PLA-7310, Submits 2014 Annual Radiological Environmental Operating Report, PLA-7310
| ML15134A005 | |
| Person / Time | |
|---|---|
| Site: | Susquehanna  |
| Issue date: | 05/13/2015 |
| From: | Franke J Susquehanna |
| To: | Document Control Desk, Office of Nuclear Reactor Regulation |
| References | |
| PLA-7310 | |
| Download: ML15134A005 (122) | |
Text
MAY 1 8 2015 Jon A. Franke Site Vice President U.S. Nuclear Regulatory Commission Attn: Document Control Desk Washington, DC 20555-0001 PPL Susquehanna, LLC 769 Salem Boulevard Berwick, PA 18603 Tel. 570.542.2904 Fax 570.542.1504 jfranke@pplweb.com SUSQUEHANNA STEAM ELECTRIC STATION ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT PLA-7310 Docket Nos. 50-387 and 50-388 The Susquehanna Steam Electric Station Annual Radiological Environmental Operating Report is hereby submitted for the calendar year 2014 in accordance with Technical Specification 5.6.2.
Should you have any questions or require additional information, please contact Mr. Jeffery Grisewood, Manager-Nuclear Regulatory Affairs at (570) 542-1330.
contains no new regulatory commitments.
~~L J
A. Franke 014 Annual Radiological Environmental Operating Report Copy: NRC Region I Mr. J. E. Greives, NRC Sr. Resident Inspector Mr. J. A. Whited, NRC Project Manager Mr. L. J. Winker, PA DEP/BRP
Attachment to PLA-7310 2014 Annual Radiological Environmental Operating Report
- Susquehanna Steam Electric Station Units 1 & 2 2014 ANNUAL REPORT Annual Radiological Environmental Operating Report
SUSQUEHANNA STEAM ELECTRIC STATION UNITS 1 and 2 Prepared by:
Reviewed by:
Annual Radiological Environmental Operating Report 2014
~{A)~~
D. W. Miller, Chemistry Support Supervisor Approved by:
er-Plant Chemistry I Environmental PPL Susquehanna, LLC 769 Salem Boulevard Berwick, Pennsylvania 18603
SUSQUEHANNA STEAM ELECTRIC STATION Units 1 & 2 2014 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT JANUARY 1 TO DECEMBER 31, 2014 PPL Susquehanna, LLC Berwick, PA April, 2015
TABLE OF CONTENTS I. Summary.......................................................................................................................... 1 II. The Radiological Environmental Monitoring Program..................................................... 5 A. Objectives of the Operational REMP................................................................... 6 B. Implementation of the Objectives........................................................................ 6 Ill. Program Description...................................................................................................... 8 A. Data Interpretation............................................................................................... 8 B. Program Exceptions............................................................................................ 9 C. Program Changes............................................................................................. 17 D. Quality Assurance Program.............................................................................. 18 E. Summary of Results -Inter-Laboratory Comparison Program......................... 18 IV. Results and Discussion............................................................................................... 22 A. Atmospheric....................................................................................................... 23
- 1. Air Particulates........................................................................................ 23
- 2. Air Iodine................................................................................................. 24 B. Direct Radiation................................................................................................. 24 C. Terrestrial.......................................................................................................... 25
- 1. Milk.......................................................................................................... 25
- 2. Groundwater........................................................................................... 26
- 3. Drinking Water........................................................................................ 28
- 4. Food Products......................................................................................... 29
- 5. Soil.......................................................................................................... 30 D. Aquatic.............................................................................................................. 32
- 1. Surface Water......................................................................................... 32
- 2. Fish......................................................................................................... 33
- 3. Shoreline Sediment................................................................................. 34 E. Land Use Census.............................................................................................. 36 V. Annotations to Previous AREOR.................................................................................. 37 VI. Conclusions................................................................................................................. 37 VII. References................................................................................................................. 38
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TABLE OF CONTENTS (cont'd)
Appendix A-Program Summary..................................................................................... A-1 Appendix B-Sample Designation and Locations............................................................ B-1 Appendix C-Data Tables............................................................................................... C-1 Appendix D-Summary of Results from Analytics, Environmental Resource Associates (ERA) and Department of Energy (DOE) - Mixed Analyte Performance Evaluation Program (MAPEP) and PPL REMP Laboratory Quality Control Spike Program..................................... D-1 Appendix E - REMP Sample Equipment Operability Trending....................................... E-1
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LIST OF TABLES Appendix A Table Table A Summary of Data for SSES........................................................................ A-3 Appendix B Tables Table B-1 Sampling Locations.................................................................................... B-4 Table B-2 Susquehanna Steam Electric Station Radiological Environmental Monitoring Program.................................................................................... B-9 Appendix C Tables Table C-1 Gross Beta Analyses of Air Particulate Filters Susquehanna Steam Electric Station......................................................................................... C-3 Table C-2 Gamma Spectroscopic Analyses of Composited Air Particulate Filters Susquehanna Steam Electric Station....................................................... C-4 Table C-3 lodine-131 Analyses of Air Iodine Samples Susquehanna Steam Electric Station......................................................................................... C-5 Table C-4 Environmental Optically Stimulated Luminescence Dosimetry Results Susquehanna Steam Electric Station....................................................... C-6 Table C-5 lodine-131 and Gamma Spectroscopic Analyses of Milk Susquehanna Steam Electric Station.............................................................................. C-9 Table C-6 Tritium and Gamma Spectroscopic Analyses of Groundwater Susquehanna Steam Electric Station....................................................... C-1 1
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LIST OF TABLES (cont'd)
Table C-7 Annual Average Tritium Concentration in Precipitation, Perimeter Drain, Monitoring Wells and Lake Took-a-While (LTAW) Surface Water Data Susquehanna Steam Electric Station.................................... C-14 Table C-8 Gross Beta, Tritium and Gamma Spectroscopic Analyses of Drinking Water Susquehanna Steam Electric Station............................................ C-15 Table C-9 Gamma Spectroscopic Analyses of Food Products (Fruits and Vegetables) Susquehanna Steam Electric Station................................... C-16 Table C-1 0 Gamma Spectroscopic Analyses of Soil Susquehanna Steam Electric Station...................................................................................................... C-17 Table C-11 Tritium and Gamma Spectroscopic Analyses of Surface Water Susquehanna Steam Electric Station....................................................... C-18 Table C-12 Gamma Spectroscopic Analyses of Fish Susquehanna Steam Electric Station...................................................................................................... C-21 Table C-13 Gamma Spectroscopic Analyses of Shoreline Sediment Susquehanna Steam Electric Station.............................................................................. C-22 Appendix D Tables Table D-1 Analytics Environmental Radioactivity Cross Check Program Teledyne Brown Engineering Environmental Services............................................ D-3 Table D-2 ERA Environmental Radioactivity Cross Check Program Teledyne Brown Engineering Environmental Services............................................ D-6 Table D-3 DOE's Mixed Analyte performance Evaluation Program (MAPEP)
Teledyne Brown Engineering Environmental Services............................. D-7
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LIST OF TABLES (cont'd)
Table D-4 PPL REMP Laboratory Quality Control Spike Program Analytics Environmental Radioactivity Cross Check Program Teledyne Brown Engineering Environmental Services....................................................... D-9 Appendix E Table Table E-1 REMP Sample Equipment Operability Trending Susquehanna Steam Electric Station......................................................................................... E-3 LIST OF MAPS Map B-1 Direct Radiation Monitoring Locations Within *one Mile.............................. B-11 Map B-2 Direct Radiation Monitoring Locations From One to Five Miles.................. B-12 Map B-3 Direct Radiation Monitoring Locations Greater than Five Miles.................. B-13 Map B-4 Environmental Sampling Locations Within One Mile.................................. B-14 Map B-5 Environmental Sampling Locations From One to Five Miles...................... B-15 Map B-6 Environmental Sampling Locations Greater than Five Miles...................... B-16 LIST OF FIGURES Figure C-1 Gross Beta Activity (E-03 pCi/m3) in Air Particulates.................................. C-24 Figure C-2 Ambient Radiation Levels Based on Environmental Dosimetry Data............................................................................................................ C-25 Figure C-3 lodine-131 Activity in Milk........................................................................... C-26
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LIST OF FIGURES (cont'd)
Figure C-4 Annual Average Tritium Activity in Precipitation, Perimeter Drain, Surface Water Versus Ground Water......................................................... C-27 Figure C-5 Gross Beta Activity in Drinking Water......................................................... C-28 Figure C-6 Tritium Activity in Surface Water................................................................. C-29
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I.
Summary During normal operations of a nuclear power generating station there are permitted releases of small amounts of radioactive material to the environment. To monitor and determine the effects of these releases a Radiological Environmental Monitoring Program (REMP) has been established around the Susquehanna Steam Electric Station (SSES). The results of the REMP are published annually, providing a summary and interpretation of the data collected.
Ecology Ill was responsible for the collection of environmental samples during 2014. Teledyne Brown Engineering (TBE) was responsible for the analysis of environmental samples during 2014. The results are discussed in this report. Landauer provided the dosimetry services for SSES during 2014.
This Annual Radiological Environmental Operating Report (AREOR) conducted for SSES covers the period January 1, 2014 through December 31,2014. During that time period, 1366 analyses were performed on 1065 samples.
Of the two man-made radionuclides (tritium [H-3] and cesium-137 [Cs-137])
detected in the environment by the Susquehanna Steam Electric Station (SSES) Radiological Environmental Monitoring Program (REMP), tritium is the only radionuclide attributable toSSES operation. The whole body and organ dose to members of the public attributable to tritium identified in REMP cooling tower blowdown samples was 9.42E-04 mRem. Tritium was included in the dose calculation because it was identified in the REMP samples of permitted water being discharged to the Susquehanna River. The 2014 average concentration of tritium in the cooling tower blowdown water and the 2014 average cooling tower blowdown flow were used to determine the amount of tritium released. The presumed exposure pathways to the public from this radionuclide were drinking water taken from the Susquehanna River at Danville, PA and eating fish caught near the SSES discharge to the river.
Dose from ground plane deposition (shoreline exposure) is not applicable because tritium does not emit gamma radiation and the beta radiation emitted by tritium is not sufficiently penetrating to reach an individual on the shore.
Based on the above outlined methodology, the total tritium activity released from the SSES to the Susquehanna River in 2014 was 66.5 curies.
The 2014 average dilution factor for the Susquehanna River was 413, based on the annual average river flow of 6.53E+06 gpm and the annual average cooling tower blowdown flow of 1.17E+04 gpm.
The REMP Sample Equipment Operability and year to year trend comparison is located in Appendix E, Table E-1 The REMP was conducted in accordance with the SSES Technical Requirements Manual (TRM) and the respective station Offsite Dose Calculation Manual (ODCM) which are based on the design objectives in 10CFR Part 50, Appendix I, Sections IV.B.2, IV.B.3 and IV.C. The Lower Limit of Detection (LLD) values required by the TRM and SSES ODCM were achieved for the 2014 reporting period. The REMP objectives were also met during this period. The concentration of radioactive material in the environment that could be attributable to SSES operations was only a small fraction of the concentration of naturally occurring and man-made radioactivity. Since these results were comparable to the results obtained during the preoperational phase of the program and combined with historical results collected since commercial operation, it can be concluded that the levels and fluctuations were as expected and that the operation of the SSES had no significant radiological impact on the environment. Additionally, the REMP sample results for 2014 verify the adequacy of the SSES radioactive effluent control systems.
Samples of air particulates, air iodine, milk, groundwater, drinking water, vegetation, soil, surface water, fish and sediment were collected and analyzed. External radiation dose measurements were also made in the vicinity of SSES using passive dosimeters.
Air particulate samples were analyzed for concentrations of gross beta weekly and gamma emitting nuclides quarterly. Gross beta and cosmogenically produced beryllium-? (Be-7) were detected at levels consistent with those detected in previous years. No fission or activation products were detected.
High sensitivity iodine-131 (1-131) analyses were performed on weekly air samples. All results were less than the minimum detectable concentration.
Environmental gamma radiation measurements were performed quarterly using Optically Stimulated Luminescent dosimeters (OSLO). The levels of radiation detected were consistent with those observed in previous years.
Cow milk samples were analyzed for concentrations of 1-131 and gamma emitting nuclides. Alll-131 results were below the minimum detectable concentration. Naturally occurring potassium-40 (K-40) was detected at levels consistent with those detected in previous years. No fission or activation products were detected.
Groundwater samples were analyzed for concentrations of tritium and gamma emitting nuclides. Tritium activities detected were consistent with those detected in previous years. No fission or activation products were detected.
Drinking water samples were analyzed for concentrations of tritium, gross beta and gamma emitting nuclides. Tritium and gross beta activities detected were consistent with those detected in previous years. No fission or activation products were detected.
Food product (fruits, vegetables and broad leaf vegetation) samples were analyzed for concentrations of gamma emitting nuclides. Naturally occurring potassium-40 was detected at levels consistent with those detected in previous years. No fission or activation products were detected.
Soil samples were analyzed for concentrations of gamma emitting nuclides.
In addition to the naturally occurring isotopes (i.e. K-40, thorium-228
[Th-228], radium-226 [Ra-226] and actinium-228 [Ac-228]), Cs-137 was detected in one or more of the soil samples. The sample data is consistent with historical and preoperational data which indicates that the presence of Cs-137 in the soil is due to residual fallout from atmospheric nuclear weapons testing in the 1970s and early 1980s and the Chernobyl and Fukushima events.
Surface water samples were analyzed for concentrations of tritium and gamma emitting nuclides. Tritium activities detected were consistent with those detected in previous years. No fission or activation products were detected.
Fish and shoreline sediment samples were analyzed for concentrations of gamma emitting nuclides. No fission or activation products were detected in fish or sediment samples.
II.
The Radiological Environmental Monitoring Program PPL's Susquehanna Steam Electric Station (SSES) is a nuclear electrical generating facility with two boiling-water reactors and generators located just west of the Susquehanna River, approximately 5 miles northeast of Berwick, in Luzerne County, Pennsylvania. The station was constructed in the 1970's, with Unit 1 beginning commercial operation on June 8, 1983, and Unit 2 beginning commercial operation on February 12, 1985. Units 1 and 2 each generate a net 1,350 megawatts (MWe), for a total station output of 2,700 MWe.
In total PPL Susquehanna, LLC presently owns 2,347 acres of land on both sides of the Susquehanna River. Generally, this land is characterized by open deciduous woodlands interspersed with grasslands and orchards.
On the west side of the river, 1,605 (1,670 minus 65 acre Gould Island) acres of land is jointly owned between PPL Susquehanna, LLC (90%) and Allegheny Electric Cooperative (1 0%). The land uses on the west side of the river include generation & associated maintenance facilities, laydown areas, parking lots, roads, a nature preserve (the Susquehanna Riverlands), and agricultural leases to local farmers.
To the north of the Station along the river, PPL Susquehanna, LLC owns 100% of the 65-acre Gould Island. On the east side of the river, and across the river from the Station, PPL Susquehanna, LLC is the 100% owner of 677 acres that are maintained as undeveloped land, natural recreational areas, wildlife areas, and leases to local farmers.
More specific information on the demography, hydrology, meteorology, and land use characteristics of the area in the vicinity of the SSES can be found in the Environmental Report [Reference 1 ], the Final Safety Analysis Report
[Reference 2] and the Final Environmental Statement [Reference 3] for the SSES.
Radioanalytical data from samples collected under the REMP were compared with results from the preoperational phase and historical results during operations. Differences between these periods were examined statistically to determine the effects of station operations. This report presents the results from January 1 through December 31, 2014, for the SSES Radiological Environmental Monitoring Program (REMP).
A.
Objectives of the Operational REMP The objectives of the Operational REMP are to:
- 1.
Document compliance with SSES REMP Technical Requirements and radiological environmental surveillances.
- 2.
Verify proper implementation of SSES radiological effluent controls.
- 3.
Identify, measure and evaluate trends of radio nuclide concentrations in environmental pathways near SSES.
- 4.
Assess impact of SSES Effluents on the Environment and the public.
- 5.
To verify that SSES operations have no detrimental effects on the health and safety of the public or on the environment.
B.
Implementation of the Objectives
- 1.
In order to meet the objectives, an operational REMP was developed. Samples of various media were selected for monitoring due to the radiological dose impact to humans and other organisms. The selection of samples was based on:
(a)
Established critical pathways for the transfer of radionuclides through the environment to man, and (b)
Experience gained during the preoperational phase.
Sampling locations were determined based on site meteorology, Susquehanna River hydrology, local demography, and land uses.
- 2.
Sampling locations were divided into two classes, indicator and control. Indicator locations are sited where it is expected that radiation and radioactive material that might originate from the station would be detectable. Control locations are selected in areas where they would be unaffected by station operations (i.e. Susquehanna River upstream from the station, >1 0 miles from the station in least prevalent wind directions). Fluctuations in the levels of radionuclides and direct radiation at indicator locations are evaluated with respect to analogous fluctuations at control locations. Indicator and control location data are also evaluated relative to preoperational data.
- 3.
Appendix A, Program Summary, describes and summarizes the analytical results in accordance with the SSES Technical Specifications.
- 4.
Appendix 8, Sample Designation and Locations, describes the coding system which identifies sample type and location. Table 8-1 lists the location codes, locations, latitude, longitude, and the types of samples collected at each location. Table 8-2 contains sample medium, analysis and sampling details.
- 5.
The sampling locations are indicated on the following maps:
Map B-1, Direct Radiation Monitoring Locations Within One Mile Map B-2, Direct Radiation Monitoring Locations From One to Five Miles Map B-3, Direct Radiation Monitoring Locations Greater Than Five Miles Map B-4, Environmental Sampling Locations Within One Mile Map B-5, Environmental Sampling Locations From One to Five Miles Map B-6, Environmental Sampling Locations Greater Than Five Miles Ill.
Program Description A.
Data Interpretation Results of analyses are grouped according to sample type and presented in Appendix C, Data Tables. All results above the Lower Limit of Detection (LLD) are at a confidence level of+/- 2 sigma. This represents the range of values into which 95% of repeated analyses of the same sample should fall. As defined in U.S. Nuclear Regulatory Commission Regulatory Guide 4.8, LLD is 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". LLD is normally calculated as 4.66 times the standard deviation of the background counting rate, or of the blank sample count, as appropriate, divided by counting efficiency, sample size, 2.22 (dpm per picocurie), the radiochemical yield when applicable, the radioactive decay constant and the elapsed time between sample collection and time of counting. The LLD is an "a priori" number which represents the capability of the measurement system.
The Minimum Detectable Concentration (MDC) is defined as the smallest concentration of radioactive material that can be detected at a given confidence level. The MDC differs from the LLD in that the MDC takes into consideration the interference caused by the presence of other nuclides while the LLD does not. The MDC is an "a posteriori" number which is an indicator of the performance of the measurement system. The MDC is set to be below the LLD.
The grouped data were averaged and standard deviations calculated.
Thus, the +/- 2 sigma deviations of the averaged data represent sample and not analytical variability. For reporting and calculation of averages, any result occurring at or below the LLD is considered to be at that level.
B.
Program Exceptions Date Sample Location Exception Corrective Action Type 12/31/13 Surface 6S6 Week 1 of the January CR 2013-07175 to Water composite start date was 12/31/13: I&C performed 01/07/14 delayed to 01/03/14 due to maintenance, but unsuccessful blockage in sample line.
in removing blockage to sample line.
CR - 2013-07238 1/03/14: FIN performed maintenance to unblock sample line. Flow restored to required 1.5 gpm.
1/07/14: Operability verified.
Date Sample Location Exception Corrective Action Type 01/07/14 Surface 2S7 Week 2 of the January AR 2014-00936 to Water composite delayed the 1/07/14: Sampler turned off and 01/14/14 start date for 2 weeks due thermostat setting increased to to a frozen sample line thaw out frozen sample line.
due to low thermostat Replaced sample line tubing and setting. Sampler restored sampler to service @
inoperable from 1/07/14@
0930.
1411 to 1/08/14@ 0930.
01/07/14: Operability verified.
01/07/14 Surface 6S6 Diminished flow rate ( <1.5 CR 2014-01438 to Water gpm) for Week 2 of the 1/14/14: Adequate sample 01/14/14 January composite.
volume was collected during sampling period. Unable to obtain procedural aliquot.
1/15/14: FIN performed maintenance and flow restored to required 1.5 gpm.
1/21/14: Operability-ACS still diminished flow (<1.5 gpm).
01/14/14 Surface 6S6 Diminished flow rate (<1.5 CR 2014-02222 to Water gpm) due to blockage in 1/21/14 & 1/28/14: Adequate 01/21/14 sample line for Weeks 3 sample volume collected during and 4 of the January sample period. Procedural composite.
aliquot obtained.
1/22/14: I&C performed maintenance but were unsuccessful in removing blockage to sample line.
CR 2014-02382 1/27/14: Maintenance performed again (RTPM 1667128) and flow restored to required 1.5 gpm.
1/28/14: Operability verified.
Date Sample Location Exception Corrective Action Type 1 s.
Ground-2S8 Sample unavailable due to AR 2014-16224 Quarter Water (MW-7) insufficient groundwater 2/24/14: Notified PPL 2014 (water level below pump).
Chemistry. Will sample next quarter (May 2014).
01/28/14 Drinking 12H2 Week 1 of the February AR 2014-03906 to Water composite was delayed 2/04/14: Danville Water 02/11/14 due to power outage at company will institute Danville Water Company.
emergency power between 1100-1200 hours. Power may be intermittent on 2/04/14 to 2/05/14 until problem is resolved. ACS resumed normal operation when power was restored.
2/11/14: Operability verified.
03/04/14 Surface 6S6 Diminished flow rate (<1.5 CR 2014-07961 to Water gpm) for Week 1 of the 3/11/14: Adequate sample 03/11/14 March composite.
volume collected during sample period. Procedural aliquot obtained.
3/12/14: FIN performed maintenance and restored flow to required 1.5 gpm.
3/18/14: Operability-ACS still at diminished flow (<1.5 gpm).
03/05/14 AP/C 13S6Q Pump malfunction.
3/12/14: Replaced pump and to Pump would not restart for timer box. Operability verified.
03/12/14 next sample period. Also noticed timer box electrical cord was worn.
No effect on continuous sampler operation for sample period.
Date Sample Location Exception Corrective Action Type 03/11/14 Surface 6S6 Diminished flow rate (<1.5 CR 2014-08761 to Water gpm) for Week 2 of the 3/18/14: Adequate sample 03/18/14 March composite.
volume collected during sample period. Procedural aliquot obtained.
3/18/14: Operability-ACS still at diminished flow (<1.5 gpm) 3/19/14: Maintenance performed (RTPM 1699444) and flow restored to required 1.5 gpm.
3/25/14: Operability verified.
03/11/14 Surface 2S7 Week 2 of the March CR 2014-08764 to Water composite was not 3/18/14: Grab sample collected 03/18/14 collected by the ACs for
@ 0957 for week 2 of the March the sample period.
composite. Replaced tubing and Reason unknown.
recalibrated sampler. Sampler resumed normal operation.
Grab sample (for comparison) also collected at 6S6 as per REMP procedures.
03/18/14 Surface 2S7 The composite overflowed CR 2014-09912 to Water the composite container 3/25/14: Grab sample collected 03/25/14 resulting in a non-
@1112 for Week 3 of the March representative sample for composite. Recalibrated Week 3 of the March sampler. Sampler resumed composite. Reason normal operation. Grab sample unknown.
(for comparison) also collected as 6S6 as per REMP procedures.
3/27/14: Checked sampler and malfunction still exists.
Reconfigured sampler and checked tubing and rollers.
Sampler resumed normal operation. Will continue to monitor.
Date Sample Location Exception Corrective Action Type 03/25/14 Surface 2S7 The composite overflowed CR 2014-10410 to Water the composite container 4/01/14: Grab sample collected 04/01/14 resulting in a non-
@1 023 for week 4 of the March representative sample for compite. Recalibrated sampler.
Week 4 of the March Sampler resumed normal composite. Reason operation. New liquid detector unknown.
ordered and will be installed upon receipt. Grab sample (for comparison) also collected at 6S6 as per REMP procedures.
03/25/14 Surface 6S6 Diminished flow rate (<1.5 CR 2014-10403 to Water gpm) for Week 4 of the 04/01/14: Adequate sample 04/01/14 March composite.
volume collected during sample period. Unable to obtain procedural aliquot. Maintenance requested.
4/01/14: Operability-ACS still at diminished flow ( <1.5 gpm) 04/01/14 Surface 2S7 The composite overflowed CR 2014-11188 to Water the composite container 04/04/14: New liquid detector 04/08/14 resulting in a non-installed; sampler recalibrated.
representative sample for Sampler resumed normal Week 1 of the April operation.
composite. Reason unknown.
04/08/14: Grab sample collected @1 025 for week 1 of the April composite. Grab sample (for comparison) also collected at 6S6 as per REMP procedures. Recalibrated sampler. Sampler resumed normal operation.
04/01/14 Surface 6S6 Diminished flow rate (<1.5 CR2014-11180 to Water gpm) for Week 1 of the Adequate sample volume 04/08/14 April composite.
collected during sample period.
Unable to obtain procedural aliquot. Maintenance requested.
04/08/14 Surface 6S6 Diminished flow rate (<1.5 CR 2014-12027 to Water gpm) for Week 2 of the Adequate sample volume 04/15/14 April composite.
collected during sample period.
Unable to obtain procedural aliquot. Maintenance requested.
Date Sample Location Exception Corrective Action Type 04/08/14 Surface 2S7 The composite overflowed CR 2014-12033 to Water the composite container 4/10/14: Sampler reinitialized 04/29/14 resulting in a non-and resumed normal operation representative sample for with ideal aliquot.
Weeks 2, 3 and 4 of the April composite. Reason 4/14/14: FIN blew out both unknown.
bottom lines to sampler with nitrogen using a stroking rig, 4/17/14 to 4/29/14 -
both lines were not blocked.
Sampler out of service for further testing and repair.
4/15/14: Grab sample collected
@1 018 for week 2'-Apr comp.
Recalibrated sampler. Sampler resumed normal operation.
Grab sample (for comparison) also collected at 6S6 as per REMP procedures.
4/17/14: Checked sampler and malfunction still exists.
Removed sampler from site for further monitoring at Environmental Lab.
4/22/14: Grab sample collected
@ 0928 for week 3 of the April composite. Grab sample (for comparison) also collected at 6S6 as per REMP procedures.
4/28/14: Sampler sent to Teledyne lsco for repair.
4/29/14: Grab sample collected
@ 0945 for week 4 of the April composite. Grab sample (for comparison) also collected at 6S6 as per REMP procedures Date Sample Location Exception Corrective Action Type 04/29/14 Surface 2S7 Weeks 1 I 2 and 3 of the CR 2014-12033 to Water May composite samples Grab samples collected to meet 06/03/14 unavailable. Sampler out TRM requirements. Grab of service for repair.
sample (for comparison) also collected at 6S6 as per REMP 5/27/14 to 6/03/14-Week procedure.
5-Maycomp Repaired sampler still not 5/06/14@ 0919-Week 1 May working properly. Taken comp.
out of service. Weekly 5/13/14@ 0953-Week 2 May composites unavailable.
comp 5/19/14@ 0829-Week 3 May comp 6/03/14 @0842-Week 5 May comp.
5/20/14: Repaired sampler installed but delayed start date of 5/22/14 due to incorrect settings.
5/27/14: Valid sample collected for 5/22/14 to 5/27/14 - Week 4 Maycomp.
5/29/14: Sampler taken out of service again. New ISCO sampler ordered.
05/13/14 Surface 6S6 Diminished flow rate (<1.5 CR 2014-16878 to Water gpm) for Week 3 of the 5/19/14: Adequate sample 05/19/14 May composite.
collected for sample period.
Unable to obtain procedural aliquot. Maintenance requested.
5/27/14: I&C performed maintenance. Installed new float and restored required flow.
6/03/14: Operability verified.
06/03/14 Surface 2S7 Weeks 1 I 21 3 and 4 of the CR 2014-12033 to Water June composite samples New sampler ordered.
07/01/14 unavailable. Sampler out Grab samples collected to meet of service due to TRM requirements. Grab inoperability.
sample (for comparison also collected at 6S6 as per REMP procedure.
6/10/14@ 0945-Week 1 Jun comp.
6/17/14@ 0947-Week 2 Jun comp 6/24/14@ 1017-Week 3 Jun comp 7/01/14 @ 0955-Week 4 Jun comp Date Sample Location Exception Corrective Action Type 07/01/14 Surface 2S7 Week 1 of the July CR 2014-12033 to Water composite sample New sampler 07/29/14 unavailable. Sampler out of ordered.
service due to inoperability.
Grab sample collected to meet 07/07/14 to 07/29/14-TRM requirements.
Representative grab Grab sample (for samples collected for comparison) also weeks 2, 3 and 4 of the collected at 6S6 as July composite.
perREMP procedure.
7/08/14@ 1223-Week 1 for July composite.
AR 2014-23370 7/07/14: New sampler installed and put in service
@ 1054 hours0.0122 days <br />0.293 hours <br />0.00174 weeks <br />4.01047e-4 months <br />.
07/30/14 AP/C 6G1 Timer box malfunction -
AR 2014-25387 to digits failed to advance 8/06/14: Timer box 08/06/14 properly. No effect on replaced.
continuous sampler Operability verified.
operation for sample period.
10/14/14 Surface 6S6 Week 3 of the October CR 2014-32645 to Water composite sample 10/21/14@ 1145:
10/21/14 unavailable. No sample Grab sample flow available at ACS, collected at possibly due to blocked alternate location sample line. Non-5S9 to meet TRM representative composite requirements.
for sample period.
Requested maintenance.
10/21/14 Surface 6S6 Week 4 of the October CR 2014-33340 to Water composite sample 10/27/14@ 0940:
10/27/14 unavailable. No sample Grab sample flow available at ACS, collected at possibly due to blocked alternate location sample line. Non-5S9 to meet TRM representative composite requirements.
for sample period.
Maintenance requested to clear blockage in line.
FIN currently awaiting clearance order to complete work.
Date Sample Location Exception Corrective Action Type 10/27/14 Surface 6S6 Week 1 of the November CR 2014-34496 to Water composite sample had 11/04/14@ 1505:
11/04/14 insufficient volume due to Grab sample start date and time collected at unknown and insufficient alternate location sample volume. Grab 5S9 to meet TRM sample collected for Week requirements.
- 1.
10/29/14: FIN was unsuccessful in removing sample line blockage.
Maintenance ordered.
Sometime between 10/29/14 and 11/04/14, the sample line cleared itself and the ACS became operational.
11/04/14: ACS reset to start week 2 Novcomp.
11/05/14 AP/C 3S2 11/05/14 to 11/12/14 AR 2014-35344 to Timer box malfunction -
11/12/14:
11/12/14 digits failed to advance Replaced timer properly. No effect on box. Verified continuous sampler operability.
operation for sample period.
12/09/14 AP/C 13S6 Pump malfunction-AR 2014-38538 to inadequate flow rate 12/17/14:
12/17/14 (below procedural 2.0-2.4 Replaced pump cfm) as discovered during and verified air weekly change out. No flow.
effect on continuous sampler operation for sample period.
2014 Totals: 14 occurrences resulted in entry into TRO 3.11.4.1 Condition A All remaining occurrences were non-TRO events. Actions to prevent recurrence were not applicable to any of the occurrences in 2014.
C.
Program Changes Three broad leaf locations, 1186, 383 and 8G1 were added to the program in 2014. Leafy vegetation is collected at these locations in response to the loss of a milk sampling location (1 OS3).
D.
Quality Assurance Program Teledyne Brown Engineering The quality of the results obtained by TBE is ensured by the implementation of the Quality Assurance Program as described in the Teledyne Brown Engineering Quality Assurance Manual and the Teledyne Brown Engineering Procedure Manual.
E.
Summary of Results-Inter-laboratory Comparison Program The TBE laboratory performed 169 analyses of Performance Evaluation (PE) containing spiked samples of air particulate, air iodine, milk, soil, vegetation and water matrices, as part of the Teledyne Quality Control Spike Program. (Appendix D, Tables D-1 through D-3),
The PE samples, supplied by Analytics Inc., Environmental Resource Associates (ERA) and Department of Energy's (DOE) Mixed Analyte Performance Evaluation Program (MAPEP), were evaluated against the following acceptance criteria:
- 1.
Analytics Evaluation Criteria Analytics' evaluation report provides a ratio of reported result and Analytics' known value. Since flag values are not assigned by Analytics, TBE evaluates the reported ratios based on internal QC requirements, which are based on the DOE MAPEP criteria.
- 2.
ERA Evaluation Criteria ERA's evaluation report provides an acceptance range for control and warning limits with associated flag values. ERA's acceptance limits are established per the United States Environmental Protection Agency (USEPA), National Environmental Laboratory Conference (NELAC) performance testing (PT) program requirements or ERA's standard operating procedure (SOP) for the Generation of Performance Acceptance Limits, as applicable. The acceptance limits are either determined by a regression equation specific to each analyte or a fixed percentage limit promulgated under the appropriate regulatory document.
- 3.
DOE Evaluation Criteria MAPEP's evaluation report provides an acceptance range with associated flag values.
The MAPEP defines three levels of performance: Acceptable (flag ="A"), Acceptable with Warning (flag = 'W"), and Not Acceptable (flag = "N"). Performance is considered acceptable when a mean result for the specified analyte is +/- 20% of the reference value. Performance is acceptable with warning when a mean result falls in the range from +/- 20% to +/- 30% of the reference value (i.e., 20% <bias< 30%). If the bias is greater than 30%, the results are deemed not acceptable.
Teledyne Brown Engineering In reviewing our environmental inter-laboratory crosscheck programs, we identified 1) duplication of efforts on some matrices and. isotopes and 2) that we are performing crosscheck samples on some matrices and isotopes that we do not perform for clients. Since the DOE MAPEP is designed to evaluate the ability of analytical facilities to correctly analyze for radiological constituents representative of those at DOE sites, the needed changes were made to the MAPEP program. Therefore, the following isotopes were removed from the MAPEP program:
Soil - gamma -will be provided by Analytics twice per year, starting in 2015. For 2014, one soil gamma is provided by MAPEP, the 2nd soil gamma is provided by Analytics.
AP -gamma-is currently provided by Analytics.
Water-gamma, H-3, Sr-90, uranium, gross alpha and gross beta currently provided by ERA.
MAPEP evaluates non-reported (NR) analyses as failed if they were reported in the previous series.
For the TBE laboratory, 163 out of 169 analyses performed met the specified acceptance criteria. Six analyses (Ni-63, K-40 and 1-131 in water, and two Sr-90s and one Gross Alpha in AP samples) did not meet the specified acceptance criteria for the following reasons:
- 1.
Teledyne Brown Engineering's MAPEP March 2014 Ni-63 in water result of 32.7 +/- 1.69 Bq/L was overlooked when reporting the data but would have passed the acceptance range of 23.9 -
44.2 Bq/L.
- 2.
Teledyne Brown Engineering's MAPEP March 2014 K-40 in water result of 1.63 +/- 2.49 Bq/L was overlooked when reporting the data but would have passed the false positive test. NCR 14-04
- 3.
Teledyne Brown Engineering's ERA November 2014 1-131 in water result of 15.8 pCi/L was lower than the known value of 20.3 pCi/L, failing below the lower acceptance limit of 16.8.
The result was evaluated as failed with a found to known ratio of 0.778. No cause could be found for the slightly low result.
All ERA 1-131 evaluations since 2004 have been acceptable.
NCR 14-08
- 4.
Teledyne Brown Engineering's MAPEP March 2014 Sr-90 in AP result of 0.822 Bq/sample was lower than the known value of 1.18 Bq/sample, falling below the lower acceptance limit of 0.83 Bq/sample. The rerun result was still low, but fell within the lower acceptance range of 0.836. The rerun result was statistically the same number as the original result. No cause could be found for the slightly low results. NCR 14-04
- 5.
Teledyne Brown Engineering's MAPEP September 2014 Sr-90 in AP result of 0.310 Bq/sample was lower than the known value of 0.703 Bq/sample. The gravimetric yield of 117% was very high (we normally see yields of 60% to 70 %) and could account for the low activity. NCR 14-09
- 6.
Teledyne Brown Engineering's MAPEP September 2014 Gr-Aipha in AP result of 0.153 Bq/sample was lower than the known value of 0.53 Bq/sample. The AP sample was counted on the wrong side. The AP was flipped over and recounted with acceptable results. NCR 14-09 In addition, PPL's REMP Laboratory Spike Program provided independently procured Analytics spiked samples as part of PPL's Quality Control Spike Program.
The criteria for the acceptability of the spiked analysis results were established by PPL and are based on criteria originally developed by the NRC. The criteria are based on an empirical relationship that combines prior experience and accuracy needs. As the resolution of the measurement process improves, the criteria for determining acceptability become tighter. Conversely, as the resolution of the process becomes poorer, the criteria for determining acceptability become wider.
The TBE laboratory performed 144 analyses of Performance Evaluation (PE) containing spiked samples of air particulate, air iodine, milk, soil and water matrices. (Appendix D, Table D-4)
For the TBE laboratory, 138 out of 141 analyses performed met the specified acceptance criteria. Six analyses (three Co-60 and one Ce-141 in an air particulate, a Cr-51 in soil and an 1-131 in milk) did not meet the specified acceptance criteria or internal QA requirements. The TBE laboratory initiated Nonconformance Report 15-04 to address the failures.
IV.
Results and Discussion The analytical results of the 2014 REMP samples are divided into categories based on exposure pathways: atmospheric, direct radiation, terrestrial, and aquatic. The analytical results for the 2014 REMP are summarized in Appendix A, Program Summary. The data for individual samples are presented in Appendix C, Data Tables. The data are compared to the formal preoperational environmental monitoring program data (April 1972 to September 1982) and to historical data during operations. The data collected demonstrates that the SSES REMP was conducted in compliance with the TRM and the SSES ODCM.
A.
Atmospheric Atmospheric REMP sampling includes the collection of air particulate, air iodine and direct radiation samples.
- 1.
Air Particulates Air particulate samples were collected weekly at four indicator locations (382, 12E1, 1281 and 1386) and two control locations (6G1 and 8G1 ). Each of the samples collected for the year were analyzed for gross beta. Quarterly composites of the weekly samples from each location were analyzed for specific gamma emitters.
Gross Beta Gross beta activity was detected in 208 of 208 of the indicator location samples at concentrations ranging from 6 to 26 E-3 pCi/m3 with an average concentration of 13 E-3 pCi/m3, and in 1 04 of 1 04 of the control location samples at concentrations ranging from 7 to 23 E-3 pCi/m3 with an average of 12 E-3 pCi/m3. The maximum preoperational level detected was 102 E-3 pCi/m3 with an average concentration of 62 E-3 pCi/m3.
(Table C-1, Appendix C); Historical levels of gross beta are shown in Figure C-1. Results for gross beta analysis from 1974 to current year are plotted.
Gamma Spectrometry Gamma spectroscopy was performed on each of the 24 quarterly composite samples.
Beryllium-?, attributed to cosmic ray activity in the atmosphere, was detected in all 16 indicator location composites at concentrations ranging from 52 E-3 to 125 E-3 pCi/m3 with an average concentration of 92 E-3 pCi/m3, and in the eight control location composites ranging in concentration from 75 to 131 E-3 pCi/m3 with an average concentration of 103 E-3 pCi/m3.
The maximum preoperational level detected was 85 E-3 pCi/m3 with an average concentration of 74 E-3 pCi/m3. (Table C-2, Appendix C)
All other gamma emitters were less than the LLD.
- 2.
Air Iodine Filtered air iodine samples were collected weekly at four indicator locations (3S2, 12E1, 12S1 and 13S6) and two control locations (6G1 and 8G1 ). Each of the samples collected for the year were analyzed for 1-131.
lodine-131 lodine-131 was not detected in any indicator location samples or control location samples. Preoperational data is not available for comparison. {Table C-3, Appendix C)
B.
Direct Radiation Ambient radiation levels in the environs were measured with a pair of optically stimulated luminescent dosimeters (OSLO) composed of aluminum oxide crystals supplied and processed by Landauer.
Packets containing OSLDs for quarterly exposure were placed in the owner-controlled area and around the Site at various distances and in each land based meteorological sector. Emphasis was placed on special interest areas such as population centers, nearby residences, and schools.
A total of 57 locations were monitored for direct radiation during 2014, including 30 site boundary locations, 16 outer distance locations, six special interest locations and five control locations.
The average dose rate for the 206 indicator dosimeters was 20.4 milliroentgen per standard quarter. The average control dose rate for the 19 control dosimeters was 18.4 milliroentgen per standard quarter.
The preoperational average for the quarterly direct radiation readings was 17.6 milliroentgen per standard quarter. The results of the direct radiation measurements for 2014 confirmed that the radiation levels in the vicinity of the SSES were similar to previous years. (Table C-4, Appendix C); Figure C-2 -Ambient Radiation Levels Based on Environmental Dosimetry Data from 1973 to current year are plotted as quarterly averages.
C.
Terrestrial Terrestrial REMP sampling includes the collection of milk, groundwater, drinking water, vegetation and soil samples.
- 1.
Milk Milk samples were collected semi-monthly when cows were on pasture and monthly when cows were not grazing on open pasture. Animals are considered on pasture from April to October of each year. Samples were collected in new polyethylene containers and transported in ice chests with no preservatives added to the milk.
Milk samples were collected at local dairy farms from 2 indicator locations (5E2 and 13E3) and one control location (10G1). Each sample was analyzed for 1-131 and gamma emitters.
lodine-131 lodine-131 was not detected above minimum detectable concentration in any of the 60 samples analyzed.
Preoperational data is not available for comparison. (Table C-5, Appendix C); Figure C-3 -lodine-131 Activity in Milk results from 1976 to 2014 are plotted.
Gamma Spectrometry Naturally occurring K-40 was detected in all 60 samples with concentrations for the 40 indicator location samples ranging from 1,171 to 1,576 pCi/L with an average concentration of 1,340 pCi/L, and the 20 control location sample concentrations ranging from 1,009 to 1,401 pCi/L with an average concentration of 1,254 pCi/L. The maximum preoperational level detected was 1,500 pCi/L with an average concentration of 1,358 pCi/L. Naturally occurring Th-228 was not detected in any of the samples. Preoperational data is not available for comparison. (Table C-5, Appendix C)
All other gamma emitters were less than the LLD.
- 2. GroundWater An expanded groundwater monitoring network was initiated in 2006 for the SSES as part of a site-wide hydrogeological investigation in accordance with the Nuclear Energy Institute (NEI) Groundwater Protection Initiative (GPI). The additional groundwater monitoring wells are sampled as part of the Radiological Environmental Monitoring Program (REMP) to regularly assess groundwater quality and provides early detection of any inadvertent leaks or spills of radioactive materials that could reach groundwater. Groundwater is sampled quarterly and analyzed for H-3 and gamma activity.
Additionally, precipitation sampling was initiated in 2007 and analyzed for H-3 activity to assess the influence of station airborne H-3 emissions on groundwater H-3 activities.
Precipitation washout monitoring data is not used in dose calculations; however, the data does give a gross indication of H-3 concentrations which makes its way into surface water and soil where it eventually seeps into shallow groundwater. The annual average H-3 concentration in precipitation, perimeter drain manholes, groundwater monitoring wells and surface water is summarized in Table C-7 and graphically depicted in Figure C-4 -Annual Average Tritium Activity (pCi/L) in precipitation, Perimeter Drain, Surface Water Versus Ground Water.
Ground water samples were collected quarterly at 14 indicator locations (2S2, 484, 6810, 1182, 183, 488, 489, 884, 7810, 1387,288, 6S11A, 6812 and 7811) and one control location, (12F3). Each sample was analyzed for H-3 and gamma emitters.
Tritium Tritium activity was detected above the minimum detectable concentration in 4 of the 55 indicator location samples with concentrations ranging from 201 to 224 pCi!L with an average concentration of 214 pCi/L. No Tritium was detected in any of the four control location samples. The maximum preoperational level detected was 119 pCi/L. (Table C-6, Appendix C); Figure C Annual Average Tritium Activity (pCi/L) in precipitation, Perimeter Drain, Surface Water Versus Ground Water results from 2007 to 2014 are plotted.
Gamma Spectrometry Naturally occurring K-40 was detected in two of the 55 indicator samples. Sample concentrations ranged from 46 to 54 pCi/L with an average concentration of 50 pCi/L. No K-40 was detected in any of the four control location samples.
Naturally occurring Th-228 was detected in one of 55 indicator samples at a concentration of 5 pCi!L. No Th-228 was detected in any of the four control location stations.
Preoperational data is not available for comparison. (Table C-6, Appendix C)
All other gamma emitters were less than the LLD.
- 3.
Drinking Water Drinking water samples were collected monthly from one location (12H2). Each sample was analyzed for gross beta, H-3 and gamma emitters.
Gross Beta Gross beta activity was detected in five of the 12 drinking water samples. Sample concentrations ranged from 2.0 to 3.3 pCi/L with an average concentration of 2.4 pCi/L. The maximum preoperational level detected was 3.2 pCi/L with an average concentration of2.7 pCi/L. (Table C-8, Appendix C); Figure C Gross Beta Activity in Drinking Water results from 1977 to 2014 are plotted.
Tritium Tritium activity was not detected in any of the drinking water samples. The maximum preoperational level detected was 194 pCi/L with an average of 132 pCi/L. (Table C-8, Appendix C)
Gamma Spectrometry Naturally occurring K-40 was not detected in any of the samples. Preoperational data is not available for comparison.
(Table C-8, Appendix C)
All other gamma emitters were less than the LLD.
- 4. Food Products Food products from two indicator locations (3S3 and 11 S6) and one control location (8G1) were collected throughout the growing season. All samples (vegetable and broadleaf) were analyzed for gamma emitters and included green beans, potatoes, field corn, kale, swiss chard and collards.
Gamma Spectrometry Naturally occurring Be-7, attributed to cosmic ray activity in the atmosphere, was detected in 16 of the 31 indicator location samples with concentrations ranging from 154 to 725 pCi/kg wet with an average concentration of 396 pCi/kg wet, and in seven 12 control location samples with concentrations ranging from 211 to 532 pCi/kg wet with an average concentration of 366 pCi/kg wet. Preoperational data is not available for comparison.
Naturally occurring K-40 was detected in all 31 indicator location samples with concentrations ranging from 3,837 to 8,566 pCi/kg wet with an average concentration of 6,034 pCi/kg wet, and in all 12 control location samples with concentrations ranging from 3,397 to 6,548 pCi/kg wet with an average concentration of 4,945 pCi/kg wet. The maximum preoperational level detected was 4,800 pCi/kg wet with an average concentration of 2,140 pCi/kg wet.
Naturally occurring Ac-228 was detected in one of the 31 indicator location samples at a concentration of 96 pCi/kg wet.
No Ac-228 was detected in any of the 12 control location samples. Preoperational data is not available for comparison.
Naturally occurring Th-228 was detected in one of the 31 indicator location samples at a concentration of 63 pCi/kg wet.
No Th-228 was detected in the control location samples.
Preoperational data is not available for comparison. (Table C-9, Appendix C)
All other gamma emitters were less than the LLD.
- 5.
Soil Soil samples were collected annually from one indicator location (12S1) and one control location (8G1 ). Each sample was analyzed for gamma emitters.
Gamma Spectrometry Naturally occurring K-40 was detected in all three indicator location samples at concentrations ranging from 12,820 to 15,520 pCi/kg dry with an average concentration of 13,907 pCi/kg dry, and in all three control location samples at concentrations ranging from 7,911 to 13,930 pCi/kg dry with an average concentration of 11,877 pCi/kg dry. The maximum preoperational level detected was 1,100 pCi/kg dry with an average concentration of 9,800 pCi/kg dry.
Cesium-137 was detected in one of the three indicator location samples at a concentration of 176 pCi/kg dry. No Cs-137 was detected in the control location samples. The maximum preoperational level detected was 1,200 pCi/kg dry with an average concentration of 700 pCi/kg dry.
Naturally occurring Ra-226 was detected in one of the three indicator location samples at a concentration of 2,456 pCi/kg dry. The maximum preoperational level detected was 1,300 pCi/kg dry with an average concentration of 1,100 pCi/kg dry.
Naturally occurring Ac-228 was detected in all of the three indicator location samples at concentrations ranging from 1,022 to 1,151 pCilkg dry with an average concentration of 1,100 pCi/kg dry, and in two of the three control location samples at concentrations ranging from 767 to 1,393 pCi/kg dry with an average concentration of 1,080 pCi/kg dry. Preoperational data is not available for comparison.
Naturally occurring Th-228 was detected in all of the three indicator location samples at concentrations ranging from 977 to 1,600 pCi/kg dry and an average concentration of 1,298 pCi/kg dry, and in two of the three control location samples at concentrations ranging from 1,101 to 1,565 pCi/kg dry with an average concentration of 1,333 pCi/kg dry. The maximum preoperational level detected was 1,300 pCi/kg dry with an average concentration of 1,100 pCi/kg dry. (Table C-1 0, Appendix C)
All other gamma emitters were less than the LLD.
D.
Aquatic Aquatic samples include surface water, fish and sediment samples.
- 1.
Surface Water Surface water samples were collected routinely at seven indicator locations (6S5, 2S7, LTAW, 4S7, 5S9, 5S12 and 7812) and one control location (6S6). Each sample was analyzed for H-3 and gamma emitters.
Tritium Tritium activity was detected in 17 of 45 indicator location samples with concentrations ranging from 167 to 11,500 pCi/L with an average concentration of 2,387 pCi/L. The range of H-3 levels in surface water are biased high due to inclusion of samples from the cooling tower blowdown line (CTBD; location 2S7). Routine station operation includes infrequent batch releases of slightly radioactive water which are discharged into the CTBD. When the H-3 concentration from CTBD samples is averaged with those obtained from Susquehanna River downstream monitoring locations, the result is an overall indicator location average that is higher than the actual average H-3 levels of the downstream river water. No radioactivity attributable to station operations was identified above analysis detection levels in any samples from the Susquehanna River in 2014. Tritium was not detected in any of the control location samples. The maximum preoperational level detected was 319 pCi/L, with an average concentration of 140 pCi/L. (Table C-11, Appendix C) [Figure C Tritium Activity in Surface Water, results from 1972 to 2014 are plotted.]
Gamma Spectrometry Naturally occurring K-40 was detected in 3 of the 45 indicator location samples with concentrations ranging from 42 to 44 pCi/L with an average concentration of 43 pCi/L, and in one of the 17 control location samples at a concentration of 90 pCi/L.
Preoperational data is not available for comparison.
Naturally occurring Th-228 was detected in one of the 45 indicator location samples at a concentration of 5 pCi/L, and in one of the 17 control location samples at a concentration of 4 pCi/L. Preoperational data is not available for comparison.
(Table C-11, Appendix C) lodine-131 lodine-131 was not detected in any of the indicator or control samples. The maximum preoperational level detected was 0.43 pCi/L, with an average concentration of 0.33 pCi/L. (Table C-11, Appendix C)
All other gamma emitters were less than the LLD.
- 2.
Fish Edible species of fish were collected in the spring and fall of 2014 at two indicator locations (IND [Susquehanna River] and LTAW) and one control location (2H [Susquehanna River]).
Each sample was analyzed for gamma emitters.
Gamma Spectrometry Naturally occurring K-40 was detected in all eight indicator location samples at concentrations ranging from 3,103 to 6,178 pCi/kg wet with an average concentration of 4,185 pCi/kg wet, and in all seven control location samples at concentrations ranging from 2,636 to 5,083 pCi/kg wet with an average concentration of 4,084 pCi/kg wet. The maximum preoperational level detected was 3,600 pCi/kg dry with an average concentration of 3,200 pCi/kg dry. (Table C-12, Appendix C)
All other gamma emitters were less than the LLD.
- 3.
Shoreline Sediment Sediment samples were collected from the Susquehanna River in the spring and fall at two indicator locations (78 and 12F) and one control location (28). Each sample was analyzed for gamma emitters.
Gamma Spectroscopy Naturally occurring K-40 was detected in all four of the indicator location samples at concentrations ranging from 10,620 to 14,120 pCi/kg dry with an average concentration of 12,268 pCi/kg dry, and in all three control location samples with concentrations ranging from 13,970 to 16,860 pCi/kg dry with an average concentration of 15,873 pCi/kg dry. The maximum preoperational level detected was 11,000 pCi/kg dry with an average concentration of 8,500 pCi/kg dry.
Cesium-137 was not detected in any of the samples. The maximum preoperational level detected was 210 pCi/kg dry with an average concentration of 110 pCi/kg dry.
Naturally occurring Ra-226 was detected in two of the four indicator location samples at concentrations of 1,677 and 2,378 pCi/kg dry with an average concentration of 2,028 pCi/kg dry, and in two of the three control location samples with concentrations of 1,915 and 2,524 p/Ci/kg dry with an average concentration of 2,220 pCi/kg dry. The maximum preoperational level detected was 1,900 pCi/kg dry with an average concentration of 700 pCi/kg dry.
Naturally occurring Ac-228 was detected in all four indicator location samples at concentrations ranging from 1,021 to 1,223 pCi/kg dry with an average concentration of 1,130 pCi/kg dry, and in all three of the control location samples at concentrations ranging from 943 to 1,423 pCi/kg dry with an average concentration of 1,262 pCi/kg dry. Preoperational data is not available for comparison. (Table C-13, Appendix C)
Naturally occurring Th-228 was detected in all of the four indicator location samples at concentrations ranging from 1,027 to 1,628 pCi/kg dry with an average concentration of 1,269 pCilkg dry, and in all three of the control location samples at concentrations ranging from 1,221 and 1,858 pCi/kg dry with an average concentration of 1,538 pCi/kg dry. The maximum preoperational level detected was 3,200 pCi/kg dry with an average concentration of 1,300 pCi/kg dry.
All other gamma emitters were less than the LLD.
E.
Land Use Census SYNOPSIS OF 2014 LAND USE CENSUS Ecology Ill, Inc. conducted a Land Use Census during the 2014 growing season around SSES to comply with the ODCM. The purpose of the survey was to document the nearest milk animal, residence and garden greater than 50 m2 (approximately 500 ft2) producing broad leaf vegetation within a distance of 8 km (approximately 5 miles) in each of the 16 meteorological sectors surrounding the SSES.
Distance in Miles from the PPL Reactor Buildings Nearest Nearest Nearest Residence Garden Dairy Farm Meteorological Sept, 2014 Sept, 2014 Sept, 2014 Sector miles miles miles 1
N 1.3 3.2
>5.0 2
NNE 1.0 2.3 a,c,e
>5.0 3
NE 0.9 2.7
>5.0 4
ENE 2.1 2.4 a,b,c
>5.0 5
E 1.4 4.3 4.5 d 6
ESE 0.5 3.1
>5.0 7
SE 0.5 0.6
>5.0 8
SSE 0.6 2.9
>5.0 9
s 1.0 3.1
>5.0 10 ssw 0.9 1.3
>5.0 11 sw 1.5 1.9
>5.0 12 WSW 1.3 1.3 1.7 d 13 w
1.2 2.0 5.0 14 WNW 1.1 1.3
>5.0 15 NW 0.8 0.9 a,c
>5.0 16 NNW 0.6 4.0
>5.0 a Chickens raised for consumption at this location b Ducks raised for consumption at this location c Eggs consumed from chickens at this location d Fruits/vegetables raised for consumption at this location e Beef cattle raised for consumption at this location The 2014 Land Use Census results are summarized in the above table.
There were two changes in the nearest garden census. Two new owners were identified for sectors 5 and 9.
V.
Annotations to Previous ARE OR There are no annotations to previous ARE OR.
VI.
Conclusions The Radiological Environmental Monitoring Program for SSES was conducted during 2014 in accordance with the SSES TRM and ODCM. The LLD values required by the TRM and ODCM were achieved for this reporting period (See Appendix A and Appendix C). The objectives of the program were also met c;:luring this period. The data collected assists in demonstrating that SSES was operated in compliance with TRM and ODCM requirements.
The concentration of radioactive material in the environment that could be attributable to SSES operations was only a small fraction of the concentration of naturally occurring and man-made radioactivity. Since these results were comparable to the results obtained during the preoperational phase of the program, which ran from 1972 to 1982, and with historical results collected since commercial operation, it is concluded that operation of the SSES had no significant radiological impact on the health and safety of the public or the environment.
From the results obtained, it can be concluded that the levels and fluctuations of radioactivity in environmental samples were as expected for the environment surrounding the SSES.
VII.
References
[1]
Ecology Ill, Inc. 2014. Susquehanna Steam Electric Station, 2014 Land Use Census. Prepared for PPL Susquehanna, LLC, Berwick, PA.
December 2014. Ecology Ill, Inc., Berwick, PA.
[2]
Ecology Ill, Inc. 2013~ Land Use Census, in Quality Assurance Program and Procedures for the Radiological Environmental Monitoring Program at the Susquehanna SES Environmental Laboratory. Revision 4-18 (Nov 2013). Ecology Ill, Inc., Berwick, PA.
[3]
Google Earth. 2014. Website: http://earth.google.com.
[4]
Pennsylvania Department of Transportation. 1990. Columbia County General Highway Map. PA DOT, Harrisburg, PA.
[5]
Pennsylvania Department of Transportation. 1990. Luzerne County General Highway Map. PA DOT, Harrisburg, PA.
[6]
PPL Susquehanna, LLC. 2013. Radiological Environmental Monitoring Program, ODCM-QA-008, Rev. 16 in Susquehanna Steam Electric Station Offsite Dose Calculation Manual, Docket Nos. 50-387 and 50-388.
[7]
Susquehanna Steam Electric Station, 5-mile radius aerial photograph, REMPE-182244-0. PPL Susquehanna, Berwick, PA
[8]
United States Geological Survey. 1976. Berwick Quadrangle Topographic Map. 7.5 minute series. USGS, Reston, VA.
[9]
United States Geological Survey. 1977. Sybertsville Quadrangle Topographic Map. 7.5 minute series. USGS, Reston, VA.
[1 0]
United States Nuclear Regulatory Commission. "An Acceptable Radiological Environmental Monitoring Program." Radiological Assessment Branch Technical Position. November 1979, Revision 1.
USNRC, Washington, DC.
[11]
Ecology Ill, "Susquehanna Steam Electric Station, 2013 Land Use Census", (November 2013).
[12]
PPL, "Engineering Study, EC-ENVR-1012 (Revision 2, February 2013)", Interpretation of Environmental Direct Radiation Results.
[13]
PPL, Tritium Release REMP Calculation (RETDAS) V.3.6.6) - March 2015.
[14]
NCRP Report No. 160, "Ionizing Radiation Exposure of the Population of the United States", (2009).
APPENDIX A PROGRAM
SUMMARY
A-1
Intentionally left blank A-2
TABLE A
SUMMARY
OF DATA FOR SSES OPERATIONAL RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM NAME OF FACILITY: SUSQUEHANNA STEAM ELECTRIC STATION J..OCATION OF FACILITY: LUZERNE COUNTY, PENNSYLVANIA Reporting Period: December 31, 2013 to January 09, 2015 ANALYSIS AND LOWER-LIMIT NUMBER OF MEDIUM OR PATHWAY TOTAL NUMBER OF ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NONROUTINE SAMPLED OF ANALYSIS DETECTION MEAN (3)
NAME MEAN (3)
MEAN (3)
REPORTED (UNIT OF MEASURE MEND PERFORMED (1)
(LLD) (2)
RANGE DISTANCE AND DIRECTim RANGE RANGE MEASURMENTS Air Particulates GR-B 312 10 1.279E+01 (208/208) 12E1 1.346E+01 (52/52) 1.206E+01 (104/104) 0 (E-3 pCitm")
(5.850E+OO-2.620E+01) 4.7 MILES WSW (8.040E+OO-2.620E+01)
(7.210E+OO-2.270E+01)
GAMMA 24 BE-7 24 N/A 9.204E+01 (16/16) 8G1 1.072E+02 (4/4) 1.025E+02 (8/8) 0 (5.176E+01-1.245E+02) 12 MILES SSE (8.125E+01 - 1.305E+02)
(7.504E+01 - 1.305E+02)
K-40 24 N/A 5.526E+OO (16/16) 12E1 1.047E+01 (4/4) 2.134E+OO (8/8) 0
(-3.116E+OO-1.903E+01) 4.7 MILES WSW (4.210E+OO-1.903E+01)
(-7.821E+OO-1.061E+01)
I w CS-134 24 50 2.083E-01 (16/16) 8G1 5.745E-01 (4/4) 4.723E-01 (8/8) 0
(-7.791 E 1.323E+OO) 12 MILES SSE
(-1.340E 1.656E+OO)
(*1.340E 1.656E+OO)
CS-137 24 60 1.774E-02 (16/16) 12S1 1.813E-01 (4/4)
-2.856E-01 (8/8) 0
(*5.534E 3.369E-01) 0.4 MILES WSW
(*1.536E 3.369E-01)
(-6.181E 3.742E-01)
Charcoal GAMMA 312 (E-3 pCi/m")
1-131 312 70
-7.098E-02 (208/208) 3S2 2.392E-01 (52/52)
-8.529E-01 (104/104) 0
(-1.503E+01-1.075E+01) 0.5 MILESNE
(-1.472E+01-9.831E+OO) (-1.329E+01-1.112E+01)
Ambient Radiation OSLO 226 N/A 20.4 (206/206) 9S2 42.4 (4/4) 18.4 (19/19) 0 (mRistd. qtr.)
(12.5-48.9) 0.2MILESS (39.0 - 48.9)
(13.6-25.4)
Milk 1-131 60 1
-1.751E-01 (40/40) 10G1
-1.155E-01 (20/20)
-1.155E-01 (20/20) 0 (pCi/1)
(-7.160E 1.440E-01) 14 MILES SSW
(-3.750E 2.130E-01)
(*3.750E 2.130E-01)
GAMMA 60 K-40 60 N/A 1.340E+03 (40/40) 13E3 1.343E+03 (20/20) 1.254E+03 (20/20) 0 (1.171 E+03 - 1.576E+03) 5.0MILESW (1.171 E+03 - 1.576E+03)
(1.009E+03 - 1.401 E+03)
CS-134 60 15
-1.647E+OO (40/40) 5E2
-1.580E+OO (20/20)
-2.071E+OO (20/20) 0
(-8.591 E+OO
- 3.323E+OO) 4.SMILES E
(-8.591E+OO-3.323E+OO) (-5.901E+OO
- 9.930E-01)
TABlE A
SUMMARY
OF DATA FOR SSES OPERATIONAL RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM NAME OF FACILITY: SUSQUEHANNA STEAM ELECTRIC STATION LOCATION OF FACILITY: LUZERNE COUNTY, PENNSYLVANIA Reporting Period: December 31, 2013 to January 09, 2015 ANALYSIS AND LOWER LIMIT NUMBER OF MEDIUM OR PATHWAY TOTAL NUMBER OF ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NONROUTINE SAMPLED OF ANALYSIS DETECTION MEAN (3)
NAME MEAN (3)
MEAN (3)
REPORTED (UNIT OF MEASUREMEND PERFORMED (1)
(LLD) (2)
RANGE DISTANCE AND DIRECTim RANGE RANGE MEASURMENTS Milk (cont'd)
CS-137 60 18 2.657E-01 (40/40) 10G1 3.911E-01 (20/20) 3.911E-01 (20/20) 0 (pCI/1)
(-3.494E+OO-3.727E+OO) 14 MILES SSW
(-3.068E+OO - 3.4BBE+OO) (-3.068E+OO - 3.488E+OO)
BA-140 60 60 3.720E-01 (40/40) 10G1 4.435E+OO (20/20) 4.435E+OO (20/20) 0
(-1.949E+01 - 1.710E+01) 14 MILES SSW
(-7.567E+OO-1.983E+01) (-7.567E+OO-1.983E+01)
LA-140 60 15
-3.036E-01 (40/40) 5E2 3.612E-01 (20/20)
-8.719E-01 (20/20) 0
(-7.380E+OO-3.880E+OO) 4.5 MILESE
(-4.934E+OO-3.805E+OO) (-7.461 E+OO-4.385E+OO)
TH-228 60 N/A 1.365E+OO (40/40) 5E2 1.957E+OO (20/20) 3.568E-01 (20/20) 0 I
.j:::..
(-6.931E+OO-9.891E+OO) 4.5 MILES E
(-4.043E+OO - 7.407E+OO) (-4.444E+OO - 7.027E+OO)
Ground Water H-3 59 2000 6.618E+01 (55/55) 4S8 1.867E+02 (4/4)
-2.573E+01 (4/4) 0 (pCI/1)
(-1.020E+02-2.240E+02) 0.1 MILES ENE (9.370E+01 - 2.240E+02)
(-4.490E+01-2.410E+01)
GAMMA 59 K-40 59 N/A 1.027E+01 (55/55) 6S11A 3.950E+01 (4/4) 1.639E+01 (4/4) 0
(-4.557E+01 - 1.013E+02)
(-2.014E+01 - 1.013E+02) (-7.285E+01 - 5.531 E+01)
MN-54 59 15
-6.711E-02 (55/55) 12F3 1.234E+OO (4/4) 1.234E+OO (4/4) 0
(-2.899E+OO-1.988E+OO) 5.2 MILES WSW
(-2.449E+OO-4.516E+OO) (-2.449E+OO-4.516E+OO)
C0-58 59 15
-3.638E-01 (55/55) 6S10 6.573E-01 (4/4)
-1.262E+OO (4/4) 0
(-3.243E+OO-2.345E+OO) 0.4 MILES ESE
(-1.380E+OO-2.158E+OO) (-2.043E+OO-3.860E-02)
FE-59 59 30 4.389E-01 (55/55) 2S2 4.939E+OO (4/4) 6.933E-01 (4/4) 0
(-1.15BE+01-6.619E+OO) 0.9 MILES NNE (2.728E+OO-6.619E+OO)
(-3.741E+OO-3.341E+OO)
C0-60 59 15 2.962E-01 (55/55) 2S2 9.561E-01 (4/4)
-3.085E-01 (4/4) 0
(-4.106E+OO-5.000E+OO) 0.9 MILES NNE (1. 719E 2.025E+OO)
(-2.503E+OO-2.149E+OO)
TABLE A
SUMMARY
OF DATA FOR SSES OPERATIONAL RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM NAME OF FACILITY: SUSQUEHANNA STEAM ELECTRIC STATION LOCATION OF FACILITY: LUZERNE COUNTY, PENNSYLVANIA Reporting Period: December 31, 2013 to January 09, 2015 ANALYSIS AND LOWER LIMIT NUMBER OF MEDIUM OR PATHWAY TOTAL NUMBER OF ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NONROUTINE SAMPLED OF ANALYSIS DETECTION MEAN (3)
NAME MEAN (3)
MEAN (3)
REPORTED (UNIT OF MEASUREMEN!2 PERFORMED (1)
(LLD~ (2)
RANGE DISTANCE AND DIRECTim RANGE RANGE MEASURMENTS Ground Water (cont'd)
ZN-65 59 30
-3.256E+OO (55/55) 1S3
-2.933E-01 (4/4)
-5.287E+OO (4/4) 0 (pCi/1)
(-1.063E+01 - 3.444E+OO) 0.1 MILES N
(-4.706E+OO-3.444E+OO) (-1.214E+01-1.509E+OO)
NB-95 59 15 4.793E-01 (55/55) 6810 2.159E+OO (4/4) 1.003E+OO (4/4) 0
(-5.307E+OO-4.254E+OO) 0.4 MILES ESE (6.514E 3.671 E+OO)
(-3.144E+OO-3.401E+OO)
ZR-95 59 30
-4.386E-01 (55/55) 12F3 1.314E+OO (4/4) 1.314E+OO (4/4) 0
(-7.789E+OO-6.424E+OO) 5.2 MILES WSW
(-2.707E+OO - 4.230E+OO) (-2.707E+OO - 4.230E+OO) 1-131 59 15 4.536E-01 (55/55) 7S11 2.854E+OO (4/4)
-2.303E+OO (4/4) 0 I Vl
(-1.120E+01-8.701E+OO)
(1.215E+OO-4.462E+OO)
(-3.782E+OO- -4.517E-01)
CS-134 59 15
-1.202E+OO (55/55) 7S10 4.910E-01 (4/4)
-1.375E+OO (4/4) 0
(-7.009E+OO-2.310E+OO) 0.3 MILESSE
(-5.939E 2.310E+OO) (-6.878E+OO-1.547E+OO)
CS-137 59 18
-3.649E-01 (55/55) 7511 7.196E-01 (4/4)
-1.244E+OO (4/4) 0
(-5.956E+OO - 3.140E+OO)
(-7.209E 3.140E+OO)
(-3.034E+OO-1.296E-01)
BA-140 59 60 4.853E-01 (55/55) 7811 3.970E+OO (4/4)
-5.153E+OO (4/4) 0
(-2.274E+01 - 1.680E+01)
(-2.118E+OO-1.009E+01) (-2.182E+01-5.189E+OO)
LA-140 59 15
-1.903E-01 (55/55) 7811 1.781E+OO (4/4) 4.828E-01 (4/4) 0
(-5.338E+OO-5.774E+OO)
(-1.412E+OO-5.774E+OO) (-2.975E+OO-4.087E+OO)
TH-228 59 N/A 4.262E-01 (55/55) 6S11A 2.238E+OO (4/4) 2.134E+OO (4/4) 0
(-9.340E+OO - 6.755E+OO)
(-3.195E+OO-6.755E+OO) (-2.408E+OO-8.274E+OO)
Potable Water GR-B 12 4
1.842E+OO (12112) 12H2 1.842E+OO (12112)
.OOOE+OO 0
(pCi/1)
(9.640E 3.320E+OO) 26MILESWSW (9.640E 3.320E+OO)
H-3 12 2000 1.931E+01 (12112) 12H2 1.931E+01 (12/12)
.OOOE+OO 0
(-8.280E+01-7.740E+01) 26MILESWSW
(-8.280E+01 - 7.740E+01)
TABLE A
SUMMARY
OF DATA FOR SSES OPERATIONAL RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM NAME OF FACILITY: SUSQUEHANNA STEAM ELECTRIC STATION LOCATION OF FACILITY: LUZERNE COUNTY, PENNSYLVANIA Reporting Period: December 31, 2013 to January 09, 2015 ANALYSIS AND LOWER LIMIT NUMBER OF MEDIUM OR PATHWAY TOTAL NUMBER OF ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NONROUTINE SAMPLED OF ANALYSIS DETECTION MEAN (3)
NAME MEAN (3)
MEAN (3)
REPORTED (UNIT OF MEASUREMENT) PERFORMED (1)
(LLD) (2)
RANGE DISTANCE AND DIRECTim RANGE RANGE MEASURMENTS Potable Water (cont'd)
GAMMA 12 (pCi/1)
K-40 12 N/A
-8.802E+OO (12/12) 12H2
-8.802E+OO (12/12)
.OOOE+OO 0
(-1.264E+02-4.268E+01) 26MILESWSW
(-1.264E+02-4.268E+01)
MN-54 12 1p 6.455E-02 (12/12) 12H2 6.455E-02 (12/12)
.OOOE+OO 0
(-3.737E 8.250E-01) 26MILESWSW
(-3.737E 8.250E-01)
C0-58 12 15 8.895E-02 (12/12) 12H2 8.895E-02 (12/12)
.OOOE+OO 0
(-6.293E 7.961 E-01) 26MILESWSW
(-6.293E 7.961 E-01)
I 0"1 FE-59 12 30 3.757E-01 (12/12) 12H2 3.757E-01 (12/12)
.OOOE+OO 0
(-1.801 E+OO-4.212E+OO) 26 MILES WSW
(-1.801E+OO-4.212E+OO)
C0-60 12 15 4.205E-01 (12/12) 12H2 4.205E-01 (12/12)
.OOOE+OO 0
(-4.212E 1.612E+OO) 26 MILES WSW
(-4.212E 1.612E+OO)
ZN-65 12 30
-1.108E+OO (12/12) 12H2
-1.108E+OO (12/12)
.OOOE+OO 0
(-6.013E+OO-1.274E+OO) 26MILESWSW
(-6.013E+OO-1.274E+OO)
NB-95 12 15 5.191E-01 (12/12) 12H2 5.191 E-01 (12/12)
.OOOE+OO 0
(-4.532E 1.697E+OO) 26MILESWSW
(-4.532E 1.697E+OO}
ZR-95 12 30 2.979E-03 (12/12) 12H2 2.979E-03 (12/12)
.OOOE+OO 0
(-1.850E+OO-1.658E+OO) 26MILESWSW
(-1.850E+OO-1.658E+OO) 1-131 12 15 1.843E-01 (12/12) 12H2 1.843E-01 (12/12)
.OOOE+OO 0
(-2.154E+OO-3.847E+OO) 26MILESWSW
(-2.154E+OO-3.847E+OO)
CS-134 12 15
-6.900E-01 (12/12) 12H2
-6.900E-01 (12/12)
.OOOE+OO 0
(-3.169E+OO-1.477E-01) 26MILESWSW
(-3.169E+OO-1.477E-01)
TABLE A
SUMMARY
OF DATA FOR SSES OPERATIONAL RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM NAME OF FACILITY: SUSQUEHANNA STEAM ELECTRIC STATION LOCATION OF FACILITY: LUZERNE COUNTY, PENNSYLVANIA Reporting Period: December 31, 2013 to January 09, 2015 ANALYSIS AND LOWER LIMIT NUMBER OF MEDIUM OR PATHWAY TOTAL NUMBER OF ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NONROUTINE SAMPLED OF ANALYSIS DETECTION MEAN (3)
NAME MEAN (3)
MEAN (3)
REPORTED (UNIT OF MEASUREMENn PERFORMED (1)
(LLD) (2)
RANGE DISTANCE AND DIRECTim RANGE RANGE MEASURMENTS Potable Water (cont'd)
CS-137 12 18 6.925E-02 (12/12) 12H2 6.925E-02 (12112)
.OOOE+OO 0
{pCin)
(-9.473E 8.542E-01) 26MILESWSW
(-9.473E 8.542E-01)
BA-140 12 60
-1.865E+OO (12112) 12H2
-1.865E+OO (12112)
.OOOE+OO 0
(-1.298E+01 - 4.632E+OO) 26MILESWSW
(-1.298E+01-4.632E+OO)
LA-140 12 15 1.879E-02 (12/12) 12H2 1.879E-02 (12/12)
.OOOE+OO 0
(-2.452E+OO - 2.258E+OO) 26MILESWSW
(-2.452E+OO-2.258E+OO)
Food/Garden Crops GAMMA 43 I.....:.
(pCi/kg wet)
BE-7 43 N/A 2.676E+02 (31/31) 3S3 3.296E+02 (16/16) 2.684E+02 (12/12) 0
(-7.527E+01 - 7.254E+02) 0.9MtLES NE
(-3.024E+OO-7.254E+02) (2.424E+01 - 5.316E+02)
K-40 43 N/A 6:o34E+03 (31/31) 11S6 6.048E+03 (15/15) 4.945E+03 (12112) 0 (3.837E+03 - 8.566E+03)
O.SMILESSW (3.837E+03 - 8.566E+03)
(3.397E+03 - 6.548E+03)
MN-54 43 N/A
-1.729E+OO (31/31) 11S6
-1.214E+OO (15/15)
-2.006E+OO (12112) 0
(-1.124E+01-9.815E+OO)
O.SMILESSW
(-1.028E+01-9.815E+OO) {-6.834E+OO-4.982E+OO)
C0-58 43 N/A 1.210E+OO (31/31) 3S3 2.542E+OO
{16/16)
-1.239E+OO (12112) 0
(-1.378E+01 - 1.305E+01) 0.9MILES NE
(-4.598E+OO-1.305E+01) (-9.362E+OO-8.917E+OO)
FE-59 43 N/A 5.537E+OO (31/31) 383 7.635E+OO (16/16)
-3.334E-01 (12112) 0
(-1.931E+01-5.459E+01) 0.9MILES NE
(-1.931E+01-5.459E+01) (-1.957E+01-1.554E+01)
C0-60 43 N/A 4.354E-01 (31/31) 8G1 2.827E+OO (12112) 2.827E+OO (12112) 0
(-9.726E+OO-2.910E+01) 12 MILES SSE
(-5.741E+OO-9.391E+OO) (-5.741E+OO-9.391E+OO)
ZN-65 43 N/A
-1.521E+01 (31/31) 8G1
-1.119E+01 (12/12)
-1.119E+01 (12112) 0
(-6.832E+01 ~ 1.286E+01) 12 MILES SSE
(-3.571 E+01 - 1.240E+01) (-3.571 E+01 - 1.240E+01)
TABLE A
SUMMARY
OF DATA FOR SSES OPERATIONAL RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM NAME OF FACILITY: SUSQUEHANNA STEAM ELECTRIC STATION LOCATION OF FACILITY: LUZERNE COUNTY, PENNSYLVANIA Reporting Period: December 31, 2013 to January 09, 2015 ANALYSIS AND LOWER LIMIT NUMBER OF MEDIUM OR PATHWAY TOTAL NUMBER OF ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NON ROUTINE SAMPLED OF ANALYSIS DETECTION MEAN (3)
NAME MEAN (3)
MEAN (3)
REPORTED (UNIT OF MEASUREMEN] PERFORMED (1)
~LLD) (2)
RANGE DISTANCE AND DIRECTim RANGE RANGE MEASURMENTS Food/Garden Crops (cont'd) NB-95 43 N/A 3.896E+OO (31/31) 8G1 6.361E+OO (12112) 6.361E+OO (12/12) 0 (pCi/kg wet)
(-9.075E+OO-2.819E+01) 12 MILES SSE
(-5.951E+OO-2.408E+01) (-5.951E+OO - 2.408E+01)
ZR-95 43 N/A
-4.594E+OO (31/31) 11S6
-1.510E+OO (15/15)
-3.606E+OO (12/12) 0
(-4.471 E+01 - 2.062E+01) 0.5MILESSW
(-2.943E+01-2.062E+01) (-1.742E+01-1.349E+01) 1-131 43 60 1.109E+OO (31/31) 8G1 3.918E+OO (12112) 3.918E+OO (12112) 0
(-1.460E+01 - 2.736E+01) 12 MILES SSE
(-2.101E+01-1.921E+01) (-2.101E+01-1.921E+01)
CS-134 43 60
-6.011E+OO (31/31) 8G1
-4.311E+OO (12112)
-4.311E+OO (12112) 0 I 00
(-2.824E+01-1.189E+01) 12 MILES SSE
(-1.691E+01-1.043E+01) (-1.691E+01-1.043E+01)
CS-137 43 80 4.107E-01 (31/31) 3S3 5.340E-01 (16/16) 5.073E-01 (12112) 0
(-1.281E+01-1.004E+01) 0.9 MILESNE
(-8.977E+OO-1.004E+01) (-1.423E+01-8.437E+OO)
BA-140 43 N/A 4.095E+OO (31/31) 8G1 1.103E+01 (12112) 1.103E+01 (12112) 0
(-3.395E+01 - 5.377E+01) 12 MILES SSE
(-4.126E+01-4.971E+01) (-4.126E+01-4.971E+01)
LA-140 43 N/A
-8.006E-01 (31/31) 383 2.451E-02 (16/16)
-4.344E-01 (12112) 0
(-1.969E+01 - 1.119E+01) 0.9 MILESNE
(-1.969E+01 - 1.119E+01) (-9.554E+OO-8.407E+OO)
AC-228 43 N/A 1.014E+01 (31/31) 3S3 1.208E+01 (16/16) 3.504E+OO (12112) 0
(-5.352E+01 - 9.599E+01) 0.9MILES NE
(-4.094E+01-9.599E+01) (-3.536E+01-4.671E+01)
TH-228 43 N/A 1.046E+01 (31/31) 8G1 1.362E+01 (12/12) 1.362E+01 (12112) 0
(-2.046E+01 - 6.337E+01) 12MILES SSE
(-4.155E+OO-3.961E+01) (-4.155E+OO-3.961E+01)
Soil GAMMA 6
(pCI/kg dry)
K-40 6
NIA 1.391E+04 (3/3) 12S1 1.391E+04 (3/3) 1.188E+04 (3/3) 0 (1.282E+04-1.552E+04) 0.4 MILES WSW (1.282E+04-1.552E+04) (7.911E+03-1.393E+04) cs-134 6
150 2.867E+OO (3/3) 8G1 3.611E+01 (3/3) 3.611E+01 (3/3) 0
(-5.293E+01 - 7.844E+01) 12MILES SSE
(-2.275E+01 - 1.370E+02) (-2.275E+01 - 1.370E+02)
TABLE A
SUMMARY
OF DATA FOR SSES OPERATIONAL RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM NAME OF FACILITY: SUSQUEHANNA STEAM ELECTRIC STATION LOCATION OF FACILITY: LUZERNE COUNTY, PENNSYLVANIA Reporting Period: December 31, 2013 to January 09, 2015 ANALYSIS AND LOWER LIMIT NUMBER OF MEDIUM OR PATHWAY TOTAL NUMBER OF ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NONROUTINE SAMPLED OF ANALYSIS DETECTION MEAN (3)
NAME MEAN (3)
MEAN (3)
REPORTED (UNIT OF MEASUREMENn PERFORMED (1)
(LLD) (2)
RANGE DISTANCE AND DIRECTim RANGE RANGE MEASURMENTS Soil (cont'd)
C$-137 6
180 1.027E+02 (3/3) 12S1 1.027E+02 (3/3) 5.091E+01 (3/3) 0 (pCilkg dry)
(3.359E+01-1.756E+02) 0.4 MILES WSW (3.359E+01 - 1.756E+02)
(3.599E+01 - 7.834E+01)
RA-226 6
N/A 1.714E+03 (3/3) 8G1 2.057E+03 (3/3) 2.057E+03 (3/3) 0 (7.506E+02-2.456E+03) 12MILESSSE (3.736E+02-3.122E+03)
(3.736E+02-3.122E+03)
AC-228 6
N/A 1.100E+03 (3/3) 12S1 1.100E+03 (3/3) 9.595E+02 (3/3) 0 (1.022E+03-1.151E+03) 0.4 MILES WSW (1.022E+03-1.151E+03)
(7.185E+02 - 1.393E+03)
TH-228 6
N/A 1.298E+03 (3/3) 12S1 1.298E+03 (3/3) 1.062E+03 (3/3) 0 I 1.0 (9. 770E+02-1.600E+03) 0.4 MILES WSW (9.770E+02-1.600E+03)
(5.208E+02 - 1.565E+03)
Surface Water H-3 62 2000 9.186E+02 (45/45) 2S7 2.676E+03 (15/15) 1.825E+01 (17/17) 0 (pCi/1)
(-7.330E+01-1.150E+04) 0.1 MILES NNE (7.370E+01-1.150E+04)
(-8.000E+01 - 1.130E+02)
GAMMA 62 K-40 62 N/A
-3.091E-02 (45/45) 5S9 2.416E+01 (2/2)
-9.996E+OO (17117) 0
(-1.446E+02-5.416E+01) 0.8 MILES E (9.515E+OO-3.881E+01)
(-1.222E+02-8.986E+01)
MN-54 62 15
-2.277E-01 (45/45)
LTAW 4.853E-02 (4/4) 1.001E-02 (17/17) 0
(-3.1 02E+OO-2.213E+00) 0.7 MILES NE
(-1.543E+OO-8.776E-01) (-8.428E 8.827E-01)
C0-58 62 15 1.027E-01 (45/45) 4S7 1.488E+OO (4/4)
-7.428E-02 (17/17) 0
(-4.326E+OO-3.272E+OO) 0.4 MILES ENE (3.528E 3.272E+OO)
(-1.619E+OO-9.776E-01)
FE-59 62 30
-9.799E-02 (45/45)
LTAW 2.244E+OO (4/4)
-2.639E-02 (17/17) 0
(-8.763E+OO-4.240E+OO) 0.7MILES NE
(-8.753E 4.240E+OO)
(-2.153E+OO-2.974E+OO)
C0-60 62 15 1.872E-01 (45/45) 5S12 8.048E-01 (4/4) 3.989E-01 (17/17) 0
(-3.462E+OO - 2.901 E+OO) 0.4 MILES E
(-4.814E 1.995E+OO)
(-5.821E 1.754E+OO)
TABLE A
SUMMARY
OF DATA FOR SSES OPERATIONAL RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM NAME OF FACILITY: SUSQUEHANNA STEAM ELECTRIC STATION LOCATION OF FACILITY: LUZERNE COUNTY, PENNSYLVANIA Reporting Period: December 31, 2013 to January 09, 2015 ANALYSIS AND LOWER LIMIT NUMBER OF MEDIUM OR PATHWAY TOTAL NUMBER OF ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NONROUTINE SAMPLED OF ANALYSIS DETECTION MEAN (3)
NAME MEAN (3)
MEAN (3)
REPORTED (UNIT OF MEASUREMEN] PERFORMED ~1)
(LLD) (2)
RANGE DISTANCE AND DIRECTim RANGE RANGE MEASURMENTS Surface Water (cont'd)
ZN-65 62 30
-1.853E+OO (45/45) 7812 9.220E-01 (4/4)
-7.112E-01 (17/17) 0 (pCi/1)
(-8.975E+OO-5.301E+OO) 0.3 MILESSE
(-2.043E+OO-5.301E+OO) (-3.865E+OO-2.529E+OO)
NB-95 62 15 2.968E-01 (45/45) 7S12 1.309E+OO (4/4) 4.255E-01 (17/17) 0
(-3.352E+OO - 4.606E+OO) 0.3 MILESSE
(-2.273E+OO-4.606E+OO) (-4.640E 1.732E+OO)
ZR-95 62 30 3.242E-01 (45/45) 7S12 2.211E+OO (4/4) 4.194E-01 (17/17) 0
(-2.960E+OO - 7.017E+OO) 0.3 MILESSE
(-2.293E+OO-7.017E+OO) (-1.960E+OO-3.161E+OO)
I 1-131 61 15 5.014E-01 (44/44) 5S9 4.775E+OO (1/1) 7.522E-01 (17/17) 0 0
(-6.590E+OO-7.356E+OO) 0.8 MILES E (4.775E+OO)
(-7.222E+OO-1.127E+01)
CS-134 62 15
-1.264E+OO (45/45) 6S5
-5.320E-01 (12/12)
-9.929E-01 (17/17) 0
(-8.213E+OO - 2.938E+OO) 0.9 MILES ESE
(-2.941E+OO-3.227E-01) (-3.560E+OO-7.650E-01)
CS-137 62 18 8.895E-02 (45/45) 5S12 7.478E-01 (4/4)
-3.778E-02 (17/17) 0
(-3.873E+OO - 3.084E+OO) 0.4 MILES E
(-6.704E 3.084E+OO)
(-6.782E 5.440E-01)
BA-140 62 60 1.015E+OO (45/45) 7S12 3.342E+OO (4/4) 2.072E+OO (17/17) 0
(-1.646E+01-1.719E+01) 0.3MILES SE
(-5.520E+OO-1.719E+01) (-7.534E+OO-8.427E+OO)
LA-140 62 15
-5.522E-01 (45/45)
LTAW 1.950E-03 (4/4)
-2.951E-01 (17/17) 0
(*6.013E+OO-3.583E+OO) 0.7MILES NE
(-2.869E+OO-3.583E+OO) (-5.267E+OO
- 2.599E+OO)
TH-228 63 N/A 2.101E-01 (46/46) 7S12 9.741E-01 (4/4) 4.604E-01 (17/17) 0
(-7.178E+OO - 5.771E+OO) 0.3 MILES SE (2.861 E 1.941 E+OO)
(-4.408E+OO-3.997E+OO)
Fish GAMMA 15 (pCi/kg wet)
K-40 15 N/A 4.185E+03 (8/8)
IND 4.313E+03 (717) 4.084E+03 (7/7) 0 (3.103E+03-6.178E+03) 0.9-1.4 MILES ESE (3.103E+03-6.178E+03)
(2.636E+03-5.083E+03)
MN-54 15 130
-4.662E+OO (8/8)
IND
-1.709E+OO (7/7)
-2.030E+OO (717) 0
(-2.533E+01 - 2.151E+01) 0.9-1.4 MILES ESE
(-1.681E+01-2.151E+01) (-2.870E+01-3.452E+01)
TABLE A
SUMMARY
OF DATA FOR SSES OPERATIONAL RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM NAME OF FACILITY: SUSQUEHANNA STEAM ELECTRIC STATION LOCATION OF FACILITY: LUZERNE COUNTY, PENNSYLVANIA Reporting Period: December 31, 2013 to January 09, 2015 ANALYSIS AND LOWER LIMIT NUMBER OF MEDIUM OR PATHWAY TOTAL NUMBER OF ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NON ROUTINE SAMPLED OF ANALYSIS DETECTION MEAN (3)
NAME MEAN (3)
MEAN (3)
REPORTED (UNIT OF MEASUREMENT) PERFORMED (1)
(LLD) (2)
RANGE DISTANCE AND DIRECTim RANGE RANGE MEASURMENTS Fish (cant' d)
C0-58 15 130
-9.167E+OO (8/8) 2H 1.752E+01 (7/7) 1.752E+01 (717) 0 (pCi/kg wet)
(-2.904E+01 - 3.049E+01) 30 MILES NNE
(-3.479E+OO-6.651E+01) (-3.479E+OO-6.651E+01)
FE-59 15 260 1.690E+01 (8/8)
LTAW 4.898E+01 (1/1)
-1.575E+01 (717) 0
(-8.308E+01 - 6.687E+01) 0.7 MILESNE (4.898E+01)
(-9.126E+01 - 4.909E+01)
C0-60 15 130
-1.255E-01 (8/8) 2H 7.097E+OO (717) 7.097E+OO (7/7) 0
(-2.503E+01 - 2.269E+01) 30 MILES NNE
(-1.425E+01-3.607E+01) (-1.425E+01-3.607E+01)
- t>
I ZN-65 15 260
-6.021E+01 (8/8)
LTAW 5.417E+OO (1/1)
-1.634E+01 (7/7) 0
(-1.153E+02-2.040E+01) 0.7MILES NE (5.417E+OO)
(-7.934E+01 - 4.821E+01)
CS-134 15 130
-1.883E+01 (8/8)
LTAW
-1.168E+0.1 (1/1)
-2.069E+01 (7/7) 0
(-5.200E+01
- 2.159E+01) 0.7 MILES NE
(-1.168E+01)
(-9.304E+01-1.916E+01)
CS-137 15 150 1.096E+01 (8/8)
IND 1.416E+01 (7/7)
-1.975E+01 (7/7) 0
(-4.966E+01-6.935E+01) 0.9-1.4 MILES ESE
(-4.966E+01 - 6.935E+01) (-5.620E+01-2.742E+01)
Sediment GAMMA 7
(pCi/kg dry)
K-40 7
NIA 1.227E+04 (4/4) 2B 1.587E+04 (3/3) 1.587E+04 (3/3) 0 (1.062E+04-1.412E+04) 1.6 MILES NNE (1.397E+04-1.686E+04) (1.397E+04 - 1.686E+04)
CS-134 7
150
-1.038E+OO (4/4) 2B 1.864E+01 (3/3) 1.864E+01 (3/3) 0
(-2.696E+01 - 3.375E+01) 1.6 MILES NNE
(-1.709E+OO-4.202E+01) (-1.709E+OO-4.202E+01)
CS-137 7
180 2.104E+01 (4/4) 2B 4.220E+01 (3/3) 4.220E+01 (3/3) 0
(-1.115E+01-6.190E+01) 1.6 MILES NNE (3.632E+01 - 4.676E+01)
(3.632E+01 - 4.676E+01)
RA-226 7
N/A 1.468E+03 (4/4) 2B 2.128E+03 (3/3) 2.128E+03 (3/3) 0 (7.992E+02-2.378E+03) 1.6 MILES NNE (1.915E+03-2.524E+03)
(1.915E+03-2.524E+03)
I N.
ANALYSIS AND MEDIUM OR PATHWAY TOTAL NUMBER SAMPLED OF ANALYSIS (UNIT OF MEASUREMENn PERFORMED (1)
Sediment (cont'd)
(pCi/kg dry)
AC-228 TH-228 7
7 TABLE A
SUMMARY
OF DATA FOR SSES OPERATIONAL RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM NAME OF FACILITY: SUSQUEHANNA STEAM ELECTRIC STATION LOCATION OF FACILITY: LUZERNE COUNTY, PENNSYLVANIA Reporting Period: December 31, 2013 to January 09, 2015 LOWER LIMIT OF ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN DETECTION MEAN (3)
NAME MEAN (3)
(LLD) (2)
RANGE DISTANCE AND DIRECTim RANGE CONTROL LOCATION MEAN (3)
RANGE N/A 1.130E+03 (4/4) 28 1.262E+03 (3/3) 1.262E+03 (3/3)
(1.021 E+03 - 1.223E+03) 1.6 MILES NNE (9.428E+02-1.423E+03)
(9.428E+02 - 1.423E+03)
N/A 1.269E+03 (4/4) 2B 1.538E+03 (3/3) 1.538E+03 (3/3)
(1.027E+03 - 1.628E+03) 1.6 MILES NNE (1.221E+03-1.858E+03)
(1.221E+03 - 1.858E+03)
- 1. The total number of analyses does not include duplicates, splits or repeated analyses.
- 2. The Technical Requirement LLDs are shown when applicable.
NUMBER OF NONROUTINE REPORTED MEASURMENTS 0
0
- 3. The mean and range are based on all available measure results. The ratio Indicated in parentheses Is the total number of results used to calculate the mean to the total number of samples.
- 4. USNRC Reporting Levels are specified in the Technical Requirmeents (i.e., when Reporting Levels in Technical Requirements are exceeded).
APPENDIXB SAMPLE DESIGNATION AND LOCATIONS B-1
Intentionally left blank B-2
SAMPLE DESIGNATION All distances from the SSES to monitoring locations are measured from the standby gas treatment vent at 44200/N34117 (Pa. Grid System). The location codes are based on both distance and direction from the SSES. The letters in the location codes indicate if the monitoring locations are on site (within the site boundary) or, if they are not on site, the approximate distances of the location from the SSES as described below:
s
= On site E
= 4-5 miles A
= < 1 mile F
= 5-10 miles B
= 1-2 miles G
= 10-20 miles c
= 2-3 miles H
= > 20 miles D
= 3-4 miles The numbers preceding the letters in the location codes provide the direction of the monitoring _locations from the SSES by indicating the sectors in which they are located. A total number of 16 sectors (numbered one through 16) equally divide an imaginary circle on a map of the SSES and its vicinity, with the SSES at the center of the circle. The middle of sector one is directed due North (N). Moving clockwise from sector one, the sector immediately adjacent to sector one is sector two, the middle of which is directed due north, north east (NNE). Continuing to move clockwise the sector number increases to 16, which is the north northwest sector (NNW).
B-3
TABLE 8-1 SAMPLING LOCATIONS Specific information about the individual sampling locations are given in Table B-1. Maps B-1 through B-6 show the locations of sampling stations with respect to the Site. A Portable Global Positioning
- System (GPS) was used to provide the coordinates of sampling locations.
STATION CODE STATION LOCATION LATITUDINAL LONGITUDINAL SAMPLE TYPE LESS THAN ONE MILE FROM THE SSES DEG.
DEG.
2S7 0.1 mi.NNE 41.093540
-76.144773 Surface water 5S9 0.8mi.E; 41.093292
-76.130472 Surface water 5S12 0.4 mi.E; 41.092540
-76.138704 Surface water 7S12 0.3 mi.SE; 41.088507
-76.143270 Surface water 6S5 0.9 mi.ESE; 41.084639
-76.130642 Surface water 6S6 **
0.8 mi.ESE; 41.088115
-76.131637 Surface water LTAW 0.7 mi.NE-ESE; 41.098356
-76.135401 Surface water to4S7 0.4 mi.ENE; 41.094418
-76.138236 Surface water I
+>-LTAW 0.7 mi.NE-ESE; 41.098356
-76.135401 Fish 12S1 0.4mi.WSW; 41.088436
-76.154314 Air 13S6 0.4mi.W; 41.091771
-76.153869 Air 3S2 0.5 miNE; 41.095716
-76.140207 Air 12S1 0.4mi.WSW; 41.088436
-76.154314 Soil 2S8 0.1 mi.NNE; 41.094991
-76.. 044207 Ground water 2S2 0.9 mi.NNE; 41.102243
-76.136702 Ground water 4S4 0.5 mi.ENE; 41.095471
-76.138798 Ground water 6S10 0.4 mi.ESE; 41.090511
-76.137802 Ground water 6S11A 0.4 mi.ESE; 41.083448
-76.133412 Ground water 6S11B 0.4 mi.ESE; 41.083448
-76.133411 Ground water 6S12 0.8 mi.ESE; 41.083411
-76.116935 Ground water 7S11 0.3mi.SE; 41.083527
-76.133513 Ground water 11S2 0.4 mi.SW; 41.088816
-76.152793 Ground water 1S3 0.1 miN; 41.093640
-76.146076 Ground water
- Control Location
(
TABLE B-1 (cont'd)
SAMPLING LOCATIONS STATION CODE STATION LOCATION LATITUDINAL LONGITUDINAL SAMPLE TYPE LESS THAN ONE MILE FROM THE SSES OEG.
OEG.
488 0.1 mi.ENE; 41.092306
-76.144283 Ground water 489 0.3mi.E; 41.093369
-76.141644 Ground water 884 0.1 mi.88E; 41.091424
-76.145531 Ground water 7810 0.3 mi.8E; 41.089736
-76.142783 Ground water 1387 0.2mi.W; 41.091236
-76.149647 Ground water 382 0.5 mi.NE; 41.095716
-76.140207 Precipitation 1281 0.4mi.W8W; 41.088436
-76.154314 Precipitation 1186 0.5mi.SW; 41.085305
-76.152022 8roadleaf 3S3 0.9 mi.NE; 41.101856
-76.133090 8rqadleaf 5810 0.7mi.E; 41.0.93899
-76.132814 8roadleaf
':p Site 1 0.1 mi.E8E;
- v.
41.092275
-76.145022 Precipitation 8ite2 0.1 mi.SSE; 41.091309
-76.145708 Precipitation Site 3 0.1 mi.WSW; 41.091243
-76.147345 Precipitation Site 4 0.1 mi.NW; 41.093321
-76.147316 Precipitation
,FROM ONE to FIVE MILES FROM THE SSES IND 0.9mi.ESE; 41.085141
-76.130174 Fish IND 1.4 mi.ESE; 41.075618
~76.132682 Fish 28 **
1.6 mi.NNE; 41.112441
-76.134758 Sediment 78 1.2 mi.SE; 41.078924
-76.131548 Sediment 12E1 4.7mi.WSW; 41.072418
-76.230554 Air 5E2 4.5mi.E; 41.085184
-76.061099 Milk 8C1 2.9 mi.SSE; 41.054518
-76.129027 8roadleaf 1085 1.3 mi.8SW; 41.075404
-76.157422 8roadleaf 1003 3.5mi.8SW; 41.045449
-76.171899 Milk 13E3 5.0mi.W; 41.100259
-76.241102 Milk 1101 3.3mi.8W; 41.055212
-76.186797 Food Products 11D2 3.5mi.SW; 41.054827
-76.205081 Food products
- Control Location
TABLE B-1 (cont'd)
SAMPLING LOCATIONS STATION CODE STATION LOCATION LATITUDINAL LONGITUDINAL SAMPLE TYPE GREATER THAN FIVE MILES FROM THE SSES DEG.
DEG.
12H2 26mi.WSW; 40.947192
-76.604524 Drinking water 2H **
30 mi. NNE; 41.459508
-75.853096 Fish 12F 6.9mi.WSW; 41.041323
-76.255396 Sediment 6G1 **
13.5 mi.ESE; 41.018989
-75.906515 Air 8G1 **
12 mi.SSE; 40.928886
-76.055092 Air 8G1 **
12 mi.SSE; 40.928886
-76.055092 Soil 8G1 **
12 mi.SSE; 40.928886
-76.055092 Precipitation 8G1 **
12mi.SSE; 40.928886
-76.055092 Broadleaf
- 10G1 **
14mi.SSW; 40.934847
-76.284449 Milk 12F3 **
5.2mi.WSW; 41.054491
-76.232176 Ground water tO 12F7 8.3mi.WSW; 41.036689
-76.286776 Food Products I 0\\ 11F2 S.Smi.SW; 41.045741
-76.242128 Food products 15G1 **
11.4 mi.NW; 41.188578
-76.324598 Broadleaf OSLO LOCATIONS LESS THAN ONE MILE FROM THE SSES 1S2 0.2mi.N; 41.09566
-76.146121 OSLO
.2S2 0.9 mi. NNE; 41.10207
-76.141192 OSLO 2S3 0.2 mi.NNE; 41.09486
-76.144101 OSLO 3S2 0.5 mi.NE; 41.09574
-76.140086 OSLO
.3S3 0.9 mi.NE; 41.10183
-76.133127 OSLO 4S3 0.2 mi.ENE; 41.09322
-76.141934 OSLO 4S6 0.7 mi. ENE; 41.09687
-76.133807 OSLO 5S4 0.8mi.E; 41.09286
-76.131604 OSLO 5S7 0.3mi.E; 41.09199
-76.141165 OSLO 6S4 0.2 mi.ESE; 41.09132
-76.142616 OSLO 6S9 0.2 mi.ESE; 41.09067
-76.142966 OSLO
'7S6 0.2 mi.SE; 41.08972
-76.14359 OSLO
- Control Location
TABLE B-1 (cont'd)
SAMPLING LOCATIONS STATION CODE STATION LOCATION LATITUDINAL LONGITUDINAL SAMPLE TYPE LESS THAN ONE MILE FROM THE SSES OEG.
OEG.
7S7 0.4 mi.SE; 41.08745
-76.142033 OSLO 8S2 0.2 mi.SSE; 41.08907
-76.14437 OSLO 9S2 0.2 mi.S; 41.08952
-76.14322 OSLO
- 10S1 0.4mi.SSW; 41.08663
-76.150082 OSLO 10S2 0.2mi.SSW; 41.08894
-76.147881 OSLD 1187 0.4 mi.SWN; 41.08832
-76.15297 OSLD 12S1 0.4mi.WSW; 41.0887
-76.154112 OSLO 12S3 0.4mi.WSW; 41.08968
-76.153192 OSLD 13S2 0.4mi.W; 41.09198
-76.153166 OSLO 13S5 0.4 mi.W; 41.09179
-76.153167 OSLD o::l13S6 0.4 mi.W; 41.09177
-76.154073 OSLD
~ : 14S5 0.5mi.WNW; 41.09503
-76.153787 OSLO 15S5 0.4 mi.NW; 41.09576
-76.15103 OSLO 16S1 0.3mi.NNW; 41.09611
-76.147388 OSLD 16S2 0.3mi.NNW; 41.09599
-76.148922 OSLD 6A4
- 0.6 mi.ESE; 41.08791
-76.136795 OSLO 8A3 0.9 mi.SSE; 41.07982
-76.1139078 OSLD 15A3.
0.9mi.NW; 41.10003
-76.1585 OSLD 16A2.
0.8mi.NNW; 41.1025
-76.151595 OSLO FROM ONE to FIVE MILES FROM THE SSES 12S7 1.1 mi.WSW; 41.08621
-76.165914 OSLD 882.
1.4 mi.SSE; 41.07483
-76.130724 OSLO 981 1.3mi.S; 41.07356
-76.147874 OSLD 1083.
1.7mi.SSW; 41.07064
-76.156646 OSLD 105 4.0 mi.N; 41.14936
-76.144346 OSLD 8D3 4.0 mi.SSE; 41.03824
-76.121683 OSLO
- Special Interest Area (other than controls)
- STATION CODE STATION LOCATION
- FROM ONE to FIVE MILES FROM THE SSES 904 3.6mi.S; 1001 3.0mi.SSW; 1202 3.7mi.WSW; 1401 3.6mi.WNW; 3E1 4.7 miNE; 4E2 4.7 mi.ENE; 5E2 4.5mi. E; 6E1 4.7 mi.ESE; 7E1 4.2 mi.SE; 11E1 4.7 mi. SW; to 12E1
- 4.7 mi.WSW; I 00 13E4 4.1 mi.W;
- GREATER THAN FIVE MILES FROM THE SSES 2F1 5.9 mi. NNE; 15F1 5.4 mi.NW; 16F1 7.8mi.NNW; 3G4 **
17 mi.NE; 4G1 **
14 mi.ENE; 7G1 **
14 mi.SE; 12G1 **
15mi.WSW; 12G4 **
10mi.WSW;
- Special Interest Area (other than controls)
- Control Location TABLE B-1 (cont'd)
SAMPLING LOCATIONS LATITUDINAL LONGITUDINAL SAMPLE TYPE OEG.
OEG.
41.04015
-76.144529 OSLO 41.05446
-76.175026 OSLO 41.07363
-76.213306 OSLO 41.10706
-76.211891 OSLO 41.13953
-76.082398 OSLO 41.12157
-76.064115 OSLO 41.08539
-76.060486 OSLO 41.07275
-76.059529 OSLO 41.04891
-76.090309 OSLO 41.05188
-76.218713 OSLO 41.0725
-76.230331 OSLO 41.08962
-76.223726 OSLO 41.16796
-76.09146 OSLO 41.15595
-76.202506 OSLO 41.18985
-76.229283 OSLO 41.23431
-76.869061 OSLO 41.13898
-75.885121 OSLO 40.94636
-76.974184 OSLO 41.0262
-76.411566 OSLO 40.03868
-76.327731 OSLO
TABLE B-2 SUSQUEHANNA STEAM ELECTRIC STATION RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Sample Analysis Sampling Method Collection Procedure Number Analytical Procedure Number Medium Ambient Dosimeter Quarterly SSES, HP-TP-205 Landauer Procedure L313, lnlight Dosimeter Analysis Radiation Air Gross Beta Weekly E-111, Appendix 2 TBE-2008 Gross Alpha and/or Gross Beta Activity in Various Matrices.
Air 1-131 Weekly E-111, Appendix 2 TBE-2012 Radioiodine in Various Matrices Air Gamma Quarterly E-111, Appendix 2 TBE-2007 Gamma Emitting Radioisotope Analysis Drinking Water Gross Beta Monthly E-111, Appendix 5 TBE-2008 Gross Alpha and/or Gross Beta Activity in Various Matrices.
ttl I \\0 Surface &
Tritium Monthly (LTAW, 4S7, E-111, Appendix 3, 4, 5, 6, & 7 TBE-2010 Tritium and Carbon-14 Analysis by Liquid Drinking Water 5S12 and 7812 Scintillation.
Quarterly)
Surface &
Gamma Monthly (LTAW, 4S7, E-111, Appendix 3, 4, 5, 6, & 7 TBE-2007 Gamma Emitting Radioisotope Analysis.
Drinking Water 5S12 and 7S12 Quarterly)
Ground Water Tritium Quarterly E-111, Appendix 8 TBE-2010 Tritium and Carbon-14 Analysis by Liquid Scintillation Ground Water Gamma Quarterly E-111, Appendix 8 TBE-2007 Gamma Emitting Radioisotope Analysis I
tci I.......
0 TABLE B-2 (cont'd)
SUSQUEHANNA STEAM ELECTRIC STATION RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Sample Analysis Sampling Method Collection Procedure Number Analytical Procedure Number J
Medium I
Precipitation Tritium Monthly (Apr-Nov) I E-111, Appendix 10 TBE-2010 Tritium and Carbon-14 Analysis by Liquid Quarterly Scintillation Milk Gamma Monthly/BI-Weekly E-111, Appendix 9 TBE-2007 Gamma Emitting Radioisotope Analysis Milk 1-131 Monthly/Bi-Weekly E-111, Appendix 9 TBE-2012 Radioiodine In Various Matrices Fish Gamma Semi-Annually E-111, Appendix 11 TBE-2007 Gamma Emitting Radioisotope Analysis (Spring/Fall)
Sediment Gamma Semi-Annually E-111, Appendix 12 TBE-2007 Gamma Emitting Radioisotope Analysis (Spring/Fall)
Fruits &
Gamma In Season (When E-111, Appendix 13 TBE-2007 Gamma Emitting Radioisotope Analysis Vegetables available)
E-111, Appendix 15 Soil Gamma Annually E-111, Appendix 14 TBE-2007 Gamma Emitting Radioisotope Analysis
MAP B-1 Direct Radiation Monitoring Locations Within One B-11
MAP 8-2 Direct Radiation Monitoring Locations From One to Five Miles I
MlfflfVDla
)
i j
- i;
(..
I?
~-. J B-12
__1:,.-r* -*-\\.. / -~
- ***~
. 1 \\{
)
MAP B-3 Direct Radiation Monitoring Locations Greater Than Five Miles B-13
MAP B-4 Environmental Sampling Locations Within One Mile
\\ L r. ~
I \\
B-14
MAP B-5 Environmental Sampling Locations From One to Five Miles B-15
MAP 8-6 Environmental Sampling Locations Greater Than Five Miles B-16
APPENDIXC DATA TABLES C-1
Intentionally left blank C-2
TABLE C-1 GROSS BETA ANALYSES OF AIR PARTICULATE FILTERS SUSQUEHANNA STEAM ELECTRIC STATION Results in units of E-03 pCi/cu.m. +/- 2 sigma COLLECTION 382 6G1 8G1 12E1 12S1 13S6 PERIOD 01/02/14 - 01/08/14 14 +/- 3 12 +/- 2 11 +/- 2 16 +/- 3 15 +/- 3 11 +/- 2 01/08/14 - 01/15/14 14 +/- 2 10 +/- 2 11 +/- 2 14 +/- 2 16 +/- 2 12 +/- 2 01/15/14 - 01/22/14 21 +/- 3 14 +/- 2 15 +/- 2 17 +/- 2 18 +/- 2 17 +/- 3 01/22/14 - 01/29/14 13 +/- 2 10 +/- 2 13 +/- 2 12 +/- 2 11 +/- 2 15 +/- 2 01/29/14 - 02/04/14 15 +/- 3 16 +/- 3 14 +/- 3 18 +/- 3 14 +/- 3 15 +/- 3 02/04/14 - 02/12/14 18 +/- 2 17 +/- 2 18 +/- 2 22 +/- 3 21 +/- 3 19 +/- 2 02/12/14 - 02/19/14 15 +/- 2 17 +/- 2 15 +/- 2 17 +/- 3 15 +/- 3 17 +/- 3 02/19/14 - 02/26/14 10 +/- 2 11 +/- 2 12 +/- 3 12 +/- 2 13 +/- 2 12 +/- 2 02/26/14 - 03/05/14 20 +/- 3 23 +/- 3 21 +/- 3 26 +/- 3 19 +/- 3 23 +/- 3 03/05/14 - 03/12/14 17 +/- 3 16 +/- 3 16 +/- 3 15 +/- 3 15 +/- 3 14 +/- 3 03/12/14 - 03/19/14 12 +/- 2 13 +/- 2 11 +/- 2 13 +/- 2 12 +/- 2 10 +/- 2 03/19/14 - 03/26/14 9+/-2 13 +/- 2 12 +/- 2 11 +/- 2 10 +/- 2 11 +/- 2 03/26/14 - 04/02/14 11 +/- 2 10 +/- 2 9 +/- 2 9 +/- 2 10 +/- 2 9+/-2 04/02/14 - 04/09/14 12 +/- 2 9 +/- 2 11 +/- 2 10 +/- 2 11 +/- 2 11 +/- 2 04/09/14 - 04/16/14 13 +/- 2 12 +/- 2 10 +/- 2 13 +/- 2 15 +/- 2 12 +/- 2 04/16/14 - 04/23114 15 +/- 2 15 +/- 2 14 +/- 2 17 +/- 3 15 +/- 2 16 +/- 3 04/23/14 - 04/30/14 9+/-2 10 +/- 2 7 +/-2 10 +/- 2 8+/-2 9+/-2 04/30/14 - 05/07/14 6+/-2 8+/-2 8+/-2 8 +/- 2 7+/-2 7+/-2 05/07/14 - 05/14/14 16 +/- 2 13 +/- 2 13 +/- 2 15 +/- 2 13 +/- 2 13 +/- 2 05/14/14 - 05/21/14 12 +/- 2 11 +/- 2 12 +/- 2 14 +/- 2 11 +/- 2 12 +/- 2 05/21/14 - 05/28/14 10 +/- 2 11 +/- 2 10 +/- 2 13 +/- 2 9+/-2 10 +/- 2 05/28114 - 06/04/14 10 +/- 2 10 +/- 2 10 +/- 2 9 +/- 2 8+/-2 11 +/- 2 06/04114 - 06111/14 6+/-2 8 +/- 2 9+/-2 9 +/-2 8+/-2 8+/-2 06/11114 - 06118/14 9+/-2 9 +/- 2 9 +/- 2 11 +/- 2 8+/-2 8+/-2 06/18/14 - 06/25/14 11 +/- 2 10 +/- 2 10 +/- 2 11 +/- 2 10 +/- 2 13 +/- 2 06/25/14 - 07/02/14 14 +/- 2 12 +/- 2 12 +/- 2 14 +/- 2 10 +/- 2 12 +/- 2 07/02/14 - 07/09/14 13 +/- 2 11 +/- 2 15 +/- 2 14 +/- 2 14 +/- 2 13 +/- 2 07/09/14 - 07/16/14 11 +/- 2 12 +/- 2 11 +/- 2 13 +/- 2 12 +/- 2 15 +/- 2 07/16/14 - 07/23/14 14 +/- 2 13 +/- 2 12 +/- 2 13 +/- 2 11 +/- 2 12 +/- 2 07/23114 - 07/30/14 12 +/- 2 12 +/- 2 9 +/- 2 11 +/- 2 10 +/- 2 13 +/- 2 07/30/14 - 08/06114 16 +/- 2 14 +/- 2 15 +/- 2 16 +/- 2 13 +/- 2 17 +/- 2 08/06/14 - 08/13114 13 +/- 2 11 +/- 2 9 +/- 2 11 +/- 2 13 +/- 2 13 +/- 2 08/13/14 - 08/20/14 12 +/- 2 11 +/- 2 13 +/- 2 15 +/- 2 12 +/- 2 11 +/- 2 08/20/14 - 08/27/14 13 +/- 2 12 +/- 2 10 +/- 2 12 +/- 2 11 +/- 2 11 +/- 2 08/27/14 - 09/03114 13 +/- 2 13 +/- 2 14 +/- 2 12 +/- 2 13 +/- 2 11 +/- 2 09/03/14 - 09/10/14 15 +/- 2 12 +/- 2 11 +/- 2 17 +/- 2 17 +/- 2 15 +/- 2 09/10114 - 09/17/14 8+/-2 8+/-2 8 +/- 2 9 +/- 2 9+/-2 8+/-2 09/17114 - 09/24/14 15 +/- 2 15 +/- 2 14 +/- 2 16 +/- 2 15 +/- 2 15 +/- 2 09/24114 - 10101/14 17 +/- 3 17 +/- 2 18 +/- 2 18 +/- 3 17 +/- 2 19 +/- 3 10/01/14 - 10/08/14 13 +/- 2 11 +/- 2 13 +/- 2 15 +/- 2 14 +/- 2 12 +/- 2 10/08/14 - 10/15/14 13 +/- 2 14 +/- 2 14 +/- 2 14 +/- 2 14 +/- 2 14 +/- 2 10/15/14 - 10/22/14 8+/-2 10 +/- 2 10 +/- 2 11 +/- 2 12 +/- 2 8+/-2 10/22/14 - 10/29114 11 +/- 2 14 +/- 2 13 +/- 2 12 +/- 2 12 +/- 2 12 +/- 2 10/29/14 - 11/05/14 13 +/- 2 12 +/- 2 14 +/- 2 14 +/- 2 15 +/- 2 13 +/- 2 11/05/14 - 11/12/14 13 +/- 2 10 +/- 2 10 +/- 2 13 +/- 2 12 +/- 2 12 +/- 2 11/12/14 - 11/19/14 11 +/- 2 8+/-2 10 +/- 2 9+/-2 11 +/- 2 8+/-2 11/19/14 - 11/25/14 18 +/- 3 14 +/- 2 19 +/- 3 19 +/- 3 18 +/- 3 17 +/- 3 11/25/14 - 12/03/14 13 +/- 2 11 +/- 2 14 +/- 2 15 +/- 2 15 +/- 2 12 +/- 2 12/03/14 - 12/09/14 14 +/- 3 15 +/- 3 13 +/- 2 16 +/- 3 16 +/- 3 15 +/- 3 12/09/14 - 12/17/14 10 +/- 2 7+/-2 8 +/- 2 11 +/- 2 10 +/- 2 9+/-2 12/17/14 - 12123/14 8 +/- 2 7+/-2 8+/-2 10 +/- 2 9+/-2 7+/-2 12/23/14 - 12/30/14 9+/-2 13 +/- 2 13 +/- 2 10 +/- 2 9+/-2 10 +/- 2 C-3
TABLE C-2 GAMMA SPECTROSCOPIC ANALYSES OF COMPOSITED AIR PARTICULATE FILTEF SUSQUEHANNA STEAM ELECTRIC STATION Results in units of E-03 pCi/cu.m. +/- 2 sigma SITE COLLECTION Be-7 K-40 Cs-134 Cs-137 PERIOD 6G1 01/02/14 - 04/02/14 98 +/- 23
< 17
< 1
< 1 04/02/14 - 07/02/14 102 +/- 25
< 13
< 1
< 1 07/02/14 - 10/01/14 116 +/- 21
< 23
< 1
< 1 10/01/14 - 12/30/14 75 +/- 20
< 28
<2
<2 AVERAGE 98 +/- 34 8G1 01/02/14 - 04/02/14 113 +/- 26
< 25
<2
< 2 04/02/14 - 07/02/14 104 +/- 29
< 33
<2
<2 07/02/14 - 10/01/14 131 +/- 26
< 18
< 1
< 1 10/01114 - 12/30/14 81 +/- 17
<17
< 1
< 1 AVERAGE 107 +/- 41 382 01/02/14 - 04/02/14 84 +/- 19
< 20
< 1
< 1 04/02/14 - 07/02/14 120 +/- 24
< 21
< 1
< 1 07/02/14 - 10/01114 123 +/- 25
<5
< 1
< 1 10/01/14 - 12/30/14 73 +/- 19
< 16
< 1
< 1 AVERAGE 100 +/-51 12E1 01/02/14 - 04/02114 94 +/- 20
< 21
< 1
< 1 04/02/14 - 07/02/14 101 +/- 23
< 8
< 1
< 1 07/02/14 - 10/01/14 104 +/- 26
< 12
<2
< 1 10/01/14 - 12/30/14 68 +/- 22
< 21
< 1
< 1 AVERAGE 92 +/- 32 1281 01/02/14 - 04/02/14 87 +/- 28
< 36
<2
<2 04/02/14 - 07/02/14 107 +/- 21
< 15
< 1
< 1 07/02/14 - 10/01/14 90 +/- 19
< 16
< 1
< 1 10/01/14 - 12/30/14 52+/- 16
< 23
< 1
< 1 AVERAGE 84 +/- 47 1386 01/02/14 - 04/02/14 68 +/- 22
< 26
< 1
< 1 04/02/14 - 07/02/14 125 +/- 23
< 16
< 1
< *J 07/02/14 - 10/01/14 110 +/- 23
< 23
< 1
< 1 10/01/14 - 12/30/14 67 +/- 18
< 5
< 1
< 1 AVERAGE 93 +/-58 C-4
TABLE C-3 IODINE-131 ANALYSES OF AIR IODINE SAMPLES SUSQUEHANNA STEAM ELECTRIC STATION Results in units of E-03 pCi/cu.m. +/- 2 sigma COLLECTION 382 6G1 8G1 12E1 1281 1386 PERIOD 01/02/14 - 01/08/14
< 17
< 16
< 17
< 17
< 16
< 17 01/08/14 - 01/15/14
< 10
<8
<8
<7
<9
< 10 01/15/14 - 01/22/14
< 8
< 7
<7
<7
<8
< 8 01/22/14 - 01/29/14
<8
<"9
<9
<8
<8
<8 01/29/14 - 02/04/14
< 10
< 10
< 10
< 10
< 10
< 10 02/04/14 - 02/12/14
< 12
< 10
< 10
< 10
< 12
< 12 02/12/14 - 02/19/14
< 12
< 9
<8
< 10
< 12
< 12 02/19/14 - 02/26/14
< 9
< 10
< 10
<9
< 10
<9 02/26/14 - 03/05/14
< 10
< 9
<9
<9
< 10
<9 03/05/14 - 03/12/14
<9
< 9
<8
< 8
<9
< 9 03/12/14 - 03/19/14
< 19
< 18
< 17
< 18
< 20
< 19 03/19/14 - 03/26/14
< 19
< 18
< 18
< 17
< 19
< 19 03/26/14 - 04/02/14
< 10
< 9
<9
< 9
< 11
< 11 04/02/14 - 04/09/14
< 11
< 10
< 10
<9
< 10
< 11 04/09/14 - 04/16/14
<7
<8
<8
<7
<7
<7 04/16/14 - 04/23/14
< 12
< 9
<9
<8
< 11
< 12 04/23/14 - 04/30/14
<9
<9
<9
< 8
<8
<9 04/30/14 - 05/07/14
<8
<9
<9
<8
<8
<8 05/07/14 - 05/14/14
<8
< 9
<8
<9
<8
<8 05/14/14 - 05/21/14
<9
< 10
<9
< 10
< 10
< 10 05/21/14 - 05/28/14
< 16
< 15
< 19
< 20
< 17
< 17 05/28/14 - 06/04/14
<4
<8
<8
<8
<8
<7 06/04/14 - 06/11/14
< 15
< 17
< 17
< 17
< 16
< 16 06/11/14 - 06/18/14
< 10
< 10
< 10
< 10
< 9
<9 06/18/14 - 06/25/14
< 10
< 10
< 10
< 10
<9
< 9 06/25/14 - 07/02/14
<8
<8
< 9
<9
<8
< 8 07/02/14 - 07/09/14
<7
<7
<8
<8
<7
<7 07/09/14 - 07/16/14
< 13
< 12
< 13
< 13
< 13
< 13 07/16/14 - 07/23/14
<7
<8
<8
<9
<8
<8 07/23114 - 07/30/14
< 15
< 17
< 18
< 18
< 15
< 15 07/30/14 - 08106/14
<9
< 10
< 10
< 11
<9
<9 08/06114 - 08/13114
< 14
<9
<9
< 9
< 10
< 10 08/13/14 - 08/20/14
< 10
< 10
< 10
< 10
< 10
< 10 08/20/14 - 08/27/14
< 18
< 18
< 18
< 19
< 18
< 18 08/27/14 - 09/03/14
< 12
< 15
< 15
< 16
< 12
< 12 09/03114 - 09/10/14
< 16
< 13
< 13
< 14
< 16
< 16 09/10114 - 09/17/14
< 10
< 11
< 10
< 11
< 10
< 10 09/17/14 - 09/24/14
< 15
< 18
< 18
< 19
< 15
< 15 09/24/14 - 10/01/14
< 18
< 20
< 19
< 19
< 18
< 18 10/01114 - 10/08/14
< 10
< 10
< 10
< 11
< 10
< 10 10/08/14 - 10/15/14
< 11
< 11
< 11
< 12
< 11
< 11 10/15/14 - 10/22/14
< 19
< 19
< 19
< 20
< 19
< 19 10/22114 - 10/29/14
<9
<9
< 9
<9
< 9
<8 10/29114 - 11/05/14
< 19
< 19
< 19
< 19
< 19
< 19 11/05/14 - 11/12/14
<9
< 11
< 11
< 11
<9
< 9 11/12/14-11/19/14
< 17
< 14
< 14
< 14
<17
< 17 11/19/14 - 11/25/14
< 12
< 13
< 13
< 13
< 11
< 11 11/25/14 - 12/03/14
< 9
< 10
< 10
< 10
< 9
<9 12/03/14 - 12/09/14
< 12
< 12
< 12
< 12
< 12
< 12 12109/14 - 12/17/14
< 10
< 9
< 9
<9
<9
< 15 12117/14 - 12/23/14
<8
< 18
< 15
< 17
<8
<8 12/23/14 - 12130/14
< 16
< 18
< 16
< 16
< 16
< 17 C-5
(1 I 0\\
TABLEC-4 LOCATION ON SITE m-2S2 2S3 3S2 3S3 4S3 4S6 5S4 5S7 6S4 6S9 7S6 7S7 8S2 9S2 10S1 10S2 11S7 12S1 12S3 12S7 13S2 13S5 13S6 14S5 15S5 16S1 16S2 ENVIRONMENTAL OPTICALLY STIMULATED LUMINESCENCE DOSIMETRY RESULTS SUSQUEHANNA STEAM ELECTRIC STATION Results {1) are in mR/std. qtr {2) +/- 2 sigma {3)
First Quarter Second Quarter Third Quarter 01/30/14 to04/10/14 04/10/14 to 07/10/14 07/1 0/14 to 1 0/24/14 30.0 +/- 0.2 20.0 +/- 0.1 25.4 +/- 0.7 21.5 +/- 0.4 16.9 +/- 1.4 15.6 +/- 0.7 25.3 +/- 1.3 20.1 +/- 0.2 19.2 +/- 0.1 20.7 +/- 0.7 15.3 +/- 1.8 14.3 +/- 0.8 18.6 +/- 0.6 15.5 +/- 0.5 14.6 +/- 0.7 26.8 +/- 0.1 19.1 +/- 2.2 20.3 +/- 1.6 19.6 +/- 0.3 16.7 +/- 1.7 14.3 +/- 1.2 18.6 +/- 0.2 13.8 +/- 0.9 12.9 +/- 0.2 21.6 +/- 0.6 16.2 +/- 0.7 15.5 +/- 0.7 29.3 +/- 0.2 25.8 +/- 0.9 23.2 +/- 1.5 27.2 +/- 0.8 22.6 +/- 1.1 23.8 +/- 2.5 25.6 +/- 0.1 22.1 +/- 0.0 19.5 +/- 1.2 19.5 +/- 0.3 16.5 +/- 0.0 12.8 +/- 0.1 27.8 +/- 0.2 23.0 +/- 0.7 24.6 +/- 1.2 42.5 +/- 0.6 39.4 +/- 1.0 39.0 +/- 0.9 20.6 +/- 0.4 14.8 +/- 0.8 14.8 +/- 0.3 35.5 +/- 0.6 32.2 +/- 1.3 33.2 +/- 2.2 20.8 +/- 0.8 14.8 +/- 0.1 14.9 +/- 0.2 21.4 +/- 0.1 17.0 +/- 0.2 17.3 +/- 0.1 24.8 +/- 0.6 20.8 +/- 1.1 20.4 +/- 0.1 19.7 +/- 0.2 15.6 +/- 1.1 14.5 +/- 0.5 29.3 +/- 1.7 26.0 +/- 2.9 24.1 +/- 3.4 30.9 +/- 0.2 27.9 +/- 0.2 28.0 +/- 0.1 25.8 +/- 0.2 23.9 +/- 0.6 20.4 +/- 1.2 25.2 +/- 0.2 20.1 +/- 2.1 21.7 +/- 0.8 22.4 +/- 0.5 17.9 +/- 0.4 17.1 +/- 0.2 27.7 +/- 0.1 20.4 +/- 0.8 22.3 +/- 0.1 27.4 +/- 0.3 20.4 +/- 0.2 21.5 +/- 0.1 See the comments at the end of this table.
Fourth Quarter 10/24/14 to 01/09/15 25.5 +/- 0.7 15.2 +/- 0.2 24.5 +/- 0.4 18.3 +/- 0.8 (4) 24.6 +/- 0.8 17.9 +/- 0.2 15.8 +/- 0.1 18.6 +/- 0.2 27.8 +/- 1.5 25.3 +/- 0.6 24.8 +/- 0.2 16.5 +/- 0.5 30.6 +/- 0.7 48.9 +/- 4.3 17.1+/-2.1 37.3 +/- 4.6 18.0 +/- 0.1 19.7 +/- 1.7 (4) 18.7 +/- 1.0 29.9 +/- 1.8 28.4 +/- 0.9 22.0 +/- 0.2 22.7 +/- 0.6 21.6 +/- 2.3 23.3 +/- 0.8 23.8 +/- 0.2
(')
I
-....)
TABLE C-4 LOCATION 0-1 MILE OFFSITE 6A4 8A3 15A3 16A2 1-2 MILES OFFSITE 8B2 9B1 1083 2-4 MILES OFFSITE 105 803 904 1001 1202 1401 4-5 MILES OFFSITE 3E1 4E2 5E2 6E1 7E1 11E1 12E1 13E4 ENVIRONMENTAL OPTICALLY STIMULATED LUMINESCENCE DOSIMETRY RESULTS SUSQUEHANNA STEAM ELECTRIC STATION Results (1) are in mR!std. qtr (2) +/- 2 sigma (3)
First Quarter Second Quarter Third Quarter 01/30/14 to04/10/14 04/10/14 to 07/10/14 07/10/14 to 1 0/24/14 22.4 +/- 0.3 18.7+/-0.1 16.7 +/- 1.2 19.2 +/- 0.9 14.7 +/- 0.0 13.4 +/- 0.5 18.5 +/- 0.0 15.6 +/- 0.3 13.3 +/- 1.5 17.8 +/- 0.6 14.1 +/- 0.6 13.3 +/- 0.0 20.5 +/- 0.2 15.3 +/- 0.8 13.8 +/- 1.1 24.1 +/- 0.1 20.7 +/- 0.2 19.5 +/- 0.5 20.3 +/- 0.6 15.0 +/- 1.3 12.5 +/- 0.4 23.7 +/- 0.2 18.5 +/- 0.9 18.7 +/- 0.4 22.5 +/- 0.3 16.4 +/- 1.0 15.6 +/- 0.3 22.4 +/- 0.5 19.5 +/- 0.1 19.3 +/- 2.7 21.8 +/- 0.7 18.2 +/- 0.0 15.6 +/- 1.5 21.0 +/- 0.2 17.2 +/- 1.8 14.5 +/- 1.4 21.1 +/- 0.2 17.6 +/- 0.1 15.7 +/- 0.2 19.6 +/- 0.3 14.5 +/- 0.8 13.2 +/- 1.3 22.4 +/- 0.2 18.6+/-1.1 18.1 +/- 1.6 23.5 +/- 0.7 17.9 +/- 1.3 16.6 +/- 1.5 24.1 +/-0.7 20.0 +/- 0.4 17.6 +/- 0.9 23.8 +/- 1.2 18.5 +/- 0.6 16.1 +/- 0.5 19.6 +/- 0.0 16.2 +/- 4.0 12.7 +/- 1.0 19.7 +/- 0.1 14.5 +/- 0.4 13.6 +/- 0.1 22.2 +/- 0.3 19.2 +/- 0.4 20.2 +/- 1.8 See the comments at the end of this table.
Fourth Quarter 10/24/14 to01/09/15 20.6 +/- 1.3 14.2 +/- 2.2 14.8 +/- 0.5 13.9+/-0.1 15.8 +/- 1.8 21.4 +/- 1.8 18.8 +/- 0.3 19.2 +/- 1.7 17.4 +/- 1.1 17.0 +/- 1.1 18.0 +/- 1.2 17.4 +/- 0.8 18.5 +/- 0.0 13.9 +/- 1.9 16.2 +/- 0.9 17.0 +/- 1.1 18.7 +/- 1.3 17.9 +/- 2.0 13.4 +/- 0.3 16.9 +/- 0.3 20.9 +/- 1.6
<1 I
TABLE C-4 LOCATION 5-10 MILES OFFSITE 2F1 15F1 16F1 10-20 MILES OFFSITE 3G4 4G1 7G1 12G1 12G4 ENVIRONMENTAL OPTICALLY STIMULATED LUMINESCENCE DOSIMETRY RESULTS SUSQUEHANNA STEAM ELECTRIC STATION Results (1) are in mR/std. qtr (2) +/- 2 sigma (3)
First Quarter 01/30/14 to 04/10/14 22.0 +/- 0.4 21.4 +/- 0.6 24.2 +/- 0.2 25.4 +/- 0.3 24.1 +/- 0.1 22.2 +/- 0.1 20.1 +/- 0.6 21.8 +/- 0.2 Second Quarter 04/10/14 to 07/10/14 17.5 +/- 0.3 18.7 +/- 0.7 18.2 +/- 1.2 17.1 +/- 0.7 20.3 +/- 0.6 (4) 14.2 +/- 1.1 16.3 +/- 1.0 Third-Quarter 07/10/14 to 10/24/14 17.2 +/- 0.6 17.2 +/- 0.8 18.5 +/- 0.4 17.9 +/- 0.8 19.1 +/- 2.3 17.0 +/- 0.2 13.6 +/- 1.1 15.7 +/- 0.1 See the comments at the end of this table.
oo LOCATION INDICATOR Average (5)
CONTROL Average (5)
COMMENTS 23.5 +/- 3.8 19.0 +/- 8.2 22.7 +/- 0.7 17.0 i 4.4 (1) Individual monitor location results are normally the average of the elemental doses of four elements from the two dosimeters assigned to each monitoring location.
(2) A standard (std.) quarter (qtr.) is considered to be 91.25 days. Results obtained for monitoring periods of other durations are nonnalized by multiplying them by 91.25/x, where x is the actual duration in days of the period.
(3) Uncertainties for individual monitoring location results are two standard deviations of the elemental doses of four elements from the two dosimeters assigned to each monitoring location, representing the variability between the elemental doses of each of the four dosimeter elements.
18.2 +/- 8.0 16.6 +/- 2.6 (4) No measurement could be made at this location because the dosimeters were lost, stolen, or damaged. Refer to Section Ill, Program Description.
of the Annual Radiological Environmental Operating Report for an explanation of program exceptions to REMP.
(5) Uncertainties associated with quarterly Indicator and control averages are two standard deviations, representing the variability between the results of the individual monitoring locations.
Fourth Quarter 10/24/14 to 01/09/15 17.4 +/- 1.7 20.6 +/- 0.9 19.3 +/- 0.8 18.9 +/- 1.1 19.6 +/- 1.6 17.1 +/- 0.7 14.3 +/- 1.8 15.9 +/- 0.3 20.7 +/- 11.3 17.2 +/- 2.7
TABLE C-5 SITE COLLECTION 10G1 13E3 PERIOD 01/06/14 02/04/14 03/10/14 04/07/14 04/21/14 05/05/14 05/19/14 06/02/14 06/16/14 06/30/14 07/15/14 07/28/14 08/11/14 08/25/14 09/08/14 09/22/14 10/07/14 10/20/14 11/10/14 12/08/14 AVERAGE 01/06/14 02/04/14 03/10/14 04/07/14 04/21/14 05/05/14 05/19114 06102/14 06116/14 06/30/14 07115/14 07/28/14 08/11114 08/25/14 09/08/14 09/22/14 10/07/14 10120/14 11/10/14 12/08/14 AVERAGE IODINE-131 AND GAMMA SPECTROSCOPIC ANALYSES OF MILK SUSQUEHANNA STEAM ELECTRIC STATION Results in pCi/Liter +/- 2 sigma 1-131 K-40 Cs-134 Cs-137 Ba-140 La-140 Th-228
< 0.7
< 0.4
< 0.7
< 0.4
< 0.4
< 0.4
< 0.6
< 0.4
< 0.4
< 0.4
< 0.5
< 0.5
< 0.2
< 0.5
< 0.8
< 0.5
< 0.3
< 0.7
< 0.4
< 0.4
< 1.0
< 0.5
< 0.7
< 0.4
< 0.4
< 0.4
< 0.7
< 0.4
< 0.4
< 0.4
< 0.5
< 0.5
< 0.2
< 0.6
< 0.7
< 0.5
< 0.4
< 0.9
< 0.4
< 0.2 1254 +/- 130 1168 +/- 179 1346 +/- 166 1350 +/- 122 1150 +/- 143 1222 +/- 172 1244 +/- 151 1267 +/- 147 1337 +/- 170 1357 +/- 126 1241 +/- 174 1212 +/- 166 1271 +/- 114 1219 +/- 116 1276 +/- 165 1307 +/- 161 1009 +/- 157 1298 +/- 102 1154 +/- 150 1401 +/- 145 1254 +/- 181 1341 +/- 126 1261 +/- 146 1395 +/- 116 1326 +/- 104 1309 +/- 147 1339 +/- 177 1273 +/- 145 1216 +/- 186 1171 +/- 159 1181 +/- 159 1176+/-150 1316 +/- 145 1357 +/- 116 1322 +/- 100 1576 +/- 169 1477 +/- 136 1347 +/- 144 1476 +/- 99 1446 +/- 171 1556 +/- 155 1343 +/- 235
<4
<6
<6
<4
<6
<9
<6
< 8
<7
<5
<6
<6
<4
<4
<7
<7
<6
<4
<6
<6
<5
<7
<5
<4
<5
<6
<6
<8
<6
<6
<5
<5
<4
<4
<6
<5
<5
<4
< 10
<6 C-9
<5
< 6
<7
<4
<7
< 10
<7
<8
< 8
< 5
< 6
<8
<5
<4
<7
<8
< 9
<5
< 7
<6
< 6
< 9
< 5
<4
< 6
<7
<7
<9
< 8
<6
<5
<6
<5
<4
<8
<5
<7
<4
< 11
<7
< 38
< 34
< 27
< 23
< 38
<55
< 30
< 44
< 39
< 21
< 26
< 39
< 23
< 27
< 38
<38
< 51
< 38
< 37
< 38
< 39
< 35
< 19
< 24
< 33
< 40
< 27
< 47
< 38
< 23
< 21
< 30
< 23
< 31
< 44
< 28
< 45
< 34
<53
< 38
< 12
< 13
<5
<6
< 12
<6
<8
<8
< 14
<6
< 11
<7
<7
< 10
<9
<9
< 15
< 11
<7
<9
< 14
< 13
<5
<6
< 10
< 11
<9
< 12
<9
<3
<6
<6
<5
<7
< 10
<6
< 14
< 9
< 13
<9
< 9
< 14
< 11
< 9
< 12
< 18
< 11
< 15
< 13
< 10
< 12
< 14
< 9
< 7
< 15
< 13
< 11
< 7
< 12
< 11
< 10
< 14
< 10
< 9
< 12
< 13
< 13
< 14
< 15
< 10
< 11
< 11
< 8
< 7
< 14
< 10
< 11
< 8
< 19
< 12
TABLE C-5 IODINE-131 AND GAMMA SPECTROSCOPIC ANALYSES OF MILK SUSQUEHANNA STEAM ELECTRIC STATION Results in pCi!Liter +/- 2 sigma SITE COLLECTION 1-131 K-40 Cs-134 Cs-137 Ba-140 La-140 Th-228 PERIOD 5E2 01/06/14
< 0.8 1412 +/- 114
< 5
< 5
< 40
< 11
< 10 02/04/14
< 0.5 1383 +/- 165
<6
< 6
< 33
< 11
< 13 03/10/14
< 0.7 1564 +/- 164
<6
<6
< 24
< 9
< 13 04/07/14
< 0.4 1295 +/- 77
<3
< 3
< 15
< 5
<5 04/21/14
< 0.5 1242 +/- 101
<4
< 4
< 24
<7
<7 05/05/14
< 0.4 1296 +/- 134
<5
< 5
< 25
< 5
< 10 05/19/14
< 0.5 1294 +/- 152
<7
< 8
< 34
< 10
< 13 06/02/14
< 0.3 1457 +/- 190
< 7
<9
< 44
< 13
< 15 06/16/14
< 0.4 1244 +/- 152
< 5
<6
< 34
< 6
< 12 06/30/14
< 0.4 1291 +/- 144
<6
<6
< 23
<7
< 11 07/15/14
< 0.4 1320 +/- 155
< 9
<9
< 41
< 9
< 17 07/28/14
< 0.5 1192 +/- 133
< 5
<4
< 20
< 6
<9 08/11/14
< 0.2 1464 +/- 94
< 3
<4
< 19
< 5
<7 08/25/14
< 0.6 1354 +/- 103
<4
<4
< 33
< 8
<7 09/08114
< 0.6 1399 +/- 128
< 5
<5
< 20
<8
<9 09/22/14
< 0.5 1219 +/- 155
<6
<7
< 32
< 11
< 13 10/07/14
< 0.4 1194 +/- 129
< 6
<7
< 49
< 14
< 12 10/20/14
< 0.8 1356 +/- 135
<5
<5
< 48
< 11
< 11 11/10/14
< 0.3 1278 +/- 143
<4
< 5
< 29
<9
< 9 12/08/14
< 0.2 1485 +/- 144
<6
< 6
< 28
<9
< 10 AVERAGE 1337 +/- 205 C-10
TABLE C-6 TRITIUM AND GAMMA SPECTROSCOPIC ANALYSES OF GROUND WATER SUSQUEHANNA STEAM ELECTRIC STATION Results in pCi/Liter +/- 2 sigma sitE c oLLEcTioN R-3 K-40 Mn-54 Co-58 Fe-59 c o-6o Zn-65 Nb-95 Zr-95 1-131 cs-134 Cs-137 Ba-140 La-140 Th-228 PERIOD 12F3 62163114
< 140
< 128
<6
< 6
< 18
< 6
<13
< 8
< 14
< 15
<6
< 7
< 35
< 11
<13 05/05/14
< 147
< 93
<8
< 6
< 14
<6
< 11
< 6
< 12
< 12
< 7
< 5
< 28
< 12
< 13 08/21/14
< 125
< 78
<5
< 3
< 11
<5
<9
< 5
<7
<7
<4
< 4
< 20
<5
<8 11/24/14
< 131
< 37
<5
<4
< 14
<5
< 10
<5
<8
< 10
<5
<4
< 24
<8
< 10 AVERAGE 2S2 02/03/14
< 139
< 86
< 4
< 5
< 13
< 5
< 10
<5
<9
< 13
<5
<6
< 29
< 8
< 10 05/05/14
< 147
<53
< 5
< 6
< 14
< 5
< 11
<6
< 10
< 13
<6
<6
< 32
<7
< 13 08/21/14
< 125
< 95
<6
< 6
< 18
<6
< 11
< 6
< 11
< 10
<5
<7
< 28
< 8
< 12 11/24/14
< 131
< 100
<6
< 5
< 18
<6
< 14
< 6
< 10
< 13
<6
<7
< 32
< 10
< 12 AVERAGE 2S8 05/21/14
< 146
< 43
<2
< 2
< 6
<2
< 4
< 2
<4
< 11
<2
<2
< 19
<6
<4 0
07/31/14
< 124 46 +/- 28
< 1
< 1
<4
< 1
<2
< 1
<2
< 10
< 1
< 1
< 15
<4
<3 I
11/10/14
< 140
< 94
<5
< 5
< 14
<6
< 11
<6
< 11
< 11
<5
<5
< 28
< 8
< 11 AVERAGE 46 +/- 0 4S4 02/03/14
< 136
< 102
<6
< 7
< 17
<4
< 13
< 7
< 11
< 15
<6
<6
< 35
< 13
< 12 05/05/14
< 147
< 120
<5
<5
< 12
<4
<7
< 5
<. 7
< 12
<4
< 5
< 21
< 5
< 9 08/21/14
< 125
< 91
<5
<4
< 10
<5
<8
< 5
< 8
< 8
<5
<5
< 21
< 5
< 10 11/24/14
< 129
< 55
<5
<7
< 12
<9
< 14
< 7
< 11
< 15
<5
<7
< 35
<9
< 14 AVERAGE 6S10 02/03/14
< 139
< 67
<5
<6
< 15
<5
<9
<6
< 11
< 12
<5
< 5
< 37
< 13
< 12 05/05/14
< 145
< 101
<6
<5
< 11
<6
< 11
< 5
< 9
< 11
<5
<6
< 29
< 11
< 11 08/21/14
< 127
< 107
<5
< 6
< 17
<5
< 10
<6
< 9
< 8
<5
<6
< 26
< 7
< 9 11/24/14
< 131
< 101
<4
<4
< 12
<4
< 10
< 6
< 10
< 11
<4
<6
< 25
< 7
< 11 AVERAGE 11S2 02/03/14
< 141
< 91
<5
<4
< 13
<5
<9
< 5
< 7
< 12
<4
<5
< 27
< 8
< 9 05/05/14
< 147
< 106
<9
<6
< 19
<7
< 14
< 9
< 14
< 15
<7
< 7
< 38
< 14
< 12 08/21/14
< 126
< 61
<6
<4
< 15
<5
< 12
<6
< 10
<9
<5
<5
< 28
< 9
< 13 11/24/14
< 131
< 65
<7
<7
< 17
<8
< 14
< 5
< 14
< 12
<7
< 6
< 38
< 13
< 13 AVERAGE
TABLE C-6 TRITIUM AND GAMMA SPECTROSCOPIC ANALYSES OF GROUND WATER SUSQUEHANNA STEAM ELECTRIC STATION Results in pCi/Liter +/- 2 sigma s iTE c oLLEcTION R-3 K-40 Mn-54 Co-58 Fe-59 co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 Th-228 PERIOD 13S7 02/23/14
< 147
< 34
<2
<2
< 6
<2
<4
<2
<4
<7
<2
<2
< 15
< 5
<4 05/20/14
< 143
< 14
<2
<2
< 6
<2
< 3
<2
< 4
< 11
<2
<2
< 19
< 5
<4 07/29/14
< 125
< 27
< 1
< 1
< 5
< 1
<2
< 1
<2
< 12
< 1
< 1
< 19
< 6
< 3 10/28/14
< 141
< 32
<2
<2
<7
<2
<4
< 2
< 4
< 11
<2
<2
< 19
< 6
<4 AVERAGE 1S3 02/23/14
< 146
< 32
<2
<2
< 5
< 1
<3
<2
< 3
<6
<2
< 2
< 13
<4
<3 05/20/14
< 145
< 10
< 1
< 1
<4
< 1
< 2
< 1
<2
<8
< 1
< 1
< 13
< 4
<2 07/29/14
< 125
< 13
< 1
<2
< 5
< 1
<3
<2
<3
< 14
< 1
< 1
< 21
< 6
<3 10/28/14
< 141
< 23
<2
< 3
< 8
<2
<6
<3
<5
< 13
<2
< 3
< 24
< 9
<4 AVERAGE 4S8 02/23/14 219 +/- 100
< 17
<2
<2
<5
<2
<4
<2
<4
<8
<2
< 2
< 16
<4
<4
(')
05/20/14 210 +/- 100
< 19
<2
<3
<7
<2
< 5
<3
< 5
< 14
<2
<2
< 24
<6
<5 I
07/29/14
< 124
< 30
< 1
<2
<5
< 1
< 3
<2
< 3
< 13
< 1
< 1
< 19
< 5
< 3 10/28/14 224 +/- 99
< 48
< 12
<2
<2
< 23
<8
<4 N *
<2
<3
<9
<2
< 5
< 3
< 5 AVERAGE 218 +/- 14 4S9 02/24/14
< 146
< 39
<2
<2
<6
<2
<4
<3
<4
< 8
<2
<2
< 17
<4
< 5 05/19/14
< 146
< 31
< 1
<2
< 5
<2
<3
<2
< 3
< 10
< 1
<2
< 17
< 5
< 3 08/18/14
< 126
< 16
<3
< 3
< 8
<3
<6
< 3
< 6
< 6
<3
< 3
< 13
< 5
< 6 10/30/14
< 142
< 17
< 2
<2
< 6
<2
<4
< 2
< 4
< 10
<2
< 2
< 18
<5 5+/-3 AVERAGE 5+/-0 6S11A 02/27/14
< 148
< 40
< 2
< 2
<5
<2
<4
< 2
<4
< 6
< 2
<2
< 13
<3
<4 06/02/14
< 147
< 66
<6
<7
< 19
<7
< 15
<7
< 10
< 14
<8
< 8
< 28
< 10
< 14 08/19/14
< 150
<57
<6
<6
< 15
<6
< 14
<7
< 12
<8
<6
< 7
< 26
< 7
< 13 11/03/14
< 145
< 75
<4
<4
< 10
<4
<7
<4
< 7
< 15
<4
<4
< 28
< 9
< 8 AVERAGE 6S12 02/21/14
< 147
< 21
< 1
< 1
<4
< 1
< 3
<2
< 2
<6
< 1
< 1
< 11
<4
< 3 05/12/14
< 148
< 11
< 1
< 1
<4
< 1
<3
< 2
< 3
< 14
< 1
< 1
< 19
<6
< 3 07/28/14
< 125
< 8
< 1
< 1
< 3
< 1
<2
< 1
<2
< 11
< 1
< 1
< 14
<4
<2 10/27/14
< 143
< 13
< 1
< 1
<4
< 1
< 3
< 2
<3
<8
< 1
< 1
< 14
< 4
<2 AVERAGE
TABLE C-6 TRITIUM AND GAMMA SPECTROSCOPIC ANALYSES OF GROUND WATER SUSQUEHANNA STEAM ELECTRIC STATION Results in pCi/Liter +/- 2 sigma SITE COLLECTION H-3 k-4o Mn-54 Co-58 Fe-59 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 Th-228 PERIOD 7S10 02/27/14
< 149
< 46
<2
<2
<6
<2
<4
<2
< 3
<6
<2
< 2
< 12
<4
<4 05/22/14
< 145
< 20
<2
<3
<8
<2
<5
< 3
< 5
< 11
<2
< 2
< 21
< 8
<4 08/01/14
< 123
< 30
< 1
< 1
<4
< 1
<2
< 1
< 2
< 10
< 1
< 1
< 15
<5
<2 11/08/14
< 143
< 39
<4
< 5
< 11
< 5
<8
< 6
< 7
< 12
<5
< 5
< 28
<7
< 10 AVERAGE 7511 02/25/14
< 146
< 34
<2
<2
< 5
<2
<4
<2
< 3
<6
<2
<2
< 13
<4
<4 06/02/14
< 145
< 143
<7
<6
< 19
<9
< 14
< 5
< 11
< 14
<6
<7
<34
< 14
< 14 08/18/14
< 126
< 79
<4
<4
< 9
<4
<7
<4
< 6
<7
<3
<4
< 20
< 6
<8 11/08/14
< 139
< 45
<5
<6
< 17
<4
< 10
< 7
< 11
< 15
<6
< 7
< 35
< 11
< 12 AVERAGE 8S4 02/23/14
< 144
< 15
<2
<2
<5
<2
<3
< 2
<3
< 6
<2
<2
< 13
<4
<3
(')
05/20/14
< 143 54+/- 28
<2
< 2
<7
<2
< 5
< 3
<4
< 13
<2
<2
< 22
< 7
<4 I
07/29/14
< 149
<8
< 1
< 1
< 3
< 1
< 2
< 1
< 2
<9
< 1
< 1
< 14
<4
<2 w
- 10/28/14 201 +/- 84
< 19
<2
< 3
<8
< 2
< 5
<3
< 5
< 14
<2
<2
< 24
< 8
<5 AVERAGE 201 +/- 0 54+/- 0
TABLE C-7 SITE Precip Sites 3S2, 12S1, 8G1 (offsite, controls)
Precip Sites 1 and 2 (onsite. East of Station Reactor Bldgs)
Precipitation Sites 3 and 4 (onsite, West of Station Reactor Bldgs)
Perimeter Drain manholes (below grade, 28')
1S3-MW-1 (431 4S8 - MW-2 (45')
4S9 - MW-3 (94')
8S4-MW-4 (111')
(')
I 7$10- MW-5 (36')
.j:>.
13S7 - MW-6 (16')
2S8 - MW-7 (85')
6S11A-MW-8A (14')
6S11 B - MW-88 (19')
6S12-MW-9 (28')
7811 - MW-10 (132')
12F3 - Groundwater Control LTAW-Surface Water
- Revised values to reflect full scope of precipitation data.
ANNUAL AVERAGE TRITIUM CONCENTRATION IN PRECIPITATION,PERIMETER DRAIN, MONITORING WELLS AND LAKE TOOK-A-WHILE (LTAW) SURFACE WATER DATA SUSQUEHANNA STEAM ELECTRIC STATION Results in pCi/Liter +/- 2 sigma 2008 2009 2010 2011 2012 2013 62*
49 40 38 82 63 370 230*
193 216 242 182 414 404*
350 233 169 151 344 304 325 236 185 198 248 150 252 131 164 197 292 154 190 173 137 202 127 54 150 64 80 135 172 66 105 68 81 109 171 69 96
-6 74 106 142 134 143 34 80 111 Not installed Not installed Not installed 22 54 72 177 82 165 58 15 72 2014 51 142 231 179 115 187 94 60 68 71 70 103 Dry well Dry well Dry well Dry well Dry well Dry well Dry well 30
-44 45 18 6
60 21 3
-27
-9 1
-1 23 29 26
-53
-2 5
-6 45
-26 179 104 110 132 132 145 27
TABLE C-8 GROSS BETA, TRITIUM AND GAMMA SPECTROSCOPIC ANALYSES OF DRINKING WATER SUSQUEHANNA STEAM ELECTRIC STATION Results in pCi/Liter +/- 2 sigma SAMPLING PERIOD
<-----GAMMA EMITTERS----->
STATION ID START STOP Gr-B H-3 K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 12H2 12/31/13 - 01/28/14
< 1.8
< 142
< 29
< 1
< 1
< 3
< 1
< 2
< 1
<2
< 11
< 1
< 1
< 16
<4 12H2 01/28/14 - 03/04/14
< 2.2
< 145
< 12
< 1
< 1
<4
< 1
< 3
< 2
<3
< 13
< 1
< 1
< 18
< 5 12H2 03/04/14 - 04/01/14
< 2.4
< 130
< 10
< 1
< 1
< 3
< 1
< 2
< 1
<2
< 10
< 1
< 1
< 15
< 5 12H2 04/01/14 - 04/29/14
< 1.9
< 129
< 17
<2
< 2
<6
< 2
<4
<2
< 4
< 12
< 2
< 2
< 19
< 6 12H2 04/29/14 - 06/03/14 2.2 +/- 1.3
< 139
< 31
< 2
<2
< 5
< 2
< 3
< 2
<3
< 13
< 1
< 2
< 19
< 6 12H2 06/03/14 - 07/01/14
< 2.0
< 126
< 31
< 2
< 2
< 6
<2
<3
< 2
< 3
< 14
< 2
< 2
< 21
< 7 12H2 07/01/14 - 07/29/14 2.3 +/- 1.5
< 143
< 12
< 1
< 1
<4
< 1
< 2
< 1
< 2
< 13
< 1
< 1
< 17
< 5 12H2 07/29/14 - 09/02/14
< 2.4
< 136
< 14
< 1
< 1
<2
< 1
< 1
< 1
< 1
<8
< 0
< 1
< 10
< 3
()
12H2 09/02/14 - 09/30/14 2.4 +/- 1.5
< 128
< 17
< 1
< 1
< 3
< 1
< 1
< 1
<2
< 10
< 1
< 1
< 14
<4 I -
12H2 09/30/14 - 10/27/14 3.3 +/- 1.5
< 149
< 16
<2
<2
< 6
~2
<4
< 3
<4
< 15
<2
< 2
< 22
<6 Vl 12H2 10/27/14 - 12/02/14
< 1.9
< 131
<6
< 1
< 1
<2
< 1
< 1
< 1
<2
< 8
< 1
< 1
< 13
< 3 12H2 12/02/14 - 12/29/14 2.0 +/- 1.3
< 133
< 21
<2
< 3
<6
< 3
<5
< 3
< 5
< 15
< 2
< 2
< 26
< 10 AVERAGE 2.4 +/- 1.0
TABLE C-9 GAMMA SPECTROSCOPIC ANALYSES OF FOOD PRODUCTS (F~UITS AND VEGETABLES)
SUSQUEHANNA STEAM ELECTRIC STATION Results in pCi/kg (wet) +/- 2 sigma SITE COLLECTION Be-7 K-40 1-131 Cs-134 Cs-137 Ac-228 Th-228 PERIOD 8G1 07/16/14
< 148 4363 +/- 470
<.25
< 14
< 16
< 68
< 25 07116/14
< 136 4535 +/- 352
< 27
< 14
< 15
< 63
< 28 07/16/14
< 137 5545 +/- 453
< 27
< 15
< 18
< 68
< 28 08/20/14
< 211 3653 +/- 521
< 33
< 25
< 22
< 109
< 40 08/20/14 326 +/- 200 5259 +/- 688
<54
< 28
< 34
< 121
<52 08/20/14 308 +/- 160 6193 +/- 604
< 30
< 18
< 20
< 74
< 26 09/21/14 234 +/- 104 6548 +/- 399
< 38
< 12
< 15
< 61
< 22 09/21/14
< 108 4097 +/- 292
< 32
< 11
< 13
< 43
< 24 09/21/14 211 +/- 127 5710 +/- 526
< 47
< 19
< 22
< 76
< 32 10/19/14 506 +/- 150 3397 +/- 374
< 35
< 13
< 14
< 74
< 29 10/19/14 532 +/- 228 4948 +/- 642
< 42
< 23
< 22
< 89
< 35 10/19/14 443 +/- 133 5087 +/- 422
< 31
< 13
< 15
< 64
< 30 AVERAGE 366 +/- 257 4945 +/- 1952 n
I 11S6
< 35 06/30/14
< 176 5544 +/- 556
< 35
< 19
< 19
<59 0\\
06/30/14
< 123 5966 +/- 484
< 32
< 18
< 19
< 66
< 35 06/30/14
< 213 7302 +/- 650
< 41
< 20
< 22
< 94
< 37 07/16/14 175 +/- 103 4541 +/- 257
< 23
< 15
< 15
<56
< 24 07/16/14 190 +/- 82 5972 +/- 298
< 18
< 11
< 12
< 47 63 +/- 18 07/16/14 195 +/- 96 6234 +/- 333
< 16
< 9
< 10
< 43
< 17 08/20/14
< 271 4299 +/- 655
< 47
< 30
< 24
< 109
<50 08/20/14
< 172 7160 +/- 625
< 32
< 21
< 24
< 103
< 43 08/20/14
< 206 6675 +/- 675
< 39
< 25
< 28
< 123
< 43 09/21/14
< 144 3837 +/- 341
<.35
< 12
< 16
<58
< 22 09/21/14
< 118 5739 +/- 355
< 34
< 12
< 15
<50
< 22 09/21/14
< 184 7795 +/- 501
< 51
< 16
< 18
< 62
< 35 10/19/14 476 +/- 183 4670 +/- 593
< 39
< 22
< 22
< 80
< 42 10/19/14 520 +/- 161 6422 +/- 533
< 39
< 17
< 18
< 82
< 38 10/19/14
< 234 8566 +/- 711
< 53
< 18
< 25
< 89
< 40 AVERAGE 311 +/- 343 5993 +/- 2916 63 +/- 0
TABLE C-9 GAMMA SPECTROSCOPIC ANALYSES OF FOOD PRODUCTS (FRUITS AND VEGETABLES)
SUSQUEHANNA STEAM ELECTRIC STATION Results in pCi/kg (wet) +/- 2 sigma SITE COLLECTION Be-7 K-40 1-131 Cs-134 Cs-137 Ac-228 Th-228 PERIOD 3S3 06/30/14
< 124 4439 +/- 371
< 28
< 12
< 13
<57
< 29 06/30/14
< 195 6289 +/- 589
< 33
< 17
< 21
< 74
< 36 06/30/14
< 230 7513 +/- 627
< 40
< 19
< 24
< 92
< 40 07/16/14 335 +/- 89 4633 +/- 232
< 15
< 9
<9
< 41
< 18 07/16/14
< 108 4877 +/- 323
< 19
.< 12
< 13
< 51
< 19 07/16/14 154 +/- 73 7059 +/- 323
< 17
<9
< 11
< 46
< 18 08/20/14 458 +/- 165 4640 +/- 480
< 34
< 21
< 24
< 67
< 39 08/20/14 580 +/- 365 5302 +/- 771
<58
< 34
< 41
< 143
< 73 08/20/14
< 234 5821 +/- 609
< 30
< 19
< 20
< 86
< 33 09/21/14 355 +/- 140 5243 +/- 460
< 35
< 16
< 17 96
+/- 58
< 27 09/21/14 430 +/- 134 7352 +/- 480
<34
< 13
< 15
<72
< 26 09/21/14 257 +/- 148 7940 +/- 507
< 43
< 16
< 16
< 63
< 30 09/21/14 433 +/- 161 5777 +/- 454
<52
< 19
< 17
< 73
< 36 10/19/14 642 +/- 178 5903 +/- 622
< 40
< 19
< 20
< 106
< 41
()
10/19/14 725 +/- 208 6164 +/- 603 I
< 46
< 22
< 21
< 100
< 45 10/19/14 402 +/- 211 7378 +/- 736
< 45
< 24
< 24
< 86
< 41
"-l*
AVERAGE 434 +/- 333 6121 +/- 2151 96
+/- 0
TABLE C-10 GAMMA SPECTROSCOPIC ANALYSES OF SOIL SUSQUEHANNA STEAM ELECTRIC STATION Results in pCi/kg (dry)+/- 2 sigma SITE COLLECTION K-40 Cs-134 Cs-137 Ra-226 Ac-228 Th-228 PERIOD 8G1 09/17/14 13790 +/- 2010
< 97
< 129
< 3272 767 +/- 427 1101 +/- 202 09/17/14 13930 +/- 1750
< 139
< 142
< 3063 1393 +/- 491 1565 +/- 271 09/17/14 7911 +/- 2497
< 104
< 179
< 2944
< 675
< 224 MEAN 11877 +/- 6871 1080 +/- 885 1333 +/- 656 12S1 09/17/14 13380 +/- 1866
< 95 176 +/- 90
< 1733 1128 +/- 351 977 +/- 171 09/17/14 12820 +/- 2134
< 96
< 147
< 2278 1022 +/- 425 1600 +/- 192 09/17/14 15520 +/- 1791
< 77
< 96 2456 +/- 1409 1151 +/- 410 1316 +/- 127 MEAN 13907 +/- 2850 176 +/- 0 2456 +/- 0 1100 +/- 138 1298 +/- 624 C-18
TABLE C-11 TRITIUM AND GAMMA SPECTROSCOPIC ANALYSES OF SURFACE WATER SUSQUEHANNA STEAM ELECTRIC STATION, 2014 Results in pCi/liter +/- 28 SITE COLLECTION H-3 K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 Th-228 PERIOD 6S6 01/03/14 - 01/28/14
< 143
< 10
< 1
< 1
<3
< 1
< 2
< 1
< 2
< 8
< 1
< 1
< 13
<4
<2 01/28/14 - 03/04/14
< 146
< 22
< 1
<2
<5
< 1
<3
<2
<3
< 12
< 1
< 1
< 18
<6
<3 03/04/14
- 04/01/14
< 130
< 40
< 2
<2
< 7
< 2
<5
<2
<5
< 15
<2
<2
< 23
< 7
<4 03/18/14
- 04/01/14
< 132
< 41
<2
<2
< 6
< 2
<4
<2
<4
< 9
<2
<2
< 18
< 5
< 4 04/01/14
- 04/29/14
< 130
< 30
<2
<2
< 6
<2
< 3
<2
< 3
< 12
<2
<2
< 19
< 7
<3 04/08/14
- 04/29/14
< 129 90 +/- 28
<2
<2
< 5
< 2
<4
< 2
<4
< 10
<2
<2
< 17
< 6
<4 04/29/14
- 06/03/14
< 149
< 7
< 1
< 1
< 2
< 1
< 1
< 1
< 2
<6
< 1
< 1
<9
< 3
< 2 05/06/14
- 06/03/14
< 144
< 18
<2
<2
< 6
<2
< 3
< 2
<4
< 10
< 1
<2
< 16
< 6
<3 06/03/14 - 07/01/14
< 123
< 34
<2
<2
< 7
<2
< 4
< 2
< 4
< 13
< 2
<2
< 23
<8
<4 06/10/14
- 07/01/14
< 129
< 32
< 2
<2
<6
<2
<4
< 2
<4
< 9
< 2
< 2
< 17
<7
<3 07/01/14
- 07/29/14
< 146
< 26
< 1
< 1
< 3
< 1
< 2
< 1
<2
< 10
< 1
< 1
< 15
< 5
<2 07/08/14 - 07/08/14
< 147
< 22
< 1
< 1
< 3
< 1
< 2
< 1
<2
< 15
< 1
< 1
< 19
< 5
<2 07/29/14 - 09/02/14
< 137
< 8
< 1
< 1
<3
< 1
< 2
< 1
<2
< 3
< 1
< 1
< 21
< 5
<2 09/02/14 - 09/30/14
< 128
< 48
<2
<2
<8
<2
< 5
<2
<4
< 12
<2
<2
< 23
<7
<3
()
09/30/14
- 10/14/14
< 148
< 18
< 1
< 1
< 2
< 1
< 1
< 1
< 1
<9
< 1
< 1
< 11
<3 4+/-3 I
11/04/14 - 12/02/14
< 139
< 20
< 1
< 1
< 2
< 1
< 1
< 1
< 2
< 5
< 1
< 1
<9
<3
<2 12/02/14 - 12/29/14
< 123
< 13
< 1
< 2
< 3
< 3
< 9
< 1
< 1
< 15
< 5
< 3
\\0
< 5
< 1
<2 AVERAGE 90 +/- 0 4+/-0 2S7 12/31/13 - 01/28/14 3040 +/- 289
< 12
< 1
<2
<4
< 1
< 3
<2
< 3
< 10
< 1
< 1
< 16
< 5
<3 01/28/14 - 03/04/14 1740 +/- 181
< 31
<2
<2
< 6
<* 2
< 3
<2
< 3
< 13
<2
<2
< 20
<6 5 +/- 3 03/04/14
- 03/11/14
< 135
< 28
< 1
< 1
< 3
< 1
< 2
< 1
<2
< 13
< 1
< 1
< 15
<4
<2 03/18/14 - 04/01/14 2900 +/- 272
< 15
< 2
<2
< 5
<2
< 3
<2
<3
< 6
<2
<2
< 12
<4
< 3 04/08/14 - 04/29/14 433 +/- 99
< 33
< 1
<2
<4
< 1
< 3
<2
< 3
< 8
< 1
<2
< 15
<4
< 3 05/06/14 - 06/03/14 11500 +/- 952
< 15
<2
<2
< 5
< 2
<4
<2
<4
< 13
<2
<2
< 21
<5
< 4 05/22/14 - 05/27/14 2860 +/- 268
< 58
<3
<3
<9
<4
< 7
<3
< 5
< 12
<3
< 3
< 24
<9
<6 06/10/14 - 07/01/14 491 +/- 99
< 45
<2
<2
<6
<2
< 3
<2
<4
< 10
<2
<2
< 18
<6
<3 07/07/14 - 07/29/14 1150 +/- 146
< 22
< 1
< 1
<3
< 1
< 2
< 1
< 2
< 8
< 1
< 1
< 12
< 4
<2 07/08/14 - 07/08/14 354 +/- 108
< 17
< 1
< 1
< 3
< 1
< 1
< 1
< 2
< 13
< 1
< 1
< 16
<4
< 1 07/29/14
- 09/02/14 2020 +/- 198
< 13
< 1.
< 1
<2
< 1
< 1
< 1
< 1
< 11
< 1
< 1
< 12
<4
< 1 09/02/14 - 09/30/14 2630 +/- 306
< 17
<2
<2
< 5
< 2
< 3
<2
< 3
< 11
< 1
<2
< 17
<6
<3 09/30/14 - 10/27/14 461 +/- 115
< 47
<2
<2
<6
<2
<4
<2
<4
< 14
<2
< 2
< 22
<6
<4 10/27/14
- 12/02/14 2600 +/- 247 44 +/- 26
< 1
< 1
< 3
< 1
< 2
< 1
< 2
< 11
< 1
< 1
< 15
<4
< 2 12/02/14 - 12/29/14 7880 +/- 662
< 13
< 1
<2
< 5
< 1
< 3
<2
< 3
< 10
< 1
<2
< 17
<5
<3 AVERAGE 2861 +/- 6286 44 +/- 0 5+/-0
TABLE C-11 TRITIUM AND GAMMA SPECTROSCOPIC ANALYSES OF SURFACE WATER SUSQUEHANNA STEAM ELECTRIC STATION, 2014 Results in pCi/liter +/- 2S SITE COLLECTION H-3 K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 Th-228 PERIOD 6S5 01/07/14 - 01/28/14
< 140
< 16
<2
<2
<6
<2
<4
< 2
< 3
< 10
< 2
< 2
< 17
< 5
< 3 02/04/14 - 03/04/14
< 147
< 31
<2
<2
<6
< 2
< 3
< 2
<4
< 11
<2
< 2
< 18
<6
<3 03/11/14 - 04/01/14
< 133
< 14
<2
<2
<5
<2
< 3
< 2
<3
< 8
<2
<2
< 15
<5
<4 04/08/14 - 04/29/14
< 130 42 +/- 27
<2
<2
<6
<2
< 4
<2
<4
< 11
< 2
<2
< 19
<6
<4 05/06/14 - 06/03/14
< 144
< 16
<2
<2
<6
<2
< 4
<2
<4
< 11
<2
<2
< 18
<6
<3 06/10/14 - 07/01/14
< 126
<34
<2
< 2
<5
<2
<4
<2
<4
< 11
< 2
<2
< 20
<7
<4 07/08/14 - 07/29/14
< 147
< 8
< 1
< 1
<3
< 1
<2
< 1
<2
< 8
< 1
< 1
< 12
<4
<2 08/05/14 - 09/02/14 193 +/- 95
< 18
< 1
< 1
<2
< 1
< 1
< 1
< 1
< 9
< 1
< 1
< 11
<3
<2 09/09/14 - 09/30/14
< 126
< 37
<2
<2
<6
< 2
< 3
<2
<3
< 9
< 2
<2
< 16
<6
<4 10/07/14 - 10/27/14
< 145
< 29
<2
<2
<6
< 2
<4
< 2
<4
< 9
< 2
<2
< 17
<6
< 3 11/04/14 - 12/02/14 168 +/- 86 42 +/- 25
< 1
< 1
<2
< 1
< 2
< 1
<2
< 7
< 1
< 1
< 10
<3
<2 12/09/14 - 12/29/14
< 145
< 32
<2
<2
< 6
<2
<4
<2
<4
< 8
<2
<"2
< 15
<5
< 3 AVERAGE 181 +/- 35 42 +/- 0 n
4S7 02/03/14 - 02/03/14
< 142
< 20
<2
<4
< 3
<4
< 9
< 2
<2
< 19
<6
< 4 I
< 3
< 7
<2 N
05/05/14 - 05/05/14 167 +/- 98
< 98
<6
< 9
<6
<9
< 13
<6
< 5
< 33
<8
< 10 0
< 5
< 17
< 5 08/21/14 - 08/21/14
< 125
< 135
<4
<6
< 14
< 5
< 13
< 5
< 8
< 10
< 6
< 8
< 31
<6
< 14 11/24/14 - 11/24/14
< 133
< 65
<6
< 6
< 17
< 6
< 11
<6
< 11
< 13
< 5
<6
< 31
< 10
< 13 AVERAGE 167 +/- 0 LTAW 02/03/14 - 02/03/14
< 142
< 27
< 1
< 1
<4
< 2
< 3
< 1
<2
< 4
< 1
< 1
<8
<3
<3 05/05/14 - 05/05/14
< 146
< 115
<6
< 6
< 17
<7
< 10
<7
< 10
< 12
< 6
<7
< 35
<9
< 12 08/21/14 - 08/21/14
< 131
< 47
<5
<5
< 19
<4
< 13
<5
< 11
< 11
< 6
<5
< 29
<5
< 12 11/24/14 - 11/24/14
< 130
< 66
<6
<7
< 18
<7
< 14
<8
< 14
< 14
<7
<7
< 39
< 12
< 12 AVERAGE 5S1 2 02/03/14 - 02/03/14
< 139
< 30
< 1
< 2
<4
< 1
<3
<2
< 3
< 6
< 1
< 2
< 12
<3
< 3 05/05/14 - 05/05/14
< 148
< 147
<4
<6
< 18
<7
< 12
<6
< 11
< 11
<6
<8
< 30
< 9
< 13 08/21/14 - 08/21/14
< 128
< 174
<7
<7
< 14
< 8
< 14
<7
< 10
< 12
< 5
<7
< 40
<9
< 13 11/24/14 - 11/24/14
< 132
< 95
<4
<7
< 14
< 6
<9
<6
< 10
< 11
<6
<7
< 26
<7
< 10 AVERAGE
TABLE C-11 TRITIUM AND GAMMA SPECTROSCOPIC ANALYSES OF SURFACE WATER SUSQUEHANNA STEAM ELECTRIC STATION, 2014 Results in pCi/liter +/- 28 SITE COLLECTION H-3 K-40 Mn-54 Co-58 Fe-59 Co-80 Zn-65 Nb-95 Zr-95 1-131 Cs-134 Cs-137 Ba-140 La-140 Th-228 PERIOD 5S9 10/21/14 - 10/21/14
< 147
< 24
<2
< 3
< 6
<2
< 5
< 3
< 5
< 8
< 3
<3
< 17
< 5
< 5 11/04/14 - 11/04/14
< 131
< 7
< 1
< 1
< 3
< 1
<2
< 1
< 2
< 6
< 1
< 1
< 19
<6
< 1 AVERAGE 7S12 02/03/14 - 02/03/14
< 142
< 16
<2
<2
<5
< 1
< 4
<2
< 3
<6
< 2
<2
< 13
<4
<3 05/05/14 - 05/05/14
< 147
< 100
<5
<5
< 14
<6
< 12
<4
< 10
< 12
< 5
<6
< 27
<8
< 11 08/21/14 - 08/21/14
< 131
< 148
<6
<6
< 18
< 5
< 15
<9
< 13
< 11
<6
<6
< 29
< 12
< 12 11/24/14 - 11/24/14
< 128
< 37
<4
<5
< 12
<4
< 10
<5
<8
< 11
< 5
< 5
< 28
<7
< 10 AVERAGE
()
I N
TABLE C-12 GAMMA SPECTROSCOPIC ANALYSIS OF FISH SUSQUEHANNA STEAM ELECTRIC STATION Results in pCi/kg (wet) +/- 2 sigma SITE COLLECTION K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 Cs-134 Cs-137 PERIOD 2H smallmouth bass 04/28/14 4880 +/- 1168
< 73
< 90
< 235
< 73
< 161
< 74
< 75 channel catfish 04/28/14 3521 +/- 935
<56
< 57
< 155
< 60
< 140
< 49
< 49 shorthead redhorse 04/28/14 3789 +/- 1042
< 100
< 104
< 253
< 81
< 179
< 97
< 92 smallmouth bass 10/01/14 3793 +/- 1022
< 63
< 85
< 241
< 61
< 151
< 67
< 62 channel catfish 10/01/14 2636 +/- 975
< 64
< 69
< 225
< 65
< 135
<56
<58 shorthead redhorse 10/01/14 4888 +/- 1302
<50
< 77
< 123
< 73
< 103
<58
< 46 shorthead redhorse 10/01/14 5083 +/- 1096
< 73
< 73
< 187
<72
< 139
< 59
< 67 AVERAGE 4084 :!: 1801 INO smallmouth bass 04/24/14 4359 +/- 1005
< 73
< 71
< 228
< 70
< 125
< 67
< 60 channel catfish 04/24/14 3897 +/- 950
<57
< 60
< 177
< 66
< 143
< 57
< 48
(')
shorthead redhorse 04/24/14 4671 +/- 1128
< 65
< 71
< 255
< 43
< 131
< 74
< 60 I
smallmouth bass 09/29/14 3914 +/- 1108
< 133
< 61
< 61 N
< 67
< 67
< 245
< 62 N
channel catfish 09/29/14 3103 +/- 1315
< 68
< 73
< 236
< 85
< 200
< 86
< 97 shorthead redhorse 09/29/14 6178 +/- 1449
< 65
< 67*
< 243
< 49
< 120
< 49
<56 shorthead redhorse 09/29/14 4070 +/- 1122
< 78
< 90
< 257
< 75
< 174
< 74
< 100 AVERAGE 4313 +/- 1909 LTAW largemouth bass 10/02/14 3287 +/- 1309
< 47
< 65
< 212
<56
< 104
< 40
< 49 AVERAGE 3287 +/- 0
TABLE C-13 GAMMA SPECTROSCOPIC ANALYSES OF SHORELINE SEDIMENT SUSQUEHANNA STEAM ELECTRIC STATION Results in pCi/kg (dry) +/- 2 sigma SITE COLLECTION K-40 Cs-134 Cs-137 Ra-226 Ac-228 Th-228 PERIOD 28 05/31/14 16860 +/- 1581
< 66
< 90 2524 +/- 1311 1423 +/- 328 1536 +/- 140 05/31/14 16790 +/- 1789
< 81
< 101
< 1785 1419 +/- 580 1858 +/- 249 10/27/14 13970 +/- 1241
< 62
<77 1915 +/- 1270 943 +/- 311 1221 +/- 108 AVERAGE 15873 +/- 3297 2220 +/- 861 1262 +/- 552 1538 +/- 637 78 05/31/14 10770 +/- 1216
<55
< 66
< 1283 1062 +/- 245 1122+/-143 10/27/14 14120 +/- 959
< 46
< 59 2378 +/- 1244 1223 +/- 242 1628 +/- 126 AVERAGE 12445 +/- 4738 2378 +/- 0 1143 +/- 228 1375 +/- 716 12F 05/31/14 13560 +/- 1403
< 60
< 77
< 1452 1215 +/- 337 1297 +/- 122 10/27/14 10620 +/- 979
< 39
< 43 1677 +/- 982 1021 +/- 220 1027 +/- 80 AVERAGE 12090 +/- 4158 1677 +/- 0 1118+/-274 1162 +/- 382 C-23
0 I
t-..) :
~
500 FIGURE C GROSS BETAACTIVITY (E-03 pCilm3) IN AIR PARTICULATES I PREOPERATIONAL I 450 -1 CHINESE OPERATIONAL WEAPONS TEST 400 -it A- 06/17/74 B- 09/26/76 c -11/17/76 350 -1.
D - 09/17177 E- 03/14178 300 I I
F -10/15/80 250 D
Unit I
~
C**iticality E
09/10/1982 200 J
150 -108 c
~
1\\ \\
CHERI'\\OBYL 4/26/86 100 -1U A *.q
~
Unit2 j F
Criticalil) 50 -11 'tY ' w
~ \\_
I \\ 11 OJOS/1984 0
I
~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
-- lndicato**
Control
~ * *-**- **-* *------------**
(J I
N v.
FIGURE C-2 -AMBIENT RADIATION LEVELS ooscnatc(mrcmtsTo~>ASED ON ENVIRONMENTAL DOSIMETRY DATA 50 45 I PREOPERATIONAL 40 35 30 25 20 15 lvr 10 '
Unit 1 Criticality 09/10/1982 I
\\
5 0
1973 1975 1977 1979 1981 Unil2 Criticality 05/08/1984 j
OPERATIONAL Changed from TLD to OSLD system
"'""" \\
1983 1985 1987 1989 1991 1993 1995 1997 1999 2001 2003 2005 2007 2009 2011 2013 2015
--Indicato1*
Control
(")
I N
0\\
FIGURE C IODINE-131 ACTIVITY IN MILK 100 pCi/Liter A
90 1P~OPERATIONAL OPERATIONAL CHINESE 80 1 B
I WEAPONS TEST A- 09/12177 B- 03/14178 70 1 B
I c-10/15/80 60 50 40 30 Unit!
'26/86 Criticality I
Unit2 1 O -
Criticality 20 J ft9 10/1982 05/08/1984 li~JJL.-.~-.~~~--Jl.-.-.-.-.-.-.-,-,-:-,-~--~,-~-r~-r~-o~-r~-o~-.~~
0 !
(\\~
~
~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ §
~ ~
~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~
121 Indicator ISIConh*oi
()
I FIGURE C ANNUAL AVERAGE TRITIUM ACTIVITY (pCill) IN PRECIPITATION, PERIMETER DRAIN, SURFACE WATER VERSUS GROUND WATER 1000 l 900 800 700 -'
600 500 t5 400 300 200 100 0 :**s:*
-100 ~--------------------------------------------------------------------~
~~~
. ~
- §-~
~~~
~
~~
~"~
~:-fl.'-
~fl.
.¢~ -!'~ -!'~ -1':0 -!'> #f> #" -!'~ #')>'~" -!'~ -!'~ -!'~
FIGURE C TRITIUM ACTIVITY IN SURFACE WATER pCi/Litcr 3500.--------------------------------------------------------------------------------.
PREOPERATIONAL OPERATIONAL 2500
()
1500 I tv*
\\0 500
~
-500+-.. -.-.-..-.-.-..
~--~----..
~~-.~----,~~--~.-.-..
-.-.-..-.-.-~--~
~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~
~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~
Indicator Control
APPENDIX D
SUMMARY
OF RESULTS FROM ANAL YTICS, ENVIRONMENTAL RESOURCE ASSOCIATES {ERA),
DEPARTMENT OF ENERGY (DOE)- MIXED ANAL YTE PERFORMANCE EVALUATION PROGRAM (MAPEP),
AND PPL REMP LABORATORY QUALITY CONTROL SPIKE PROGRAM D-1
Intentionally left blank D-2
TABLE D-1 ANALYTICS ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING, 2014 (PAGE1 OF 3)
Identification Reported Known Ratio (c)
Month/Year Number Matrix Nuclide Units Value (a)
Value (b)
TBE/Anal~ tics Evaluation (d)
March 2014 E10854 Milk Sr-89 pCi/L 95.1 91.7 1.04 A
Sr-90 pCi/L 10.9 15.1 0.72 w
E10855 Milk 1-131 pCi/L 96.6 98.5 0.98 A
Ce-141 pCi/L 112 119 0.94 A
Cr-51 pCi/L 449 491 0.91 A
9s-134 pCi/L 186 210 0.89 A
Cs-137 pCi/L 250 253 0.99 A
Co-58 pCi/L 248 268 0.93 A
Mn-54 pCi/L 292 297 0.98 A
Fe-59 pCi/L 230 219 1.05 A
Zn-65 pCi/L 312 323 0.97 A
Co-60 pCi/L 321 337 0.95 A
E10857 AP Ce-141 pCi 53.0 53.9 0.98 A
Cr-51 pCi 232 223 1.04 A
Cs-134 pCi 100 95.3 1.05 A
Cs-137 pCi 122 115 1.06 A
Co-58 pCi 122 121 1.01 A
Mn-54 pCi 135 135 1.00 A
Fe-59 pCi 111 99.3 1.12 A
Zn-65 pCi 140 147 0.95 A
Co-60 pCi 187 153 1.22 w
E10856 Charcoal 1-131 pCi 74.1 76.4 0.97 A
E10858 Water Fe-55 pCi/L 2090 1760 1.19 A
June 2014 E10913 Milk Sr-89 pCi/L 85.9 91.3 0.94 A
Sr-90 pCi/L 13.8 14.5 0.95 A
E10914 Milk 1-131 pCi!L 86.5 90.9 0.95 A
Ce-141 pCi/L 111 124 0.90 A
Cr-51 pCi/L 255 253 1.01 A
Cs-134 pCi/L 147 162 0.91 A
Cs-137 pCi/L 123 120 1.03 A
Co-58 pCi/L 105 112 0.94 A
Mn-54 pCi/L 155 156 0.99 A
Fe-59 pCi/L 106 102 1.04 A
Zn-65 pCi!L 251 252 1.00 A
Co-60 pCi/L 218 224 0.97 A
E10916 AP Ce-141 pCi 95.1 92.6 1.03 A
Cr-51 pCi 215 190 1.13 A
Cs-134 pCi 122 122 1.00 A
Cs-137 pCi 95.1 89.8 1.06 A
Co-58 pCi 88.7 84.1 1.05 A
Mn-54 pCi 115 116 0.99 A
Fe-59 pCi 72.6 76.7 0.95 A
Zn-65 pCi 193 189 1.02 A
Co-60 pCi 179 168 1.07 A
E10915 Charcoal 1-131 pCi 85.6 85.2 1.00 A
D-3
TABLE D-1 ANALYTICS ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING, 2014 (PAGE2 OF3)
Identification Reported Known Ratio (c)
Month/Year Number Matrix Nuclide Units Value(a)
Value (b)
TBE!Anal~ics Evaluation (d)
June 2014 E10917 Water Fe-55 pCi/L 1680 1810 0.93 A
September 2014 E10946 Milk Sr-89 pCi/L 90.7 96.9 0.94 A
Sr-90 pCi/L 14.0 16.4 0.85 A
E10947 Milk 1-131 pCi/L 92.0 97.6 0.94 A
Ce-141 pCi/L 117 126 0.93 A
Cr-51 pCi/L 281 288 0.98 A
Cs-134 pCi!L 141 158 0.89 A
Cs-137 pCi/L 186 193 0.96 A
Co-58 pCi/L 137 143 0.96 A
Mn-54 pCi/L 138 142 0.97 A
Fe-59 pCi/L 162 158 1.03 A
Zn-65 pCi/L 75.2 73.0 1.03 A
Co-60 pCi/L 286 297 0.96 A
E10949 AP Ce-141 pCi 97.8 82.1 1.19 A
Cr-51 pCi 212 188 1.13 A
Cs-134 pCi 106 103 1.03 A
Cs-137 pCi 131 126 1.04 A
Co-58 pCi 85.7 93.0 0.92 A
Mn-54 pCi 92.8 92.3 1.01 A
Fe-59 pCi 113 103 1.10 A
Zn-65 pCi 53.2 47.5 1.12 A
Co-60 pCi 202 193 1.05 A
E10948 Charcoal 1-131 pCi 83.9 89.8 0.93 A
E10950 Water Fe-55 pCi!L 2010 1720 1.17 A
E10951 Soil Ce-141 pCi/g 0.208 0.186 1.12 A
Cr-51 pCilg 0.398 0.425 0.94 A
Cs-134 pCi/g 0.216 0.233 0.93 A
Cs-137 pCi/g 0.398 0.365 1.09 A
Co-58 pCi/g 0.197 0.211 0.93 A
Mn-54 pCi/g 0.242 0.209 1.16 A
Fe-59 pCi/g 0.238 0.233 1.02 A
Zn-65 pCi/g 0.117 0.108 1.08 A
Co-60 pCi/g 0.447 0.438 1.02 A
December 2014 E11078 Milk Sr-89 pCi/L 85.7 95.7 0.90 A
Sr-90 pCi/L 12.9 15.6 0.83 A
E11079 Milk 1-131 pCi/L 85.9 95.1 0.90 A
Ce-141 pCi/L 205 219 0.94 A
Cr-51 pCi/L 402 406 0.99 A
Cs-134 pCi/L 156 164 0.95 A
Cs-137 pCi/L 194 198 0.98 A
Co-58 pCi/L 122 130 0.94 A
Mn-54 pCi/L 220 225 0.98 A
Fe-59 pCi/L 183 175 1.05 A
Zn-65 pCi/L 287 297 0.97 A
D-4
TABLE D-1 ANAL YTICS ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING, 2014 (PAGE3 OF 3}
Identification Reported Known Ratio (c)
Month/Year Number Matrix Nuclide Units Value (a)
Value (b)
TBE/Anal~tics December 2014 E11081 AP Ce-141 pCi 96.4 102 Cr-51 pCi 171 190 Cs-134 pCi 73.1 76.9 Cs-137 pCi 99.0 92.6 Co-58 pCi 57.5 60.8 Mn-54 pCi 107 105 Fe-59 pCi 74.2 81.6 Zn-65 pCi 144 139 Co-60 pCi 114 110 E11080 Charcoal 1-131 pCi 93.5 98.2 E11082 Water Fe-55 pCi/L 1760 1970 (a) Teledyne Brown Engineering reported result.
(b) The Analytics known value is equal to 100% of the parameter present In the standard as determined by gravimetric and/or volumetric measurements made during standard preparation.
(c) Ratio of Teledyne Brown Engineering to Analytics results.
(d) Analytics evaluation based on TBE internal QC limits: A= Acceptable, reported result falls within ratio limits of 0.80-1.20.
W-Acceptable with warning, reported result falls within 0. 70-0.80 or 1.20-1.30. N =Not Acceptable, reported result falls outside the ratio limits of< o. 70 and> 1.30.
D-5 0.95 0.90 0.95 1.07 0.95 1.02 0.91 1.04 1.04 0.95 0.89 Evaluation (d)
A A
A A
A A
A A
A A
A
TABLE D-2 ERA ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING, 2014 (PAGE 1 OF 1)
Identification Reported Known Acceptance Month/Year Number Media Nuclide Units Value (a)
Value (b)
Limits Evaluation (c)
May2014 RAD-97 Water Sr-89 pCi/L 38.25 36.7 27.5-43.6 Sr-90 pCi/L 24.65 26.5 19.2-30.9 8a-133 pCi/L 89.1 87.9 74.0-96.7 cs~134 pCi/L 45.55 44.3 35.5-48.7 Cs-137 pCi!L 9U5 89.1 80.2-101 Co-60 pCi!L 65.10 64.2 57.8-73.1 Zn-65 pCi!L 244 235 212-275 Gr-A pCi/L 45.65 61.0 31.9-75.8 Gr-8 pCi/L 27.95 33.0 21.4-40.7 1-131 pCi/L 23.75 25.7 21.3-30.3 U-Nat pCi/L 9.61 10.2 7.95-11.8 H-3 pCi/L 8435 8770 7610-9650 MRAD-20 Filter Gr-A pCi/filter 28.0 46.0 15.4-71.4 November 2014 RAD-99 Water Sr-89 pCi/L 30.4 31.4 22.8-38.1 Sr-90 pCi/L 18.6 21.8 15.6-25.7 Ba-133 pCi/L 46.8 49.1 40.3-54.5 Cs-134 pCi/L 88.0 89.8 73.7 - 98.8 Cs-137 pCi/L 99.0 98.8 88.9-111 Co-60 pCi/L 92.5 92.1 82.9-104 Zn-65 pCi/L 325 310 279-362 Gr-A pCi/L 29.9 37.6 19.4-48.1 Gr-8 pCi/L 27.5 27.4 17.3-35.3 1-131 pCi/L 15.8 20.3 16.8-24.4 U-N at pCi!L 5.74 5.80 4.34-6.96 H-3 pCi!L 6255 6880 5940-7570 MRAD-21 Filter Gr-A pCi/filter 27.3 36.9 12.4-57.3*
(1) The lodine-131 was evaluated as failed with a ratio of o. 778. No cause could be found for the slighly low activity. TBE would evaluate this as acceptable with warning. A rerun was not possible due to 1-131 decay. All previous ERA lodine-131 evaluations since 2004 have been acceptable. NCR 14-08 (a) Teledyne Brown Engineering reported result.
(b) The ERA known value is equal to 100% of the parameler present in tile standard as determined by gravimetric and/or volumetric measurements made during standard preparation.
(c) ERA evaluation: A=acceptable. Reported result falls within the Warning Limits. NA=not acceptable. Reported result falls outside of the Control Limits. CE=check for Error. Reported result falls within the Control Limits and outside of the Warning Limit.
D-6 A
A A
A A
A A
A A
A A
A A
A A
A A
A A
A A
A N {1)
A A
A
TABLE D-3 DOE'S MIXED ANAL YTE PERFORMANCE EVALUATION PROGRAM (MAPEP)
TELEDYNE BROWN ENGINEERING, 2014 (PAGE 1 OF 2)
Identification Reported Known Acceptance Month/Year Number Media Nuclide*
Units Value (a)
Value (b)
Range Evaluation (c)
March 2014 14-MaW30 Water Am-241 Bq/L 0.764 0.720 0.504 - 0.936 A
Cs-134 Bq/L 20.7 23.1 16.2-30 0 A
Cs-137 Bq/L 28.0 28.9 20.2-37.6 A
Co-57 Bq/L 26.5 27.5 19.3-35.8 A
Co-60 Bq/L 15.6 16.0 11.2-20.8 A
H-3*-
Bq/L NR 321 225-417 N(3)
Mn-54 Bq/L 13.5 13.9 9.7 - 18.1 A
Ni-63 Bq/L NR 34.0 23.8-44.2 N(3)
Pu-238 Bq/L 0.911 0.828 0.580 - 1.076 Pu-239/240 Bq/L 0.751 0.676 0.473- 0.879 K-40 Bq/L NR (1)
N (3)
Sr-90**
Bq/L NR 8.51 5.96-11.06 N(3)
U-234/233**
Bq/L NR 0.225 0.158 - 0.293 N(3)
U-238**
Bq/L NR 1.45 1.02-1.89 N (3)
Zn-65 Bq/L
-0.201 (1)
A 14-MaS30 Soil Cs-134 Bq/kg 2.02 (1)
A Cs-137 Bq/kg 1300 1238 867-1609 A
Co-57 Bq/kg 1069 966 676-1256 A
Co-60 Bq/kg 1.32 1.22 (2)
A Mn-54 Bq/kg 1510 1430 1001 -1859 A
K-40 Bqlkg 669 622 435-809 A
Sr-90 Bq/kg 4.14 (1)
A Zn-65 Bq/kg 763 695 487-904 A
14-RdF30 AP Cs-134**
Bq/sample NR 1.91 1.34-2.48 N(3)
Cs-137**
Bq/sample NR 1.76 1.23-2.29 N(3)
Co-57**
Bq/sample NR (1)
N(3)
Co-60**
Bq/sample NR 1.39 0.97-1.81 N{3)
Mn-54**
Bq/sample NR (1)
N(3)
Sr-90 Bq/sample 0.8220 1.18 0.83-1.53 N{3)
Zn-65**
Bq/sample NR (1)
N (3) 14-GrF30 AP Gr-A Bq/sample 0.606 1.77 0.53-3.01 A
Gr-B Bq/sample 0.7507 0.77 0.39-1.16 A
14-RdV30 Vegetation Cs-134 Bq/sample 5.96 6.04 4.23-7.85 A
Cs-137 Bq/sample 5.06 4.74 3.32 - 6.16 A
Co-57 Bq/sample 11.8 10.1 7.1 -13.1 A
Co-60 Bq/sample 7.34 6.93 4.85-9.01 A
Mn-54 Bq/sample 8.95 8.62 6.03-11.21 A
Sr-90 Bq/sample 1.23 1.46 1.02-1.90 A
Zn-65 Bq/sample 8.91 7.86 5.50-10.22 A
D-7
TABLE D-3 DOE'S MIXED ANALYTE PERFORMANCE EVALUATION PROGRAM (MAPEP)
TELEDYNE BROWN ENGINEERING, 2014 (PAGE2 OF2)
Identification Reported Known Acceptance Month/Year Number Media Nuclide*
Units Value (a)
Value (b)
Ran~e Evaluation (c)
September 2014 14-MaW31 Water Am-241 Bq/L 0.705 0.88 0.62-1.14 A
Cs-134***
Bq/L NR
{1)
N(4)
Cs-137***
Bq/L NR 18.4 12.9-23.9 N(4)
Co-57***
Bq/L NR 24.7 17.3-32.1 N(4)
Co-60***
Bq/L NR 12.4 8.7-16.1 N (4)
Mn-54***
Bq/L NR 14.0 9.8-18.2 N (4)
Ni-63 Bq/L 24.07 24.6 17.2-32.0 A
Pu-238 Bq/L 0.591 0.618 0.433 - 0.803 A
Pu-239/240 Bq/L 0.0153 0.0048 (2}
A K.40***
Bq/L NR 161 113-209.
N (4)
Zn-65***
Bq/L NR 10.9 7.6-14.2 N (4) 14-MaS31 Soil Cs-134***
Bq/kg NR 622 435-809 N (4)
Cs-137***
Bq/kg NR (1)
N (4)
Co-57***
Bqlkg NR 1116 781 -1451 N (4)
Co-60***
Bqlkg NR 779 545-1013 N (4)
Mn-54***
Bq/kg NR 1009 706-1312 N (4)
K-40***
Bqlkg NR 824 577-1071 N(4)
Sr-90 Bq/kg 694 858 601 -1115 A
Zn-65***
Bqlkg NR 541 379-703 N (4) 14-RdF31 AP Sr-90 Bq/sample 0.310 0.703 0.492-0.914 N(4) 14-GrF31 AP Gr-A Bq/sample 0.153 0.53 0.16-0.90 N(4)
Gr-B Bq/sample 0.977 1.06 0.53-1.59 A
September 2014 14-RdV31 Vegetation Cs-134 Bq/sample 7.31 7.38 5.17-9.59 A
Cs-137 Bq/sample 8.93 8.14 5.70-10.58 A
Go-57 Bq/sample 10.8 9.2 6.4-12.0 A
Co-60 Bq/sample 6.31 6.11 4.28-7.94 A
Mn-54 Bq/sample 7.76 7.10 4.97-9.23 A
Sr-90 Bq/sample 0.738 0.85 0.60- 1.11 A
Zn-65 Bq/sample 7.16 6.42 4.49-8.35 A
- The MAPEP cross check isotope list has been reduced due to duplication of effort or analysis not being performed for clients.
- Starting 2014, these nuclides will no longer be part of the TBE cross check program due to duplication of effort or analysis not being performed for clients. MAPEP evaluates non-reported analyses as failed if they were repcrted in the previous series.
- All future gamma cross check samples for these isotopes will be provided by Analytics.
(1) False positive test.
(2) Sensitivity evaluation.
(3) Water, Ni-63 overlooked when reporting, but the result of 32.7 +- 1.69 would have passed the acceptance criteria. NCR 14-04 Water, the non-detected K-40 was overlooked when reporting; but would have passed the false positive test. NCR 14-04 AP, Sr-90 rerun was within the low range of the acceptqance criteria. The original and rerun results were statistically the same. No cause could be identified for the slightly low Sr-90 activity. NCR 14-04 For non reported (NR) analyses. MAPEP evaluates 'as failed if they were reported in the previous series. NCR 14-04 (4) AP, Sr-90 gravimetric yield was very high at 117%. Could indicate larger than normal amounts of calcium in the AP. A second fuming HNO 3 separation would be required to remove the excess calcium. NCR 14-09 AP, Gr-Afpha was counted on tl1e wrong side. When flipped over and recounted the results were acceptable. NCR 14-09 For non reported (NR) analyses, MAPEP evaluates as failed if they were reported in the previous series. NCR 14-09 (a) Teledyne Brown Engineering reported result.
(b) The MAPEP known value is equal to 100% of the parameter present in the standard as determined by gravimetric and/or volumetric measurements made during standard preparation.
(c) DOEIMAPEP evaluation: A=acceptable. W=acceptable with warning, N=not acceptable.
D-8
TABLE D-4 PPL REMP LABORATORY SPIKE PROGRAM ANALYTICS ENVIRONMENTAL RADIOACTIVTY CROSS CHECK PROGRAM-2014 QUALITY CONTROL SPIKE PROGRAM TELEDYNE BROWN ENGINEERING ENVIRONMENTAL SERVICES (TBE)
(PAGE 1 OF 5)
Identification Analytics TBE TBE/Analytics MonthNear Number Matrix Nuclide Units Calculated Results (a)
Results (a)
Ratio September 2014 E11015 Soil Ce-141 pCi/kg 186 +/- 6 221 +/- 34 1.19 Cr-51 pCi/kg 425 +/- 14 587 +/- 170 1.38 (1)
Cs-134 pCi/kg 233 +/- 8 218 +/- 16 0.94 Cs-137 pCi/kg 365 +/- 12 382 +/- 21 1.05 Co-58 pCi/kg 211 +/- 7 214 +/- 18 1.01 Mn-54 pCi/kg 209 +/- 7 223 +/- 20 1.07 Fe-59 pCilkg 233 +/- 8 240 +/- 31 1.03 Zn-65 pCi/kg 108 +/- 4 109 +/- 33 1.01 Co-60 pCi/kg 438 +/- 15 481 +/- 17 1.1 0 March 2014 E10827 Milk 1-131 pCi/L 94.8 +/- 3 93 +/- 4 0.98 Ce-141 pCi/L 90.6 +/- 3 78 +/- 10 0.86 Cr-51 pCi/L 374 +/- 13 332 +/- 62 0.89 Cs-134 pCi/L 160 +/- 5 137 +/-58 0.86 Cs-137 pCi/L 193 +/- 6 181 +/- 9 0.94 Co-58 pCi/L 204 +/- 7 190 +/- 10 0.93 Mn-54 pCiiL 227 +/- 8 204 +/- 10 0.90 Fe-59 pCi/L 167 +/- 6 166 +/- 15 0.99 Zn-65 pCiiL 246 +/- 8 228 +/- 18 0.93 Co-60 pCi/L 257 +/- 9 233 +/- 7 0.91 June 2014 E10928 Milk 1-131 pCi/L 94.7 +/- 3 75.2 +/- 2 0.79 (1)
Ce-141 pCi/L 144 +/- 5 126 +/- 11 0.88 Cr-51 pCi/L 294 +/- 10 274 +/-52 0.93 Cs-134 pCi/L 188 +/- 6 158 +/- 7 0.84 Cs-137 pCi/L 139 +/- 5 142 +/- 8 1.02 Co-58 pCi/L 130 +/- 4 119 +/- 8 0.92 Mn-54 pCi/L 181 +/- 6 179 +/- 9 0.99 Fe-59 pCi/L 119 +/- 4 115 +/- 10 0.97 Zn-65 pCi/L 293 +/- 10 306 +/- 20 1.04 Co-60 pCi/L 260 +/- 9 242 +/- 7 0.93 September2014 E11010 Milk 1-131 pCi/L 97.1 +/- 3 85.6 +/- 3 0.88 Ce-141 pCi/L 220 +/- 7 217 +/- 13 0.99 Cr-51 pCi/L 504 +/- 17 509 +/- 90 1.01 Cs-134 pCi/L 275 +/- 9 252 +/- 10 0.92 Cs-137 pCi/L 337 +/- 11 335 +/- 15 0.99 Co-58 pCi/L 250 +/- 8 236 +/- 14 0.94 Mn-54 pCi/L 248 +/- 8 252 +/- 16 1.02 Fe-59 pCi/L 276 +/- 9 272 +/- 19 0.99 Zn-65 pCi/L 128 +/- 4 121 +/- 30 0.95 Co-60 pCi/L 519 +/- 17 514 +/- 13 0.99 (a) Counting error is two standard deviations.
(1) NCR 15-04 was inititiated to address the failure.
D-9
TABLE D-4 PPL REMP LABORATORY SPIKE PROGRAM ANALYTICS ENVIRONMENTAL RADIOACTIVTY CROSS CHECK PROGRAM -2014 QUALITY CONTROL SPIKE PROGRAM TELEDYNE BROWN ENGINEERING ENVIRONMENTAL SERVICES (TBE)
(PAGE 2 OF 5)
Identification Analytics TBE TBE/Analytics Month/Year Number Matrix Nuclide Units Calculated Results (a)
Results (a)
Ratio December 2014 E11099 Milk 1-131 pCi/L 94.9 +/- 3 81.2 +/- 3 0.86 Ce-141 pCi/L 216 +/- 7 192 +/- 9 0.89 Cr-51 pCi/L 399 +/- 13 385 +/- 48 0.96 Cs-134 pCi/L 162 +/- 5 141 +/- 5 0.87 Cs-137 pCi/L 195 +/- 6 179 +/- 9 0.92 Co-58 pCi/L 128 +/- 4 116 +/- 9 0.91 Mn-54 pCi/L 222 +/- 7 201 +/- 10 0.91 Fe-59 pCi/L 172 +/- 5 161 +/- 13 0.94 Zn-65 pCi/L 292 +/- 10 273 +/- 16 0.93 Co-60 pCi/L 231 +/- 8 212 +/- 7 0.92 March 2014 E10828 Ap Filter Ce-141 pCi/L 52.3 +/- 2 62 +/- 3 1.19 Cr-51 pCi/L 216 +/- 8 218 +/- 769 1.01 Cs-134 pCi/L 93 +/- 3 89 +/- 8 0.96 Cs-137 pCi!L 112 +/- 4 116 +/- 12 1.04 Co-58 pCi/L 118 +/- 4 116 +/- 14 0.98 Mn-54 pCi/L 131 +/- 5 134 +/- 15 1.02 Fe-59 pCi/L 97 +/- 3 94 +/- 18 0.97 Zn-65 pCi/L 142 +/- 5 135 +/- 26 0.95 Co-60 pCi/L 149 +/- 5 204 +/- 11 1.37 (1)
March 2014 E10829 Ap Filter Ce-141 pCi 55.1 +/- 2 63 +/- 15 1.14 Cr-51 pCi 228 +/- 8 232 +/- 79 1.02 Cs-134 pCi 98 +/- 3 100 +/- 8 1.02 Cs-137 pCi 117 +/- 4 122 +/- 13 1.04 Co-58 pCi 124 +/- 4 122 +/- 15 0.98 Mn-54 pCi 138 +/- 5 135 +/- 12 0.98 Fe~ 59 pCi 102 +/- 4 111 +/- 19 1.09 Zn-65 pCi 150 +/- 5 140 +/- 34 0.93 Co-60 pCi 157 +/- 5 215 +/- 11 1.37 (1)
March 2014 E10830 Ap Filter Ce-141 pCi 54.1 +/- 2 68 +/- 2 1.26 (1)
Cr-51 pCi 224 +/- 8 249 +/- 65 1.11 Cs-134 pCi 96 +/- 3 95 +/- 6 0.99 Cs-137 pCi 115 +/- 4 118 +/- 10 1.03 Co-58 pCi 122 +/- 4 118+/-11 0.97 Mn-54 pCi 135 +/- 5 136 +/- 10 1.01 Fe-59 pCi 100 +/- 3 95 +/- 16 0.95 Zn-65 pCi 147 +/- 5 130 +/- 20 0.88 Co-60 pCi 154 +/- 5 203 +/- 9 1.32 (1)
(a) Counting error is two standard deviations.
(1) NCR 15-04 was inititiated to address the failure.
D-10
TABLE D-4 PPL REMP LABORATORY SPIKE PROGRAM ANALYTICS ENVIRONMENTAL RADIOACTIVTY CROSS CHECK PROGRAM-2014 QUALITY CONTROL SPIKE PROGRAM TELEDYNE BROWN ENGINEERING ENVIRONMENTAL SERVICES (TBE)
(PAGE3 OF 5)
Identification Analytics TBE TBE/Analytics Month/Year Number Matrix Nuclide Units Calculated Results (a)
Results (a)
Ratio June 2014 E10929 Ap Filter Ce-141 pCi 88.4 +/- 3 99.7 +/- 11 1.13 Cr-51 pCi 181 +/- 6 184 +/-59 1.02 Cs-134 pCi 116 +/- 4 121 +/- 7 1.04 Cs-137 pCi 86 +/- 3 90 +/- 11 1.05 Co-58 pCi 80 +/- 3 86 +/- 12 1.08 Mn-54 pCi 111 +/- 4 118 +/- 13 1.06 Fe-59 pCi 73 +/- 3 67 +/- 13 0.92 Zn-65 pCi 180 +/- 6 189 +/- 19 1.05 Co-60 pCi 160 +/- 6 185 +/- 9 1.16 June 2014 E10930 Ap Filter Ce-141 pCi 92.4 +/- 3 87 +/- 12 0.94 Cr-51 pCi 189 +/- 7 235 +/- 71 1.24 Cs-134 pCi 121 +/- 4 121 +/- 9 1.00 Cs-137 pCi 90 +/- 3 96 +/- 12 1.07 Co-58 pCi 84 +/- 3 81 +/- 11 0.96 Mn-54 pCi 116 +/- 4 119 +/- 14 1.03 Fe-59 pCi 76.5 +/- 3 80 +/- 16 1.05 Zn-65 pCi 189 +/- 7 185 +/- 22 0.98 Co-60 pCi 167 +/- 6 183 +/- 11 1.10 June 2014 E10931 Ap Filter Ce-141 pCi 88.6 +/- 3 87 +/- 11 0.98 Cr-51 pCi 182 +/- 6 180 +/- 61 0.99 Cs-134 pCi 116 +/- 4 116 +/- 8 1.00 Cs-137 pCi 85.9 +/- 3 83 +/- 14 0.97 Co-58 pCi 80.5 +/- 3 75 +/- 12 0.93 Mn-54 pCi 111 +/- 4 117 +/- 13 1.05 Fe-59 pCi 73.4 +/- 3 77 +/- 18 1.05 Zn-65 pCi 181 +/- 6 181 +/- 21 1.00 Co-60 pCi 161 +/- 6 174 +/- 10 1.08 December 2014 E11100 Ap Filter Ce-141 pCi 102 +/- 4 106 +/- 11 1.04 Cr-51 pCi 189 +/- 7 213 +/-57 1.13 Cs-134 pCi 77 +/- 3 83 +/- 6 1.08 Cs-137 pCi 92 +/- 3 91 +/- 9 0.99 Co-58 pCi 61 +/- 2 65 +/- 9 1.07 Mn-54 pCi 105 +/- 4 103 +/- 10 0.98 Fe-59 pCi 82 +/- 3 89 +/- 15 1.09 Zn-65 pCi 138 +/- 5 133 +/- 21 0.96 Co-60 pCi 110 +/- 4 118 +/- 8 1.07 (a) Counting error is two standard deviations.
D-11
TABLE D-4 PPL REMP LABORATORY SPIKE PROGRAM ANALYTICS ENVIRONMENTAL RADIOACTIVTY CROSS CHECK PROGRAM - 2014 QUALITY CONTROL SPIKE PROGRAM TELEDYNE BROWN ENGINEERING ENVIRONMENTAL SERVICES (TBE)
(PAGE4 OF 5}
Identification Analytics TBE TBE/Analytics Month/Year Number Matrix Nuclide Units Calculated Results (a)
Results (a)
Ratio December 2014 E11101 Ap Filter Ce-141 pCi 105 +/- 4 125 +/- 12 1.19 Cr-51 pCi 194 +/- 7 201 +/- 66 1.04 Cs-134 pCi 79 +/- 3 89 +/- 6 1.13 Cs-137 pCi 95 +/- 3 107 +/- 10 1.13 Co-58 pCi 62 +/- 2 73 +/- 10 1.18 Mn-54 pCi 108 +/- 4 126 +/- 11 1.17 Fe-59 pCi 84 +/- 3 88 +/- 17 1.05 Zn-65 pCi 142 +/- 5 175 +/- 18 1.23 Co-60 pCi 113 +/- 4 132 +/- 9 1.17 December 2014 E11102 Ap Filter Ce-141 pCi 111 +/- 4 112 +/- 13 1.01 Cr-51 pCi 205 +/- 7 207 +/- 76 1.01 Cs-134 pCi 83 +/- 3 86 +/- 6 1.04 Cs-137 pCi 100 +/- 4 104 +/- 12 1.04 Co-58 pCi 66 +/- 2 61 +/- 11 0.92 Mn-54 pCi 114 +/- 4 118 +/- 11 1.04 Fe-59 pCi 88 +/- 3 78 +/- 17 0.89 Zn-65 pCi 150 +/- 5 164 +/- 19 1.09 Co-60 pCi 119 +/- 4 132 +/- 8 1.11 March 2014 E10834 Water H-3 pCi/L 4000 +/- 133 3990 +/- 351 1.00 June 2014 E10932 Water H-3 pCi/L 2160 +/- 72 2170 +/- 207 1.00 September 2014 E11014 Water H-3 pCi/L 2510 +/- 84 2280 +/- 221 0.91 December 2014 E11106 Water H-3 pCi/L 595 +/- 20 552 +/- 115 0.93 December 2014 E11106 Water H-3 pCi/L 595 +/- 20 497 +/- 119 0.84 March 2014 E10831 Charcoal 1-131 pCi 75.2 +/- 3 76.3 +/- 4 1.01 March 2014 E10832 Charcoal 1-131 pCi 75.6 +/- 3 77.3 +/- 7 1.02 March 2014 E10833 Charcoal 1-131 pCi 75.3 +/- 3 76.8 +/- 4 1.02 September 2014 E11011 Charcoal 1-131 pCi 89.8 +/- 3 92.7 +/- 5 1.03 September 2014 E11012 Charcoal 1-131 pCi 90.1 +/- 3 92.6 +/- 4 1.03 September 2014 E11013 Charcoal 1-131 pCi 89.8 +/- 3 85.8 +/- 6 0.96 (a) Counting error is two standard deviations.
D-12
TABLE D-4 PPL REMP LABORATORY SPIKE PROGRAM ANAL YTICS ENVIRONMENTAL RADIOACTIVTY CROSS CHECK PROGRAM - 2014 QUALITY CONTROL SPIKE PROGRAM TELEDYNE BROWN ENGINEERING ENVIRONMENTAL SERVICES (TBE)
(PAGES OF 5}
Identification Analytics TBE Month/Year Number Matrix Nuclide Units Calculated Results (a)
Results (a)
December 2014 E11103 Charcoal 1-131 pCi 98.2 +/- 3 96.8 +/- 4 December 2014 E11104 Charcoal 1-131 pCi 97.3 +/- 3 96.6 +/- 10 December 2014 E11105 Charcoal 1-131 pCi 98.2 +/- 3 100 +/- 6 (a) Counting error is two standard deviations.
D-13 TBE/Analytics Ratio 0.99 0.99 1.02
APPENDIXE REMP SAMPLE EQUIPMENT OPERABILITY TRENDING E-1
Intentionally left blank E-2
tr:1 I w TABLE E-1 REMP SAMPLE EQUIPMENT OPERABILITY TRENDING SUSQUEHANNA STEAM ELECTRIC STATION Per Cent(%) Operability SAMPLING MEDIA SAMPLE LOCATION DESCRIPTION 2010 Air Particulate & Charcoal 3S2 SSES Backup Met. Tower 99.9 12S1 West Building 99.9 13S6 Former Laydown Area, West of Confers Lane 100 12E1 Berwick Hospital 100 6G1 Freeland Substation 100 PPL System Facilities Center, Humboldt 8G1 Industrial Park 99.7 Drinking Water 12H2 Danville Water Company 100 Surface Water 2S7 Cooling Tower Slowdown Discharge Line 98.0 6S6 River Water Intake Line 100
- Auto-Composite sampler problems, March through June.
New Auto-Composite sampler installed in July.
2011 2012 2013 2014 99.3 98.9 99.9 100 100 99.9 99.9 100 99.7 99.1 99.9 100 100 99.9 100.0 100 100 99.9 99.9 100 100 99.8 99.9 100 100 100 100.0 100 99.1 98.1 98.1 69" 95.5 93.4 93.2 93