20.010.6 SHIELD M-00 7.010.9 8.111.1 10.010.8 9.810.5 8.711.4 a Required by Technical Specification 3.12.1. ND = No data; TLDs lost in the field. f i 15
3 MISSISSIPPI POWER AND LIGHT Table 7. Gamma Radiation, as Measured by TLDs (continued) Not Required by Technical Specifications On-Site 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter 12-18-84 03-19-85 06-18-85 09-24-85 Date Annealed: 01-22-86 Date Read: 5-29-85 07-22-85 10-30-85 Average mR/ Quarter Mean i s.d. Location 14.9tl.6 13.811.5 17.611.1 14.010.9 15.lil.8 M-61 15.3*1.2 16.511.2 14.711.0 16.011.1 14.012.6 M-62 16.811.9 16.311.7 14.311.5 18.610.8 17.812.6 M-63 14.714.3 19.011.4 9.211.1 16.910.7 13.811.4 M-64 15.312.0 17.111.3 13.211.1 NDa 15.511.2 M-65 17.4i4.0 16.213.2 16.511.8 23.211.3 13.910.5 M-66 17.6t3.7 21.311.6 15.2il.5 20.311.2 13.811.1 M-67 30.2i16.8 15.811.0 37.611.3 50.511.7 17.113.1 M-68 34.2119.8 19.312.4 38.311.2 60.6i0.9 18.712.5 M-69 39.0i23.9 M-70 23.410.9 37.0i3.2 73.412.1 22.012.1 16.811.8 21.5tl.8 30.9tl.3 14.6i0.6 21.017.2 M-71 22.816.7 M-72 19.211.2 24.411.6 31.Si0.8 16. lil. 3 15.011.8 14.412.0 21.010.8 16.812.8 16.813.0 M-73 22.812.0 14.211.1 21.110.5 14.010.3 18.014.6 M-74 M-75 18.6tl.6 11.3il.3 17.410.7 13.7tl.7 15.213.4 M-76 21.911.3 15.111.6 18.110.5 14.0il.4 17.313.5 16.411.9 11.011.5 14.710.6 12.610.8 13.712.4 M-77 20.0il.6 19.911.3 15.310.9 15.410.7 17.612.7 M-78 16.411.5 18.521.8 16.210.7 16.5*2.0 16.911.1 M-79 22.411.5 23.7i2.4 24.310.8 19.311.1 22.412.2 M-80 22.915.3 M-81 17.6i2.0 29.6i2.5 24.411.1 20.111.7 23.311.6 15.0i0.6 22.810.9 19.111.6 20.013.8 M-82 23.914.0 M-83 25.911.1 27.9tl.7 23.lil.4 18.712.3 15.0f0.9 14.311.0 13.310.8 11.8tl.1 13.611.4 M-84 18.813.2 19.618.6 25.7i15.3 16.012.6 20.019.5 Mean s.d. a ND = No data; TLDs lost in the field. I i 16 1
MISSISSIPPI POWER AND LIGHT Table 7. Gamma Radiation, as Measured by TLDs (continued) Additional Locations, Within Fif teen (15) Mile Radius 1st Quarter 2nd Quarter 3rd Quarter 4th Quarter Dcte Annealed: 12-18-84 03-19-85 06-18-85 09-24-85 Date Read: 05-29-85 07-22-85 10-30-85 01-22-86 Location Average mR/ Quarter Mean i s.d. M-02 21.9tl.1 22.3*1.8 24.7t0.7 16.511.1 21.413.5 M-03 17.211.6 21.110.9 14.8tl.0 13.6i0.8 16.713.3 M-04 NDa 22.7tl.7 20.lil.2 18.Dio.3 20.312.4 M-05 19.311.1 15.6tl.6 18.li0.6 21.711.2 18.7*2.5 M-06 21.210.8 21.4f2.0 19.7*1.3 17.0tl.7 19.812.0 M-08 22.311.3 18.8tl.6 19.8tl.1 17.711.1 19.612.0 M-11 NDa 11.0f0.8 18.310.7 17.2il.4 15.513.9 M-12 23.Sil.0 18.2il.5 22.7tl.4 17.810.8 20.613.0 M-13 NDa 19.9tl.7 23.3i0.7 14.910.6 19.414.2 M-15 14.911.5 17.1*1.7 14.810.7 13.310.2 15.0tl.6 M-17 19.411.2 20.8tl.1 21.711.6 15.3i0.8 19.312.8 M-19 17.111.2 10.111.1 15.7tl.2 14.210.5 14.313.0 M-20 19.811.1 13.4tl.1 17.0tl.2 15. 4tl.0 16.4*2.7 M-21 20.111.4 17.2*1.3 14.2il.0 14.810.4 16.6i2.7 M-22 20.610.9 18.911.2 NDa 14.910.2 18.112.9 M-23 18.7t0.8 13.910.9 14.110.8 14.2i0.8 15.212.3 M-24 13.611.2 N0a NDa 13.411.4 13.510.1 M-26 17.811.0 20.411.2 19.0il.2 14.611.8 18.012.5 M-29 20.211.4 23.7tl.4 21.7i0.9 14.lil.5 19.914.1 M-34 20.211.9 NDa 26.511.9 15.811 4 20.815.4 M-35 14.511.4 13.011.3 19.311.0 ,, 13.6i0.6 15.112.9 M-37 20.Di0.8 14.611.8 26.5i0.5 14.410.7 18.915.7 M-87 NDa 21.711.2 25.210.6 18.311.7 21.713.4 Mean i s.d. 19.li2.7 17.914.0 19.9t4.0 15.712.1 18.0t3.6 DUPLICATE TLDs M-31 20.310.8 23.8i2.2 20.8tl.3 15.210.5 20.0t3.6 M-32 18.911.4 20.0il.9 23.211.3 14.8i0.6 19.213.5 M-60 20.511.4 11.110.7 21.9i0.9 16.0f0.6 17.414.9 M-85 17.511.4 21.711.1 17.0t0.9 14.0f0.5 17.613.2 Mean i s.d. 19.311.4 19.115.6 20.712.7 15.0i0.8 18.513.6 a ND = No data; TLDs lost in the field. 17 l
MISSISSIPPI POWER AND LIGHT Table 8. Cistern Water Collection: Monthly Units: pCi/1 Mn-54, Co -58. -60, Nb-95, Fe -59, Collection Lab Gross Cs-134, Zn-65, Date Code Beta I-131 Cs-137 La-140 Zr-95 Ba-140 Required LLD 4 1. 0 18 15 30 60 Will Cist 01-08-85 GWW-101 1.010.4 <1. 0 <18 <15 <30 <60 02-11-85 510 1.210.4 <2.4a <18 <15 <30 <60 03-07-85 787 1.110.4 < 1. 0 <18 <15 <30 <60 03-07-85 788 (GG) 1.310.4 < 1. 0 <18 <15 <30 <60 04-11-85 1357 1.110.3 <1. 0 <18 <15 <30 <60 05-13-85 1743 1.210.4 <1. 0 <18 <15 <30 <60 06-07-85 2081 1.210.4 <1.0 <18 <15 <30 <60 06-07-85 2082 (GG) 1.510.4 <1. 0 <18 <15 <30 <60 07-11-85 2610 1.610.3 < 1. 0 <18 <15 <30 <60 08-13-85 2966 1.610.4 <1. 0 <18 <15 <30 <60 09-13-85 3408 2.610.5 <1. 0 <18 <15 <30 <60 09-13-85 3409(GG) nab <1. 0 nab nab nab nab 10-15-85 3857 1.610.4 <1. 0 <18 <15 <10 <60 11-14-85 4281 1.110.4 <1. 0 <18 <15 <30 <60 12-11-85 4591 0.810.4 <1. 0 <18 <15 <30 <60 12-11-85 4592 (GG) 0.910.4 <1. 0 <18 <15 <30 <60 Trim Cist 01-07-85 GWW-100 1.110.4 <1. 0 <18 <15 <30 <60 02-11-85 509 1.010.4 <1. 0 <18 <15 <30 <60 03-07-85 785 0.810.4 <1. 0 <18 <15 <30 <60 03-07-85 786 (GG) 1.010.4 < 1. 0 <18 <15 <30 <60 04-11-85 1356 3.410.6 <1. 0 <18 <15 <30 <60 05-13-85 1744 3.310.5 <1. 0 <18 <15 <30 <60 06-07-85 2083 3.310.5 <1. 0 <18 <15 <30 <60 06-07-85 2084 (GG) 3.210.5 <1. 0 <18 (15 <30 <60 07-11-85 2611 0. 4i0. 2 <1. 0 <18 <15 <30 <60 08-13-85 2967 <0.6 <1. 0 <18 <15 <30 <60 09-13-85 3410 1.810.4 <1. 0 <18 <15 <30 <60 09-13-85 3411(GG) nab < 1. 0 nab nab nab nab 10-15-85 3558 <0.6 <1. 0 <18 <15 <30 <60 11-14-85 4282 1.510.4 < 1. 0 <18 <15 <30 <60 j 12-11-85 4593 1.210.4 <1. 0 <18 <15 <30 <60 12-11-85 4594(GG) 1.110.4 < 1. 0 <18 <15 <30 <60 a Elevated LLD due to delay in counting. NA = Not analyzed; only I-131 analysis requested for these replicate samples. i 18 l
MISSISSIPPI POWER AND LIGHT Table 8. Cistern Water (continued) QUARTERLY COMPOSITES OF MONTHLY COLLECTIONS Compositing Will Cist Trim Cist Period Lab Code H-3 Lab Code H-3 Required LLD 330 330 j 1st Quarter,1985 GWW-984 <330 GWW-981 <330 1st Quarter,1985 985 (GG) <330 982,3 (GG) <330 2nd Quarter,1985 GWW-2076 <330 GWW-2078,9 <330 . 2nd Quarter,1985 2077(GG) <330 2080(GG) <330 3rd Quarter,1985 GWW-3449 <330 GWW-3447 <330 3rd Quarter,1985 3450(GG) <330 3448 (GG) <330 4th Quarter,1985 GWW-4658 <330 GWW-4660,1 <330 4th Quarter,1985 4659(GG) <330 4662 (GG) <330 1 1 19
MISSISSIPPI POWER AND LIGHT Table 9. Surface Water Collection:- Monthly l Units: pCi/l Mn-54, Co-58,-60, Nb-95, Fe-59, Collection Lab Cs-134, Zn-65, Date Code Cs-137 La-140 Zr-95 Ba-140 Required LLD 18 15 30 60 MR UP (C) 01-17-85 GSW-214 <18 <15 <30 <60 02-12-85 520 <18 <15 <30 <60 03-14-85 1036 <18 <15 <30 <60 03-14-85 1037 (GG) <18 <15 <30 <60 04-18-85 1473 <18 <15 <30 <60 05-16-85 1812 <18 <15 <30 <60 06-13-85 2173,4 <18 <15 <30 <60 06-13-85 2176(GG) <18 <15 <30 <60 07-18-85 2714 <18 <15 <30 <60 08-21-85 3124,5 <18 <15 <30 <60 09-13-85 3451 <18 <15 <30 <60 09-13-85 3452(GG) <18 <15 <30 <60 10-17-85 3924 <18 <15 <30 <60 11-14-85 4312 <18 <15 <30 <60 12-12-85 4649,50 <18 <15 <30 <60 12-12-85 4651(GG) <18 <15 <30 <60 MR DOWN 01-17-85 GSW-215 <18 <15 <30 <60 02-12-85 521 <18 <15 <30 <60 03-14-85 1038 <18 <15 <30 <60 03-14-85 1039 (GG) <18 <15 <30 <60 04-18-85 1474 <18 <15 <30 <60 05-16-85 1813 <18 <15 <30 <60 06-13-85 2175 <18 <15 <30 <60 06-13-85 2177(GG) <18 <15 <30 <60 07-18-85 2715 <18 <15 <30 <60 08-21-85 3126 <18 <15 <30 <60 09-13-85 3453 <18 <15 <30 <60 09-13-85 3454(GG) <18 <15 <30 <60 10-17-85 3925 <18 <15 <30 <60 11-14-85 4313 <18 <15 <30 <60 12-12-85 4652 <18 <15 <30 <60 12-12-85 4653 (GG) <18 <15 <30 <60 20
MISSISSIPPI POWER AND LIGHT Table 9. Surf ace Water (continued) 4 QUARTERLY COMPOSITES OF MONTHLY COLLECTIONS Compositing MR UP MR DOWN Period Lab Code H-3 Lab Code H-3 Required LLD 330 330 1st Quarter, 1985 GSW-977 <330 GSW-979 <330 1st Quarter, 1985 978 (GG) <330 980(GG) <330 2nd Quarter,1985 GSW-2178 <330 GSW-2179 <330 2nd Quarter, 1985 2180(GG) <330 2181 (GG) <330 i 3rd Quarter, 1985 GSW-3455 <330 GSW-3457 <330 3rd Quarter,1985 3456 (GG) <330 3458 <330 4th Quarter,1985 GSW-4654 <330 GSW-4656 <330 4th Quarter, 1985 4655(GG) <330 4637 (GG) <330 T 1 21
I l MISSISSIPPI POWER AND LIGHT Table 10. Discharge. Basin Watera Collection: Monthly Units: pCi/1 Mn-54, Co-58,-60, Nb-95, Fe-59, Collection Cs-134, Zn-65, Date Lab Code Cs-137 La-140 Zr-95 8a-140 Required LLD 18 15 30 60 January, 1985 GDBW-481 <18 <15 <30 <60 February, 1985 843 <18 <15 <30 <60 March, 1985 1306 <18 <15 <30 <60 March, 1985 1307(GG) <18 <15 <30 <60 April ,1985 1779 <18 <15 <30 <60 May, 1985 2019 <18 <15 <30 <60 June,1985 2575 <18 <15 <30 <60 June, 1985 2576 (GG) <18 <15 <30 <60 July, 1985 2915 <18 <15 <30 <60 August, 1985 3459,60 <18 <15 <30 <60 September, 1985 3815 <18 <15 <30 <60 September,1985 3816 (GG) <18 <15 <30 <60 October, 1985 4243 <18 <15 <30 <60 October,1985 4244 (GG) <18 <15 <30 <60 November,1985 4581 <18 <15 <30 <60 December,1985 5036 <18 <15 <30 <60 December,1985 5037 (GG) <18 <15 <30 <60 QUARTERLY COMPOSITES OF MONTHLY SAMPLES Composite Period Lab Code H-3 Required LLO 330 1st Qtr., 1985 GDBW-1308 <330 1st Qtr., 1985 1309 (GG) <330 2nd Qtr.,1985 2573 420i90 2nd Qtr. ,1985 2574(GG) 370i90 3rd Qtr.,1985 3817 520i110 3rd Qtr. ,1985 3818 (GG) 5501110 4th Qtr., 1985 5038 4801120 4th Qtr., 1985 5039 (GG) 320t120 a This is a surf ace water sample as defined by Technical Specification 3.12.1. 22
-. . -. .. _. . ~--. . -. ..
MISSISSIPPI POWER AND LIGHT Table 11. Well Water Collection': Quarterly Units: pCi/1 Mn-54 Co-58,-60 Cs-134, Fe-59, Collection Nb-95, Zn-65, Period Lab Code H-3 Cs-137 La-140 Zr-95 Ba-140 Required LLD 330 18 15 30 60 PG WELL (C) . 01-08-85 GWW-134 <330 <18 <15 <30 <60 04-11-85 1388 <330 <18 <15 <30 <60 04-11-85 1391 (GG) <330 <18 <15 <30 <60 07-11-85 2649 <330 <18 <15 <30 <60 10-16-85 3910 <330 <18 <15 <30 <60 GGMP WELL 01-07-85 GWW-133 <330 <18 <15 <30 <60 04-11-85 1389 <330 <18 <15 <30 <60 04-11-85 1392,3 (GG) <330 <18 <15 <30 <60 07-11-85 2648 <330 <18 <15 <30 <60 10-16-85 3909 <330 <18 <15 <30 <60 DATSAM - LAKE BRUIN STATE PARK 01-09-85 GWW-146 <330 <18 <15 <30 <60 04-10-85 1390 <330 <18 <15 <30 <60 04-10-85 1394 (GG) <330 <18 <15 <30 <60 07-10-85 2647 <330 <18 <15 <30 <60 10-15-85 3908 <330 <18 <15 <30 <60 23
l MISSISSIPPI POWER AND LIGHT Table 12. Bottom Sediments Collection: Semiannually thits: pCi/g dry weight Collection Collection Lab I.D. Date Code Cs-134 Cs-137 Co-58 Co-60 Mn-54 K-40 Required LLD 0.15 0.18 0.15 0.15 0.15 Sed. Cont. 05-16-85 CBS-406 <0.15 <0.18 <0.15 <0.15 <0.15 15.410.5 Sed. Bar 05-16-85 407 <0.15a 0. 2410. 03a 1.05i0.07a 0.5410.04a 2.6210.08a 16.010.9a Sed. Ham. 05-16-85 408 <0.15 <0.18 <0.15 <0.15 <0.15 14.910.4 Sed. Bar 08-21-85 465 <0.15 <0.18 0.1710.06 0.2310.04 0.6010.06 16.110.8 Sed. Bar 09-13-85 SPS-1735 <0.15 <0.18 <0.15 <0.15 0.3110.02 Sed. Bar 10-17-85 SPS-1907 <0.15 <0.18 <0.15 <0.15 <0.15 Sed. Bar 11-14-85 GBS-541 <0.15 <0.18 0.2610.02 0.6910.02 1.6410.03 13.310.4 , 11-14-85 542 <0.15 <0.18 0.2610.02 0.6210.03 1.6010.05 13.6i0.5 l Sed. Bar (GG) Sed. Ham. 11-14-85 543 <0.15 0.1910.01 <0.15 <0.15 <0.15 14.810.4 11-14-85 544 <0.15 <0.18 <0.15 <0.15 <0.15 13.6i0.4 Sed. Ham. (GG) Sed. Cont. 11-14-85 545 <0.15 <0.18 <0.15 <0.15 <0.15 10.610.4 11-14-85 546,7 <0.15 <0.18 <0.15 <0.15 <0.15 10.010.1 Sed. Cont. (GG) a These results confirmed by reanalysis. ,
n- - y - - . MISSISSIPPI POWER AND LIGHT Table 13. Milk Collection: Monthly; twice a month when animals are on pasture. Units: pCi/1 Collection Date Lab Code I-131 Cs-134 Cs-137 8a-140 La-140 Required LLD 1.0 15 18 60 15 Alcorn State University (C) 01-08-85 GMI-55 <1. 0 <15 <18 <60 <15 01-22-85 78 <1. 0 <15 <18 <60 <15 02-06-85 131 <1. 0 <15 <18 <60 <15 02-20-85 157 <1. 0 <15 <18 <60 <15 03-05-85 199 <1. 0 <15 <18 <60 <15 03-05-85 200(GG) <1. 0 <15 <18 <60 <15 03-18-85 236 <1. 0 <15 <18 <60 <15 04-02-85 272 <1. 0 <15 <18 <60 <15 04-16-85 338 <1. 0 <15 <18 <60 <15 05-06-85 408 <1. 0 <15 <18 <60 <15 05-20-85 517 <1. 0 <15 <18 <60 <15 4 06-04-85 620 <1. 0 <15 <18 <60 <15 06-04-85 621(GG) <1. 0 <15 <18 <60 <15 06-25-85 773 <1. 0 <15 <18 <60 <15 07-02-85 898 <1. 0 <15 <18 <60 <15 07-16-85 958 <1. 0 <15 <18 <60 <15
- 07-16-85 959(GG) <1. 0 <15 <18 <60 <15 08-07-85 1150 <1. 0 <15 <18 <60 <15 08-20-85 1226 <1. 0 <15 <18 <60 <15 09-10-85 1389 <1. 0 <15 <18 <60 <15
! 09-20-85 1465 <1. 0 <15 <18 <60 <15 09-20-85 1466 (GG) <1. 0 <15 <18 <60 <15 10-08-85 1582 <1. 0 <15 <18 <60 <15
- 10-22-85 1674 <1. 0 <15 <18 <60 <15 11-12-85 1771 <1. 0 <15 <18 <60 <15
- 11-19-85 1785 <1. 0 <15 <18 <60 <15 i 12-10-85 1855 <1. 0 <15 <18 <60 <15 12-10-85 1856 (GG) <1. 0 <15 <18 <60 <15 4 12-18-85 1877 <1. 0 <15 <18 <60 <15 l l
25
-w
.\
MISSISSIPPI POWER AND LIGHT Table 14. Vegetation Collection: Monthly, when available lhlts: pCi/g wet weight Collection Collection Lab Other I . D. Date Code Sanple Type Cs-134 Cs-137 I-131 Gansnasa Required LLD 0. % 0 0.080 0.060 0.080 Control Veg Cont 85-07 01-07-85 GVE-538 Kale <0.060 <0.080 <0.060 <0.080 Veg Cont 85-08 01-07-85 539 Turnips <0.060 <0.080 <0.060 <0.080
. Veg Cont 85-09 01-07-85 54 0 Mustard <0.060 <0.080 <0.060 <0.080 Veg Cont 85-16 02-06-85 551 Kale <0.060 <0.080 <0.060 <0.080 Veg Cont 85-16 (GG) 02-06-85 552 Kale <0.060 <0.080 <0.060 <0.080
- y Veg Cont 85-17 02-06-85 553 Collards <0.060 <0.080 <0.060 <0.080 Veg Cont 85-18 02-06-85 554 Cabbage <0.060 <0.080 <0.060 <0.080 Veg Cont 85-18 (GG) 02-06-85 555 Cabbage <0.060 <0.080 <0.060 <0.080 ,
Veg Cont 85-19 03-05-85 558 Skunk Cabbage <0.060 <0.080 <0.060 <0.080 i Veg Cont 85-20 03-05-85 559 Collards <0.060 <0.080 <0.060 <0.080 Veg Cont 85-21 03-05-85 560 Redtop Bush Leaves <0.060 <0.080 <0.060 <0.080 Collards <0.060 <0.080 <0.060 <0.080 Veg Cont 85-34 04-08-85 581 Veg Cont 85-34 (GG) 04-08-85 582 Collards <0.060 <0.080 <0.060 <0.080 Veg Cont 85-35 04-08-85 583 Kale <0.060 <0.080 <0.060 <0.080 Veg Cont C5-35 (GG) 04-08-85 584 Kale <0.060 <0.080 <0.060 <0.080 Veg Cont 85-36 04-08-85 585 Rape <0.060 <0.080 <0.060 <0.080 , Veg Cont 85-36 (GG) 04-08-85 586 Rape <0.060 <0.080 <0.060 <0.080 Veg Cont 85-43 05-08-85 594 Mustard <0.060 <0.080 <0.060 <0.080 Veg Cont 85-44 05-08-85 595 Cauliflower <0.060 <0.080 <0.060 <0.080 , Veg Cont 85-45 05-08-85 596 Rape <0.060 <0.080 <0.060 <0.080 Veg Cont 85-46 06-04-85 597 Collards <0.060 <0.080 <0.060 <0.080 Veg Cont 85-46 (GG) 06-04-85 598,9 Collards <0.060 <0.080 <0.060 <0.080 Veg Cont 85-47 06-04-85 600 Kale <0.060 <0.080 <0.060 <0.080 1 Veg Cont 85-47 (GG) 06-04-85 601 Kale <0.060 <0.080 <0.060 <0.080
- Veg Cont 85-48 06-04-85 602 Mustard <0.060 <0.080 <0.060 <0.080 ,
Veg Cont 85-48 (GG) 06-04-85 603 Mustard <0.060 <0.080 <0.060 <0.080 j ) a See Introduction.
MISSISSIPPI POWER AND LIGHT Table 14. Vegetation (continued) Collection Collection Lab Other I . D. Date Code Sanple Type Cs-134 Cs -137 I-131 Gansnasa Required LLD 0.009 0.080 0.060 ~0.080 Control (continued) <0.080 Veg Cont 85-58 07-09-85 GVE-623 Turnips <0.060 <0.080 <0.060 Veg Cont 85-59 07-09-85 624 Kale <0.060 <0.080 <0.060 <0.080 Veg Cont 85-60 07-09-85 625 Mustard <0.060 <0.080 <0.060 <0.080 Veg Cont 85-64 08-06-85 701 Sweet Potato Leaves <0.060 <0.080 <0.060 <0.080 Veg Cont 85-64 (GG) 08-06-85 709 Sweet Potato Leaves <0.060 <0.080 <0.060 <0.080 Veg Cont 85-65 08-06-85 702 Co11ards <0.060 <0.080 <0.060 <0.080 Veg Cont 85-65 (GG) 08-06-85 710 Collards <0.060 <0.080 <0.060 <0.080 Veg Cont 85-66 08-06-85 703 Okra Leaves <0.060 <0.080 <0.060 <0.080 m Veg Cont 85-66 (GG) 08-06-85 711 Okra Leaves <0.060 <0.080 <0.060 <0.080 Veg Cont 85-73 09-10-85 792,3 Peanut Plant Leaves <0.060 <0.080 <0.060 <0.080
- Veg Cont 85-74 09-10-85 794 Sweet Potato leaves <0.060 <0.080 <0.060 <0.080 Veg Cont 85-75 09-10-85 795 Okra Leaves <0.060 <0.080 <0.060 <0.080 Veg Cont 85-91 11-12-85 869 Rape <0.060 <0.080 <0.060 <0.080 Veg Cont 85-92 11-12-85 870,1 Collards <0.060 <0.080 <0.060 <0.080 Veg Cont 85-93 11-12-85 872 Turnips <0.060 <0.080 <0.060 <0.080 Veg Cont 85-97 12-10-85 876 Rape <0.060 <0.080 <0.060 <0.080 Veg Cont 85-97 (GG) 12-10-85 883 Rape <0.060 <0.080 <0.060 <0.080 Veg Cont 85-98 12-10-85 877 Kale <0.060 <0.080 <0.060 <0.080 Veg Cont 85-98 (GG) 12-10-85 884 Kale <0.060 <0.080 <0.060 <0.080 Veg Cont 85-99 12-10-85 878 Mustard <0.060 <0.080 <0.060 <0.080 i
Yeg Cont 85-99 (GG) 12-10-85 885 Mustard <0.060 <0.080 <0.060 <0.080 a See Introduction. s }
s MISSISSIPPI POWER AND LIGHT Table 14. Vegetation (continued) i Collection Collection Lab Other i- I . D. Date Code Sample Type Cs-134 Cs-137 I-131 Gannasa Required LLD 0.060 0.080 0.060 0.080 i Sector J Veg 85-04 01-07-85 GVE-535 Kale <0.060 <0.080 <0.060 <0.080 ' Veg 85-05 01-07-85 536 Mustard greens <0.060 <0.080 <0.060 <0.080 Veg 85-06 01-07-85 537 Turnip greens <0.060 <0.080. <0.060 <0.080 f Veg 85-10 02-06-85 541 Grass <0.060 <0.080 <0.060 <0.080 ! Veg 85-10 (GG) 02-06-85 542 Grass <0.060 <0.080 <0.060 <0.080 j Veg 85-11 02-06-85 543 Rape <0.060 <0.080 <0.060 <0.080 i Veg 85-12 02-06-85 544,5 Kale <0.060 <0.080 <0.060 <0.080 E$ Veg 85-12 (GG) 02-06-85 546 Kale <0.060 <0.080 <0.060 <0.080 i Veg 85-25 03-06-85 564 Skunk cabbage <0.060 <0.080 <0.060 <0.080 t Veg 85-26 03-06-85 565 Hay <0.060 <0.080 <0.060 <0.080 ', Veg 85-27 03-06-85 566 Leaves <0.060 <0.080 <0.060 <0.080 .' Veg 85-31 04-08-85 574 Red clover <0.060 <0.080 <0.060 <0.080 i Veg 85-31 (GG) 04-08-85 575 Red clover <0.060 <0.080 <0.060 <0.080 i Veg 85-32 04-08-85 576 Cow vetch <0.060 <0.080 <0.060 <0.080 . Veg 85-32 (GG) 04-08-85 577 Cow wetch <0.060 <0.080 <0.060 <0.080 i Veg 85-33 04-08-85 578,9 Skunk caobage <0.060 <0.080 <0.060 <0.080 Veg 85-33 (GG) 04-08-85 580 Skunk cabbage <0.060 <0.080 <0.060 <0.080 j Veg 85-37 05-08-85 588 Brussel sprouts <0.060 <0.080 <0.060 <0.080 l Veg 85-38 05-08-85 589 Broccoli <0.060 <0.080 <0.060 <0.080 i Veg 85-39 05-08-85 590 Rape <0.060 <0.080 <0.060 <0.080 Veg 85-49 06-05-85 604 Broccoli <0.060 <0.080 <0.060 <0.080 i Veg 85-49 (GG) 06-05-85 605 Broccoli <0.060 <0.080 <0.060 <0.080 Veg 85-50 06-05-85 606 Mustard <0.060 <0.080 <0.060 <0.080 l <0.060 <0.080 Veg 85-50 (GG) 06-05-85 607 Mustard <0.060 <0.080 i Veg 85-51 06-05-85 608 Cabbage <0.060 <0.080 <0.060 <0.080 j Veg 85-51 (GG) 06-05-85 609.10 Cabbage <0.060 <0.080 <0.060 <0.080 4 j a See Introduction. , i I L-_- _ - - _- __ _ __ _ _ _ . _
*1 l
MISSISSIPPI POWER AND LIGHT Table 14. Vegetation (continued) Collection Collection Lab Other I.D. Date Code Sanple Type Cs-134 Cs-137 I-131 Gamasa Required LLO 0.060 0.080 0.060 0.080 Sector J (continued) <0.060 <0.080 <0.060 <0.080 Veg 85-55 07-09-85 GVE-619 Co11ards Veg 85-56 07-09-85 620 Rape <0.060 <0.080 <0.060 <0.080 Veg 85-57 07-09-85 621,2 Rutabaga <0.060 <0.080 <0.060 <0.080 08-07-85 712 Pear Leaves <0. %0 <0.080 <0.060 <0.080 Veg 85-67 Veg 85-67 (GG) 08-07-85 719 Pear Leaves <0.060 <0.080 <0.060 <0.080 08-07-85 Rape <0.060 <0.080 <0.060 <0.080 Veg 85-68 71 3 Weg 85-68 (GG) 08-07-85 720 Rape <0.060 <0.080 <0.060 <0.080 m <0.080
- Veg 85-69 08-07-85 714 Rutabaga <0.060 <0.080 <0.060 Veg 85-69 (GG) 08-07-85 721 Rutacaga <0.060 <0.080 <0.060 <0.080 '
09-10-85 786 Cottonwood Leaves <0.060 <0.080 <0.060 <0.080 Veg 85-103 - 09-10-85 787 China Berry Grass <0.060 <0.080 <0.060 <0.080 Veg 85-104 <0.080 09-10-85 788 Pecan Leaves <0.060 <0.080 <0.060 Veg 85-105 <0.080 Veg 85-85 11-12-85 864 Kale <0.060 <0.080 <0.060 11-12-85 863 Turnips <0.060 <0.080 <0.060 <0.080 Veg 85-86 <0.080 11-12-85 865 Rape <0.060 <0.080 <0.060 Veg 85-87 <0.060 <0.080 Veg 85-100 12-10-85 879 White Radish <0.060 <0.080 12-10-85 886 White Radish <0.060 <0.080 <0.060 <0.080 Veg 85-100 (GG) <0.080 12-10-85 880 Rutabaga <0.060 <0.080 <0.060 Veg 85-101 <0.080 Veg 85-101 (GG) 12-10-85 887 Rutabaga <0.060 <0.080 <0.060 12-10-85 881,2 Turnips <0.060 <0.080 <0.060 <0.080 Veg 85-102 <0.060 <0.080 Veg 85-102 (GG) 12-10-85 888 Turnips <0.060 <0.080 a See Introduction.
0 ' MISSISSIPPI POWER AND LIGHT Table 14. Vegetation (continued) Collection Collection Lab Other I.D. Date Code Sanple Type Cs-134 Cs-137 I-131 Gannasa Required LLD 0.060 0.080 0.060 0.080 Sector R Veg 85-01 01-07-85 GVE-531 Mustard greens <0.060 <0.080 <0.060 <0.080 Veg 85-02 01-07-85 532 Radish <0.060 <0.080 <0.060 <0.080 Veg 85-03 01-07-85 533,4 Ikarf Essex rape <0.060 <0.080 <0.060 <0.080 Veg 85-13 02-06-85 547 Assorted leaves <0.060 <0.080 <0.060 <0.080 Veg 85-13 (GG) 02-06-85 548 Assorted leaves <0.060 <0.080 <0.060 <0.080 Veg 85-14 02-06-85 549 Magnolia leaves <0.060 <0.080 <0.060 <0.080 i Veg 85-15 02-06-85 550 Grass <0.060 <0.080 <0.060 <0.080 Hay <0.060 <0.080 <0.060 <0.080 8 Veg 85-22 03-06-85 561 Spring grass <0.060 <0.080 <0.060 <0.080 Veg 85-23 03-06-85 562 Veg 85-24 03-06-85 563 Wild mustard <0.060 <0.080 <0.060 <0.080 Veg 85-28 04-08-85 567,8 Red clover <0.060 <0.080 <0.060 <0.080 j Veg 85-28 (GG) 04-08-85 569 Red clover <0.060 <0.080 <0.060 <0.080 Veg 85-29 04-08-85 570 Skunk cabbage <0.060 <0.080 <0.060 <0.080 Veg 85-29 (GG) 04-08-85 571 Skunk cabbage <0.060 <0.080 <0.060 <0.080 Veg 85-30 04-08-85 572 Cow vetch <0.060 <0.080 <0.060 <0.080 i Veg 85-30 (GG) 04-08-85 573 Cow vetch <0.060 <0.080 <0.060 <0.080 Veg 85-40 05-08-85 591 Brussel sprouts <0.%0 <0.080 <0.060 <0.080 i Veg 85-41 05-08-85 592 Mustard <0.060 <0.080 <0.060 <0.080
- Veg 85-42 05-08-85 593 Rape <0.060 <0.080 <0.060 <0.080
- Veg 85-52 06-05-85 611 Broccoli <0.060 <0.080 <0.060 <0.080
- Veg 85-52 (GG) 06-05-85 612 Broccoli <0.060 <0.080 <0.060 <0.080 Veg 85-53 06-05-85 613 Rape <0.060 <0.080 <0.060 <0.G30 Veg 85-53 (GG) 06-05-85 614 Rape <0.060 <0.080 <0.060 <0.080
. Veg 85-54 06-05-85 615 Mustard <0.060 <0.080 <0.060 <0.080
- Veg 85-54 (GG) 06-05-85 616 Mustard <0.060 <0.080 <0.060 <0.080 a
See Introduction. i 1 - - - - - - . - _ _ _ - - - - - - - - - - - - - - - - - - - - - - . - - - _ _ _ _ , .
k l 4 MISSISSIPPI POWER AND LIGHT Table 14. Vegetation (continued) Collection Collection Lab Other
- 1. D. Date Code Suple Type Cs-134 Cs-137 I-131 Gannasa Required LLD 0.060 0.080 0.060 0.080 l Sector R (continued) 3 Veg 85-61 07-09-85 GVE-626 Rape <0.060 <0.080 <0.060 <0.080 i Veg 85-62 07-09-85 627 Rutabaga <0.060 <0.080 <0.060 <0.080 i Veg 85-63 07-09-85 628 Broadleaf Pea <0.060 <0.080 <0.060 <0.080
- Veg 85-70 08-07-85 715,6 Johnson Grass <0.060 <0.080 <0.060 <0.080 i
Veg 85-70 (GG) 08-07-85 722 sbhnson Grass <0.060 <0.080 <0.060 <0.080 Veg 85-71 08-07-85 717 Kudzu <0.060 <0.080 <0.060 <0.080 ! Veg 85-71 (GG) 08-07-85 723 Kudzu <0.060 <0.080 <0.060 <0.080 t Veg 85-72 08-07-85 718 Rape <0.060 <0.080 <0.060 <0.080 Veg 85-72 (GG) 08-07-85 724 Rape <0.060 <0.080 <0.060 <0.080 , Veg 85-106 09-10-85 789 1%can Leaves <0.060 <0.080 <0.060 <0.080 ! Veg 85-107 09-10-85 790 China Berry leaves <0.060 <0.080 <0.060 <0.080 4 Veg 85-108 09-10-85 791 Kudzu Leaves <0.060 <0.080 <0.060 <0.080 4 Veg 85-88 11-12-85 866 Box Elder Leaves <0.060 <0.080 <0.060 <0.080
$ Yeg 85-89 11-12-85 867 Mustard <0.060 <0.080 <0.060 <0.080 Veg 85-90 11-12-85 868 Dogwood Leaves <0.060 <0.080 <0.060 <0.080 Veg 85-94 12-10-85 873 Mustard <0.060 <0.080 <0.060 <0.080 i Veg 85-95 12-10-85 874 White Radish <0.060 <0.080 <0.060 <0.080
- Veg 85-96 12-10-85 875 Kale <0.060 <0.080 <0.060 <0.080 1
} l a See Introduction. i l .i o s 1
MISSISSIPPI POWER AND LIGHT Table 15. Fish Collection: Semiannually Units: pCi/g wet weight Mn-54, Collection Collection Co-58.-60, Fe-59, Site Date Lab Code Sanple Type Cs-134 Cs-137 Zn-65 I Required LLD 0.13 0.15 0.26 MR Upstream 04-16-85 GF-539,40 Catfish <0.13 <0.15 <0.26 MR Upstream (GG) 04-16-85 GF-541 Catfish <0.13 <0.15 <0.26 m MR Downstream 04-16-85 GF-542 Catfish <0.13 <0.15 <0.26 N MR Downstream (GG) 04-16-85 GF-543 Catfish <0.13 <0.15 <0.26 MR Upstream 10-17-85 GF-720 Catfish <0.13 <0.15 <0.26 MR Upstream (GG) 10-17-85 GF-721 Catfish <0.13 <0.15 <0.26 MR Downstream 10-17-SS GF-722 Catfish <0.13 <0.15 <0.26 MR Downstream (GG) 10-17-85 GF-723 Catfish <0.13 <0.15 <0.26 4 h d
MISSISSIPPI POWER AND LIGHT Table 16. Meat Collection: Annually
- Units
- pCi/g wet weight Mn-54, .
Collection Collection Co-58,-60, Fe-59, Site Date Lab Code Sanple Type Cs-134 Cs-137 Zn-65 Required LLD 0.13 0.15 0.26 Sector M, 3.2-4.8 km 11-25-85 SPS-1900 Venison <0.13 <0.15 <0.26 j 4 4 s l
MISSISSIPPI POWER AND LIGiT Table 17. Special Sanples Collection: Annually Units: pCi/g wet weight or pCi/1 (Effluent) Mn-54, Collection Collection Lab Sanple Co-58, -60 Fe-59, I . D. Date Code Type Cs-134 Cs-137 Zn-65 Required LLD - Basin 8 sanples 0.13 0.15 0.26 Influent End 08-08-85 SPS-1702 Sediment <0.13 <0.15 <0.26 Basin B 09-10-85 SPS-1728 Sediment <0.13 <0.15 <0.26 Influent End 10-08-85 SPS-1800 Sediment <0.13 <0.15 <0.26 Basin B 11-27-85 SPS-1869 Sediment <0.13 <0.15 <0.26 Basin 8 12-04-85 SPS-1883 Sediment <0.13 <0.15 <0.26 W Required LLD 15 18 30 Sewage Effluent 01-23-85 SPW-1519 Water <15 <18 <30 Outfall 015 Sewage Effluent 02-14-85 SPW-1541 Water <15 <18 <30 Outf all 015 Sewage Effluent 03-14-85 SPW-1575 Water <15 <18 <30 Outfall 015 Sewage Effluent 04-25-85 SPW-1631 Water <l5 <18 <30 Outf all 015 Sewage Effluent 05-22-85 SPW-1643 Water <15 <18 <30 Outf all 015 Sewage Effluent 07-03-85 SPW-1699 Water <15 <18 <30 Outfall 015 Sewage Effluent 08-22-85 SPW-1717 Water <l5 <18 <30 Outfall 015 e k
MISSISSIPPI POWER AND LIGHT Table 17. Special Sag les (continued) Mn-54, Collection Collection Lab Sagle Gross Co-58, -60, Fe-59, I . D. Date Code Type Betaa Cs-134 Cs-137 Zn-65 Required LLD 15 18 30 Sewage Effluent 09-12-85 SPW-1726 Water --
<15 <18 <30
- Outfall 015 Sewage Effluent 10-09-85 SPW-1801 Water --
<15 <18 <30 Outfall 015 Sewage Effluent 10-09-85 SPW-1802 Water --
<15 <18 <30 g Outfall 015 (GG)
Sewage Effluent 11-14-85 SPW-1809 Water --
<15 <15 <30 Outfall 015 Sewage Effluent 12-12-85 SPW-1903 Water -- <15 <18 <30 Outfall 015 Outfall 007 06-20-85 SPW-1667 Water --
<15 <18 <30 Outfall 007 07-17-85 SPW-1698 Water -- <15 <18 <30 Outfall 007 08-08-85 SPW-1701 Water 4.811.6 <15 <18 <30 j Outfall 007 09-10-85 SPW-1727 Water 3.410.8 <15 <18 <30 Outfall 007 10-08-85 SPW-1799 Water 2.210.5 <15 <18 <30 Outfall 007 11-21-85 SPW-1866 Water <2.0 <15 <18 <30 a Analysis for gross beta is not required; sagles analyzed per request by Mississippi Power and Light. ,
Appendix A Interlaboratory Comparison Program Results m. Y A-1
Appendix A Interlaboratory Comparison Program Results Teledyne Isotopes Midwest Laboratory (formerly Hazleton Environmental Sciences) has participated in interlaboratory comparison (crosscheck) programs since the formulation of its quality control program in December 1971. These programs are operated by agencies which supply environmental-type samples (e.g., milk or water) containing concentrations of radionuclides known to the issuing agency but not to participant laboratories. The purpose of such a program is to provide an independent cher on the laboratory's analytical procedures and to alert it to any possible prou 4 Participant laboratories measure the concentrations of specified radionuclides and report them to the issuing agency. Several months later, the agency reports the known values ta the participant laboratories and specifies control limits. Results consistently higher or lower than the known values or outside the control limits indicate a need to check the instruments or procedures used. The results in Table A-1 were obtained through participation in the environ-mental sample crosscheck program for milk, water, air filters, and food samples during the period 1982 through October 1985. This program has been conducted by the U. S. Environmental Protection Agency Intercomparison and Calibration Section, Quality Assurance Branch, Environmental Monitoring and Support Laboratory, Las Vegas, Nevada. The results in Table A-2 were obtained for thermoluminescent dosimeters (TLD's) during the period 1976, 1977, 1979, 1980, and 1981 through parti-cipation in the Second, Third, Fourth, and Fif th International Intercomparison of Environmental Dosimeters under the sponsorships listed in Table A-2. l A-2 l
._ . = -
Table A-1. U.S. Environmental Protection Agency's crosscheck program, com-parison of EPA and Teledyne Isotopes Midwest Laboratory results for milk, water, air filters, and food samples,1982 through 1985.a Concentration in pCi/lb Lab Sample Date TIML Result EPA Result Code Type Collected Analysis f2cc i3o, n=1d l STW-270 Water Jan. 1982 Sr-89 24.3*2.0 21.0i5.0 Sr-90 9.4i0.5 12. Oil.5 STW-273 Water Jan. 1982 I-131 ~8.6i0.6 8.4*1.5 STW-275 Water Feb. 1982 H-3 15801147 1820i342 STW-276 Water Feb. 1982 Cr-51 '<61 0 Co-60 26.0i3.7 2015 Zn-65 <13 15t5 Ru-106 <46 20i5 Cs-134 26.8i0.7 22i5 Cs-137 29.711.4 23t5 STW-277 Water Mar. 1982 Ra-226 11.911.9 11.611.7 STW-278 Water Mar. 1982 Gross alpha 15.6fl.9 1915 4 Gross beta 19.210.4 1915 STW-280 Water Apr. 1982 H-3 2690180 2860*360 STW-281 Water Apr. 1982 Gross alpha 75i7.9 85i21 Gross beta 114.115.9 106i5.3 i Sr-89 17.4tl.8 24*5 Sr-90 10.5i0.6 12*1.5 , Ra-226 11.4i2.0 10.9tl.5 Co-60 <4.6 0 STW-284 Water May 1982 Gross alpha 31.516.5 27.5f7 Gross beta 25.9*3.4 29*5 l STW-285 Water June 1982 H-3 1970*1408 1830*340 STW-286 Water June 1982 Ra-226 12.6tl.5 13.4*3.5 Ra-228 11.li2.5 8.7*2.3 STW-287 Water June 1982 I-131 6. 5t0. 3 4.4i0.7 STW-290 Water Aug. 1982 H-3 3210i140 28901619 l ! A-3
Table A-1. (continued) Concentration in pCi/lb Lab Sample Date TIML Result EPA Result Code Type Collected Analysis i2cc i3o, n=1d STW-291 Water Aug. 1982 I-131 94.612.5 87t15 STW-292 Water Sept. 1982 Sr-89 22.713.8 24.518.7 Sr-90 10.9i0.3 14.512.6 STW-296 Water Oct. 1982 Co-60 20.Dil.0 20i8.7 Zn-65 32.315.1 2418.7 Cs-134 15.311.5 19.0i8.7 Cs-137 21.Dil.7 20.Di8.7 STW-297 Water Oct. 1982 H-3 2470i20 25601612 STW-298 Water Oct. 1982 Gross alpha 32i30 55124 Gross beta 81.716.1 81i8.7 Sr-89 <2 0 Sr-90 14.li0.9 17.2i2.6 Cs-134 <2 1.818.7 Cs-137 22.710.6 2018.7 Ra-226 13.6i0.3 12.Si3.2 Ra-228 3.9tl.0 3.6i0.9 STW-301 Water Nov. 1982 Gross alpha 12.0il.0 19.018.7 Gross beta 34.0i2.7 24.0i8.7 STW-302 Water Dec. 1982 I-131 40. 0f 0. 0 37.0*10 STW-303 Water Dec. 1982 H-3 1940120 1990i345 STW-304 Water Dec. 1982 Ra-226 11.7i0.6 11.0 1.7 Ra-228 <3 0 STW-306 Water Jan. 1983 Sr-89 20.0*8.7 29.2i5 Sr-90 21.7i8.4 17.2il.5 STW-307 Water Jan. 1983 Gross alpha 29.0i4.09 29.0113 Gross beta 29.310.6 31.0i8.7 STM-309 Milk Feb. 1983 Sr-89 35i2.0 37*8.7 Sr-90 13.710.6 18i2.6 I-131 55.7i3.2 55i10.4 Cs-137 29tl.0 2618.7 8a-140 <27 0 K-40 163715.8 15121131 A-4
Table A-1. (continued) Concentration in pCi/lb Lab Sanple Date TIML Result EPA Result Code Type Collected Analysis i2cc 13 0, n=1d STW-310 Water Feb. 1983 H-3 2470i80 2560i612 STW-311 Water March 1983 Ra-226 11.9tl.3 12.713.3 Ra-228 <2.7 0 STW-312 Water March 1983 Gross alpha 31.614.59 31i13.4 Gross beta 27.0i2.0 28i8.7 STW-313 Water April 1983 H-3 3240i80 33301627 STW-316 Water May 1983 Gross alpha 94i7 64i19.9 Gross beta 13315 149112.4 Sr-89 1911 24i8.7 Sr-90 1211 1312.6 Ra-226 7.9i0.4 8.5i2.25 Co-60 3012 3018.7 Cs-134 27i2 3318.7 Cs-137 2911 27i8.7 STW-317 Water May 1983 Sr-89 59.712.1 57i8.7 Sr-90 33.7tl.5 3813.3 STW-318f Water May 1983 Gross alpha 12.8tl.5 1118.7 Gross beta 49.4i3.9 57*8.7 STM-320 Milk June 1983 Sr-89 2010 25i8.7 Sr-90 1011 16t2.6 I-131 3011 .30110.4 Cs-137 52 2 47*8.7 K-40 1553157 1486i129 STW-321 Water June 1983 H-3 1470 89 1529i583 STW-322 Water June 1983 Ra-226 4.310.2 4.811.24 Ra ?.28 <2.5 0 STW-323 Water July 1983 Gross alpha 31 718.7 Gross beta 2110 2218.7 i STW-324 Water August 1983 I-131 13.310.6 14i10.4 A-5
i i l Table A-1. (continued) l i Concentration in pCi/lb Lab Sample Date TIML Result EPA Result Code Type Collected Analysis i2cc i3c, n=1d STAF-326 Air August 1983 Gross beta 4212 3618.7 Filter Sr-90 1412 10t2.6 Cs-137 19t1 1518.7 Water Sept. 1983 Gross alpha 2.310.6 518.7 STW-328 Gross beta 10.7*1.2 9t8.7 , STW-329 Water Sept. 1983 Ra-226 3. 0i0. 2 3.110.81 Ra-228 3.210.7 2.010.52 STW-331 Water Oct. 1983 H-3 1300130 1210f570 STW-335 Water Dec. 1983 I-131 19.6fl.9 20i10.4 STW-3 :i Water Dec. 1983 H-3 2870fl00 2389f608 STAF-337 Air Nov. 1983 Gross alpha 18.0f0.2 19i8.7 Filter Gross beta 58.6fl.2 50f8.7 Sr-90 10.910.1 15*2.6 Cs-137 30.lf2.5 20i8.7 STW-339 Water Jan. 1984 Sr-89 47.211.9 36i8.7 Sr-90 22.514.0 24i2.6 STW-343 Water Feb. 1984 H-3 2487t76 2383i607 STM-347 Milk March 1984 I-131 5.311.1 6fl.6 STW-349 Water March 1984 Ra-226 4.010.2 4.1*1.06 Ra-228 3.610.3 2.010.52 STW-350 Water March 1984 Gross alpha 3.811.1 Si8.7 Gross beta 24.212.0 20i8.7 STW-354 Water April 1984 H-3 3560*50 35081630 STW-355 Water April 1984 Gross alpha 21.014.1 35t15. 2 l Gross beta 127.8i4.1 147t12.7 Sr-89 29.3i2.0 2318.7 1 Sr-90 16.6i0.7 26*2.6 ! Ra-226 4. 0*1. 0 4.011.04 Co-60 32.3tl.4 30i8.7 Cs-134 33.6t3.1 3018.7 Cs-137 33.3 2.2 2618.7 i A-6
Table A-1. (continued) , Concentration in pCi/lb Sample Date TIML Result EPA Result Lab i3o, n=1d Code Type Collected Analysis *2cc STW-358 Water May 1984 Gross alpha 3.0i0.6 3i8.7 Gross beta 6.711.2 618.7 Milk June 1984 Sr-89 21i3.1 25t8.7 STM-366 Sr-90 13i2.0 17*2.6 I-131 46i5.3 43110.4 Cs-137 38i4.0 3518.7 K-40 15771172 1496i130 Water July 1984 Gross alpha 5.111.1 6i8. 7 STW-368 Gross beta 11.9t2.4 1318.7 STW-369 Water August 1984 I-131 34.3f5.0 34.0t10.4 STW-370 Water August 1984 H-3 3003i253 2817f617 STF-371 Food July 1984 Sr-89 22.0i5.3 25.0t8.7 Sr-90 14.7t3.1 20.012.6 I-131 <172 39.0110.4 Cs-137 24.015.3 25.0t8.7 K-40 25031132 2605i226.0 STAF-372 Air August 1984 Gross alpha 15.311.2 17i8.7 Filter Gross beta 56.0i0.0 5118.7 Sr-90 14.3tl.2 1812.4 Cs-137 21.0*2.0 15i8.7 STW-375 Water Sept. 1984 Ra-226 5.110.4 4.911.27 Ra-228 2.210.1 2.310.60 STW-377 Water Sept. 1984 Gross alpha 3.3tl.2 5.018.7 Gross beta 12.7i2.3 16.018.7 STW-379 Water Oct. 1984 H-3 28601312 2810i356 4018.7 m STW-380 Water Oct. 1984 Cr-51 <36 Co-60 20.311.2 2018.7 Zn-65 15018.1 14718.7 Ru-106 <30 47i8.7 Cs-134 31.3t7.0 3118.7 . Cs-137 26.711.2 24i8.7 A-7
Table A-1. (continued) , Concentration in pCi/lb Sample Date TIML Result EPA Result Lab i3o, n=1d Code Type Collected Analysis fase Oct. 1984 Sr-89 15.714.2 2218.7 STM-382 Milk 16;i2.6 Sr-90 12.7tl.2 I-131 41.7i3.1 42i10.4 Cs-137 31.3*6.1 3218.7 K-40 1447i66 1517i131 Oct. 1984 ~ Gross alpha 9.711.2 14i8.7 STW-384 Water Sample A Ra-226 3. 3i0. 2 3.0*0.8 (Blind) 3.411.6 2.110.5 Ra-228 Uranium nae 5110.4 Sample 3 Gross beta 48.315.0 6418.7 Sr-89 10.714.6 1118.7 Sr-90 7.3tl.2 12i2.6 Co-60 16.311.2 1418.7 Cs-134 <2 218.7 Cs-137 16.711.2 14i8.7 Air Nov. 1984 Gross alpha 18.711.2 1518.7 STAF-387 Filter Gross beta 59.015.3 5218.7 Sr-90 18.311.2 21i2.6 Cs-137 10.3tl.2 1018.7 STW-288 Water Dec. 1984 I-131 28.012.0 36 i1 0. 4 Water Dec. 1984 H-3 3583fl10 3182i624 STW-389 Water Dec. 1984 Ra-226 8.4tl.7 8.6*2.2 l STW-391 l Ra-228 3.110.2 4.111.1
.STW-392 Water Jan. 1985 Sr-89 <3. 0 3.0i8.7 Sr-90 27.3i5.2 30.0i2.6 Jan. 1985 Gross alpha 3.311.2 518.7 f.TW-393 Water Gross beta 17.313.0 15i8.7 Jan. 1985 Sr-89 25.316.4 34. 0i 5. 0 STS-395 Food Sr-90 27.0i8.8 26.0*1.5 I-131 38.0f2.0 35.0*6.0 Cs-137 32.7*2.4 29.015.0 K-40 1410i212 1382il20 j 1
A-8
Table A-1. (continued) Concentration in pCi/lb Lab Sample Date TIML Result EPA Result Code Type Collected Analysis *2cc i3o, n=1d STW-397 Water Feb. 1985 Cr-51 <29 48i8.7 Co-60 21.313.0 2018.7 Zn-65 53.715.0 5518.7 Ru-106 <23 2518.7 Cs-134 32.311.2 3518.7 Cs-137 25.313.0 25i8.7 STW-398 Water Feb. 1985 H-3 38691319 37961634 STM-400 M'lk March 1985 I-131 7.3*2.4 9.010.9 STW-402 Water March 1985 Ra-226 4.6i0.6 5.011.3 Ra-228 <0.8 9.0i2.3 Reanalysis Ra-228 9.010.4 STW-404 Water March 1985 Gross alpha 4.7i2.3 618.7 Gross beta 11.311.2 15t8.7 STAF-405 Air March 1985 Gross alpha 9.3tl.0 10.018.7 Filter Gross beta 42.0*1.1 36. 0i8. 7 Sr-90 13.3i1.0 15.0i2.6 Cs-137 6.3tl.0 6.0i8.7 STW-407 Water April 1985 I-131 8.0*0.0 7.511.3 STW-408 Water April 1985 H-3 3399i150 35591630 STW-409 Water April 1985 (811nd) Gross alpha 29.711.8 32.0*5.0 Sample A Ra-226 4.4i0.2 4.110.6 Ra-228 nae 6.2i0.9 Uranium nae 7.0i6.0 Sample B Gross beta 74.3fil.8 72.015.0 Sr-89 12.317.6 10.015.0 Sr-90 14.712.4 15.011.5 Co-60 14.7t2.4 15.015.0 i Cs-134 12.012.0 15.0i5.0 l Cs-137 14.0*2.0 12.015.0 A-9 l l l
Table A-1. (continued) Concentration in pCi/lb Lab Sample Date TIML Result EPA Result Code Type Collected Analysis 120c i30, n=1d STW-413 Water May 1985 Sr-89 36. 0* 1 2. 4 39.0i5.0 Sr-90 14.314.2 15.011.5 STW-414 Water May 1985 Gross alpha 8.3t4.1 12.015.0 Gross beta 8. 7tl.2 11.0i5. 0 STW-416 Water June 1985 Cr-51 44. 7t6. 0 44.0*5.0 Co-60 14.3i1.2 14.0*5.0 Zn-65 50.3t7.0 47.0i5.0 Ru-106 55.315.8 62.015.0 Cs-134 32.7tl.2 35.015.0 Cs-137 22.7t2.4 20.015.0 STW-418 Water June 1985 H-3 2446t132 24161351 STM-421 Milk June 1985 Sr-89 10.3i4.6 11.0t8.7 Sr-90 9.Di2.0 11.0*2.6 I-131 11.7tl.2 11.0i10.4 Cs-137 12.711.2 11.018.7 K-40 1512i62 1525i132 STW-423 Water July 1985 Gross alpha 5.010.0 11.018.7 Gross beta 5.012.0 8.018.7 STW-425 Water August 1985 I-131 25.7t3.0 33.0i10.4 STW-426 Water August 1985 H-3 4363183 4480i776 STAF-427 Air August 1985 Gross alpha 11.310.6 13.0i8.7 Filter Gross beta 46.011.0 44.0i8;7 Sr-90 17.7i0.6 18.012.6 Cs-137 10.310.6 8.0f8.7 STW-429 Water Sept. 1985 Sr-89 15.7i0.6 20.018.7 Sr-90 7.0i0.0 7.012.6 STW-430 Water Sept. 1985 Ra-226 8.210.3 8.9i2.3 Ra-228 4.110.3 4.611.2 STW-431 Water Sept. 1985 Gross alpha 4.710.6 8.018.7 Gross beta 4.7 1.2 8.0t8.7 ey . A-10 l
f Table A-1. (continued) Concentration in pCi/lb Lab Sample Date TIML Result EPA Result Code Type Collected Analysis *2ac *3o, n=1d STW-433 Water Oct. 1985 Cr-51 <13 21.0t8.7 Co-60 19.30.6 20.0f8.7 Zn-65 19.7*0.6 19.0*8.7 Ru-106 <19 20.0*8.7 Cs-134 17.Otl.0 20.0i8.7 Cs-137 19.3i1.2 20.0*8.7 STW-435 Water Oct. 1985 H-3 1957i50 19741598 t j a Results obtained by Teledyne Isotopes Midwest Laboratory as a participant in the environmental sample crosscheck program operated by the Intercom-parison and Calibration Section, Quality Assurance Branch, Environmental 3 Monitoring and Support Laboratory, U.S. Environmental Protection Agency, b (EPA), Las Vegas, Nevada.All results are in pCi/1, except for elemental potassium (K) in mg/1; air filter samples, which are in pCi/ filter; and food, which is in DCi/kg. c Unless otherwise indicated, the TIML results are given as the mean 12 standard deviations for three determinations. j d USEPA results are presented as the known values i control limits of 3a for i n = 1. j 8 NA = Not analyzed. j f Analyzed but not reported to the EPA. .l 9 Results after calculations corrected (error in calculations when reported to l EPA). 'l ii i A-11
V 4 Table A-2. Crosscheck program results, thermoluminescent dosimeters (TLDs). mR Teledyne Average 12o d Lab TLD Result Known (all Code Type Measurement 12aa Value participants) 2nd International Intercomparisonb 115-2b CaF2:Mn Gamma-Field 17.0il.9 17.1c 16.417.7 Bulb Gamma-Lab 20.8i4.1 21.3C 18.817.6 3rd International Intercomparisone 115-3e CaF2:Mn Gamma-Field 30.7i3.2 34.914.8f 31.513.0
? hlb R; Gamma-Lab 89.616.4 91.7i14.6f 86.2124.0 4th International Intercomparison9 , 115-49 CaF2:Mn Gamma-Field 14.lil.1 14.lil.4f 15.019.0 Bulb Gamma-Lab (Low) 9.311.3 12.212.4f 12.0t7.6 3
Gamma-Lab (High) 40.411.4 45.819.2f 43.9113.2 5th International Intercomparisonh 115-5Ah CaF2:Mn Gamma-Field 31.411.8 30.Di6.01 30.2114.6 Bulb Gamma-Lab 77.415.8 75.217.61 75.8140.4 at beginning 4 Gamma-Lab 96.615.8 88.418.81 90.7131.2 at the end s
l . I Table A-2. (Continued) i mR Teledyne Average i 20 d Lab TLD Result Known (all Code Type Measurement 12da value participants) ! 115-5Bh LIF-100 Gama-Field 30.314.8 30.0161 30.2114.6 i Chips Gamma-Lab 81.li7.4 75.217.61 75.8140.4 at beginning l Gama-Lab 85.4f11.7 88.418.81 90.7131.2 ! at the end I 3=
.L a Lab result given is the mean *2 standard deviations of three determinations.
w b Second International Intercomparison of Environmental Dosimeters conducted in April of 1976 by the Health
- and Safety Laboratory (GASL), New York, New York, and the School of Public Health of the University of j Texas, Houston, Texas.
j c Value determined by sponsor of the intercomparison using continuously operated pressurized ion chad er. ] d Mean 12 standard deviations of results obtained by all laboratories participating in the program.
- e Third International Intercogarison of Environmental Dosimeters conducted in summer of 1977 by Oak Ridge
- National Laboratory and the School of Public Health of the University of Texas, Houston, Texas.
f Value *2 standard deviations as determined by sponsor of the intercomparison using continuously operated
] pressurized ion chamber.
9 Fourth International Intercogarison of Environmental Dosimeters conducted in sunener of 1979 by the School of Public Health of the University of Texas, Houston, Texas. l h Fifth International Intercomparison of Environmental Dosimeter conducted in fall of 1980 at Idaho Falls, ! Idaho and sponsored by the School of Public Health of the University of Texas Houston, Texas and Environmental Measurements Laboratory, New York, New York, U.S. Department of Energy. l 1 Value determined by sponsor of the intercomparison using contis;uously operated pressurized ion chas er. i i
--_u - - - _ _ _ _ _ _ _ _ _ _ _ _ _ m - _ v
Appendix B Data Reporting Conventions 8-1 __ ,. __ _ , , _ - . , ---i- .- -,----,, . -,-- - - - ---
Data Reportino. Conventions , 1.0. All activities are decay corrected to collection time. 2.0. Single Measurements Each single measurement is reported as follows: xis where x = value of the measurement; s = 2e counting uncertainty (corresponding to the 95% confidence level). In cases where the activity is found to be below the lower limit of detection L it is reported as
<L where L = is the lower limit of detection based on 4.66 uncertainty for a background sample.
3.0. Duolicate Analyses 3.1. Individual results: x1 s1 x2 s2 Reported result: x s where x = (1/2) (x1 + x2) s=(1/2)fs232 . 3.2. Individual results: <L1
<L2 Reported result: <L where L = lower of L1 and L2 3.3. Individual results: xis
<L Reported result: x i s if x > L; !
<L otherwise l
B-2
i .- 4.0. Computation of Averages and Standard Deviations 4.1 Averages and . standard deviations listed in the tables are computed from all of the individual measurements over the period averaged; for example, an annual standard deviation would not be the average of quarterly standard deviations. The average I and standard deviations of a set of n numbers x1, x2, . . . xn are defined as follows: x=1n Ex s- r(x-x)2 n-1 4.2 Values below the highest lower limit of detection are not included ; in the average. l 4.3 If all of the values in the averaging group are less than the highest LLD, the highest LLD is reported. 4.4 If all but one of the values are less than the highest LLD, the single value x and associated two sigma error is reported. t 4.5. In rounding off, the following rules are followed: (
+
) 4.5.1. If the figure following those to be retained is less than 5 j the figure is dropped,- and the retained figures are kept i unchanged. As an example,11.443 is rounded off to 11.44. i l 4.5.2 If the figure following those to be retained is greater than , 5, the figure is dropped, and the last retained figure is ! raised by 1. As an example,11.446 is rounded off to 11.45.. ' 4.5.3. If the figure following those to be retained is 5, and if there are no figures other than zeros beyond the five, the figure 5 is dropped, and the last-place figure retained is ! increased by one if it is an odd nunber or it is kept unchanged if an e"en number. As an exaple,11.435 is ; rounded off to 14.44, while 11.425 is rounded off to 11.42. i f B-3 ! i
.- --~.,.-,-,------,,..r... , e,--..-,-. ,r .,,-,,__.r- ,ww-.,- .-w,,,_,, ,_y,.w_--,,,,,__,wyo-,m,,,,-,,,,,y---,ww.w,,,, -,,---,-%, - , - , c-
TABLE 7-2 AP&L VEGETATION SAMPLE RESULTS J20AREOR850306 57
TABLE 7-2 AP&L VEGETATION SAMPLE RESULTS (1985) (pci/g wet weight) Collection Location Collection Lab Sample Type Cs-134 Cs-137 I-131 Other I. D. Date Code Gamma VEGR8579A Sector R 10/14/85 850075 Pecan < 0.023 < 0.021 < 0.029 < 0.078 VEGR8579GG Sector R 10/14/85 855691 Pecan < 0.023 < 0.028 < 0.042 < 0.110 VEGR8580A Sector R 10/14/85 850076 China Berry < 0.035 < 0.029 < 0.041 < 0.128 VEGR8580GG Sector R 10/14/85 850892 China Berry < 0.021 < 0.019
< 0.035 < 0.041 VEGR8581A Sector R 10/14/85 850077 Box Elder < 0.020 < 0.028 < 0.029 < 0.083 VEGR8581GG Sector R 10/14/85 850093 Box Elder < 0.016 < 0.018 < 0.037 < 0.086~
VEGJ8576A Sector J 10/14/85 850072 Rape < 0.031 < 0.025 < 0.031 < 0.094 VEGJ8577A Sector J 10/14/85 850073 Box Elder < 0.027 < 0.024 < 0.033 < 0.097 VEGJ8578A Sector J 10/14/85 850074 Mustard < 0.010 < 0.009
< 0.011 < 0.033 VEGCONT Alcorn 10/14/85 850075 Turnips < 0.017 < 0.014 < 0.013 < 0.055 8582A VEGCONT Alcorn 10/14/85 850079 Mustard < 0.015 < 0.016 < 0.019 < 0.061 8583A VEGCONT Alcorn 10/14/85 850050 Rape < 0.021 < 0.021 < 0.027 < 0.075 8584A J20AREOR850306 58
l l j MISSISSIPPI POWER & LIGHT COMPANY Helping Build Mississippi l tlR&RiWWdE P. O. B O X 16 4 0. J A C K S O N, MIS SIS S IP PI 39215-1840 l April 28, 1986 O. D. KINGSLEY, JR. WKE PREliDEas? NUCLE A R OPE RATIC8e5 U. S. Nuclear Regulatory Commission Region II 101 Marietta Street, N. W., Suite 2900 Atlanta, Georgia 30323 Attention: Dr. J. Nelson Grace, Regional Administrator
Dear Dr. Grace:
SUBJECT:
Grand Gulf Nuclear Station Unit 1 License No. NPF-29 Docket No. 50-416 Annual Radiological Environmental Operating Report for 1985 AECM-86/0l!3 In accordance with Grand Gulf Nuclear Station's (GGNS) Unit 1 Technical Specifications, attached is the Annual Radiological Environmental Operating Report for the period January 1 through December 31, 1985. Questions concerning the technical content of this report should be referred to Dr. L. R. McKay, Manager, Radiological & Environmental Services, at (601) 969-2432. Yours t y, ODK:aly
. 'f.
Attachment cc: Mr. T. H. Cloninger (w/a) Mr. R. B. McGehee (w/a) Mr. N. S. Reynolds (w/a) Mr. H. L. Thomas (w/o) Mr. R. C. Butcher (w/a) Document Control Desk (w/18) U. S. Nuclear Regulatory Commission Washington, D. C. 20555 1 ly ' c5
\
L J32AECM860317 - 1 Member Middle South Utilities System}}