Text

Annual Radiological Environmental Operating Report
	ML14210A544
Person / Time
Site:	Salem, Hope Creek
Issue date:	04/29/2014
From:	Carr E, Wagner L; Public Service Enterprise Group
To:	; Document Control Desk, Office of Nuclear Reactor Regulation
References
	LR-N14-0079
	Download: ML14210A544 (113)
	v • d • e

PSEG Nuclear LLC P.O. Box 236, Hancocks Brdge, New Jersey 080.8-0236 0 PsE.

Nuclear LLC Technical Specification Section 6.9.1.7 (Salem)

Technical Specification Section 6.9.1.6 (Hope Creek)

APR 29 2014.

LR-N1 4-0079 United States Nuclear Regulatory Coihiission Attn: Document Control Desk Washington, DC 20555-0001 1

Hope Creek Generating Station Facility Operating License No. NPF-57 NRC Docket No. 50-354 Salem Nuclear Generating Station, Unit Nos. land 2 Facility Operating License Nos. DPR-70 and DPR-75 NRC Docket Nos. 50-272 and 50-311

Subject:

2013 Annual Radiological Environmental Operating Report As required by Section 6.9.1.7 of Appendix A to Facility Operating Licenses DPR-70 and DPR-75 for Salem Generating Station Unit Nos. 1 and 2, and Section 6.9.1.6 of Appendix A to the Operating License NPF-57 for Hope Creek Generating Station, PSEG Nuclear hereby transmits one copy of the combined 2013 Annual Radiological Environmental Operating Report. This report summarizes the results of the radiological environmental surveillance program for 2013 in the vicinity of the Salem and Hope Creek Generating Stations. The result of this program for 2013 was specifically compared to the result of the pre-operational program.

There are no regulatory commitments contained in this letter.

cU

/ lea

Document Control Desk L R-N14-0079 Page 2 of 3 If you have any questions or comments on this transmittal, please contact Ms. Alison Kraus at (856) 339-7900.

Sincerely, Eric S. Carr Plant Manager - Hope Creek Lawrence M. Wagner Plant Manager-Salem

Enclosure:

2013 Annual Radiological Environmental Operating Report

Document Control Desk LR-NI14-0079 Page 3 of 3 cc:

Mr. W. Dean, Administrator - Region I U. S. Nuclear Regulatory Commission 2100 Renaissance Blvd., Suite 100 King of Prussia, PA 19406-2713 Mr. J. Lamb, Project Manager U. S. Nuclear Regulatory Commission One White Flint North Mail Stop 8BIA Washington, DC 20555-0001 Mr. Ronald L. Nimitz, NRC Inspector - Region I U. S. Nuclear Regulatory Commission 2100 Renaissance Blvd., Suite 100 King of Prussia, PA 19406-2713 USNRC Senior Resident Inspector - Hope Creek (X24)

USNRC Senior Resident Inspector - Salem (X24)

Mr. P. Mulligan, Manager New Jersey Department of Environmental Protection P.O. Box 420 MC 33-01 33 Arctic Parkway Trenton, NJ 08625 Mr. D. Rose Delaware Emergency Management Agency 165 Brick Store Landing Road Smyrna, DE 19977 Hope Creek Commitment Coordinator (H02) w/o Enclosures Salem Commitment Coordinator (X25) wto Enclosures Corporate Commitment Coordinator (N21) w/o Enclosures

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM & HOPE CREEK GENERATING STATIONS 2013 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT JANUARY 1 TO DECEMBER 31,2013

TABLE OF CONTENTS I. S u m m a ry..........................................................................................................................

1 II. The Radiological Environm ental Monitoring Program...............................................

4 A. Objectives of the O perational REM P.............................................................

5 B. Im plem entation of the O bjectives....................................................................

5 Ill. Program Description..................................................................................................

7 A. Data Interpretation..........................................................................................

7 B. Program Exceptions......................................................................................

8 C. Program Changes..........................................................................................

9 D. Quality Assurance Program.........................................................................

10 E. Summary of Results: Inter-laboratory Comparison Program.......................

10 IV. Results and Discussion..........................................................................................

13 A. Atm ospheric..................................................................................................

14

1. Air Particulates...................................................................................

15

2. Air Iodine.............................................................................................

16 B. Direct Radiation............................................................................................

16 C. Terrestrial......................................................................................................

17

1. M ilk......................................................................................................

18

2. W ell W ater (G round W ater)................................................................

19

3. Potable W ater (Drinking W ater).........................................................

20

4. Vegetables..........................................................................................

22

5. Fodder Crops.....................................................................................

23

6. Soil......................................................................................................

24

7. Beef and Gam e..................................................................................

25 D. Aquatic.........................................................................................................

26

1. Surface W ater...................................................................................

27

2. Fish...................................................................................................

29

3. Blue Crab................................................

........................................ 30

4. Sedim ent.............................................................................................

30 E. Land Use Survey...............................................................................................

32 V. Annotations to Previous AREO R............................................................................

33 VI. Hope Creek Technical Specification Limit for Primary Water Iodine Concentrations.. 33 VII. Conclusions...........................................................................................................

33 VIII. References..........................................................................................................

34

- i-

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 Evalaution Program (MAPEP) Interlaboratory Comparison P ro g ra m s...................................................................................................

D -1

-ii-

LIST OF TABLES Table B-1 Sam pling Locations..............................................................................

B-4 Table B-2 Salem and Hope Creek Generating Stations' Radiological Environm ental M onitoring Program............................................................

B-8 LIST OF DATA TABLES Table C-1 Concentrations of Gamma Emitters in Quarterly Composites of Air P a rticulates, 20 13....................................................................................

C -3 Table C-2 Concentrations of Gross Beta Emitters in Air Particulates, 2013......

C-5 Table C-3 Concentrations of Iodine-1 31 in Filtered Air, 2013...................................

C-7 Table C-4 Direct Radiation Measurements - Quarterly Dosimetry Results, 2013.... C-9 Table C-5 Concentrations of Iodine-131 and Gamma Emitters in Milk, 2013........... C-10 Table C-6 Concentrations of Gross Alpha and Gross Beta Emitters and Tritium in Well W ate r, 2 0 13.............................................................................................

C -12 Table C-7 Concentrations of Gamma Emitters in Well Water, 2013......................... C-13 Table C-8 Concentrations of Gross Alpha and Gross Beta Emitters and Tritium in Raw and Treated Potable Water (2F3), 2013..................................................

C-14 Table C-9 Concentrations of Iodine-1 31 and Gamma Emitters in Raw and Treated Potable W ater (2F3), 2013...................................................................

C-15 Table C-10 Concentrations of Gamma Emitters in Vegetables, 2013........................ C-16 Table C-11 Concentrations of Gamma Emitters in Fodder Crops, 2013.................... C-18 Table C-12 Concentrations of Gamma Emitters in Soil, 2013................................

C-19

- iii -

Table C-13 Table C-14 Table C-15 Table C-16 Table C-17 Table C-18 Table C-19 LIST OF TABLES (cont'd)

Concentrations of Gamma Emitters in Beef and Game, 2013................. C-20 Concentrations of Gross Beta Emitters in Surface Water, 2013.............. C-21 Concentrations of Tritium in Surface W ater, 2013...................................

C-22 Concentrations of Gamma Emitters in Surface Water, 2013................... C-23 Concentrations of Gamma Emitters in Edible Fish, 2013.........................

C-26 Concentrations of Gamma Emitters in Crabs, 2013.................................

C-27 Concentrations of Gamma Emitters in Sediment, 2013...........................

C-28 LIST OF MAPS Map B-1 Salem and Hope Creek Generating Stations' Radiological Environmental Monitoring Program On-Site Sampling Locations............. B-13 Map B-2 Salem and Hope Creek Generating Stations' Radiological Environmental Monitoring Program Off-Site Sampling Locations............. B-14 LIST OF FIGURES Figure 1 Gross Beta Activity in Air Particulates 1990 through 20 13...................................................................................

C -29 Figure 2 Iodine-131 Activity in Milk 1990 thro ugh 20 13...................................................................................

C -30 Figure 3 Gross Beta Activity in Surface Water 1990 throug h 20 13...................................................................................

C -3 1

- iv -

Figure 4 Tritium Activity in Surface Water 1990 thro ugh 20 13...................................................................................

C -32 Figure 5 Cesium-1 37 and Co-60 Activity in Aquatic Sediment 1990 through 20 13...................................................................................

C -32 Figure 6 Cesium-1 37 Activity in Soil 1974 through 2013 (Triennial)...................... C-34

1.

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 Salem Generating Station (SGS) and Hope Creek Generating Station (HCGS). The results of the REMP are published annually, providing a summary and interpretation of the data collected.

Public Service Enterprise Group's (PSEG) Laboratory Testing Services (LTS).

was responsible for the collection of environmental samples during 2013.

Teledyne Brown Engineering (TBE) was responsible for the analysis of environmental samples during 2013. Duplicate samples for laboratory quality assurance (QA) were sent to GEL Laboratories. Mirion Technologies provided the dosimetry services for PSEG during 2013.

The REMP was conducted in accordance with the SGS's and HCGS's Technical Specifications (TS) and the respective station's Offsite Dose Calculation Manual (ODCM). The detection capabilities, required by the Technical Specifications and SGS's and HCGS's ODCM, were achieved for the 2013 reporting period. The REMP objectives were also met. Exceptions to the program are noted and the PSEG corrective action identifier in parenthesis. The data that was collected in 2013 assists in demonstrating that SGS and HCGS were operated in compliance with Technical Specifications and ODCMs.

Most of the radioactive materials noted in this report are present in the environment either naturally occurring, such as potassium (K) 40 or Beryllium (Be) 7, or from a non-nuclear generating station activity, such as nuclear weapons testing or medical wastes. Measurements made in the vicinity of SGS/HCGS were compared to background or control measurements and the preoperational REMP study performed before Salem Unit 1 became operational.

Samples of air particulates, air iodine, milk, surface, ground (well) and potable (drinking) water, vegetables, fodder crops, soil, fish, crabs and sediment were collected and analyzed. External radiation dose measurements were also made in the vicinity of SGS/HCGS using passive dosimeters.

To demonstrate compliance with Technical Specifications and SGS's and HCGS's ODCM (Sections 3/4.12.1 & 6.8.4.h ), samples were analyzed for one or more of the following: gamma emitting isotopes, tritium (H-3),

iodine-1 31 (1-131), gross alpha and gross beta. The results of these analyses were used to assess the environmental impact of SGS and HCGS operations, thereby demonstrating compliance with Technical Specifications and SGS's and HCGS's ODCM (Section 3/4.11), applicable Federal and State regulations and to verify the adequacy of radioactive effluent control systems.

The concentration of radioactive material in the environment that could be attributable to Salem and Hope Creek stations 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 for an estuarine environment and the operation of SGS and HCGS had no significant radiological impact on the environment.

The results provided in this report for the REMP are summarized below:

There were a total of 1623 analyses on 1288 environmental samples during 2013. Of the total number of analyses and environmental samples, direct radiation dose measurements were made using 218 sets of direct reading dosimeters.

In addition to the naturally - occurring isotopes (i.e. Be-7, K-40, Ra-Nat and Th-232), Cesium-1 37 was detected on the vegetables in two of the on-site gardens. These broadleaf vegetation samples had low concentrations of Cs-1 37 (up to 19 pCi/kg) which is similar to the 2012 results from the site gardens. There were no releases of gaseous cesium from either Salem or Hope Creek in 2012 or 2013. Cesium-137, from the atmospheric atomic bomb testing, is routinely found in sediment and soil samples. Soil samples taken from the gardens in January have Cs-137 that mirrored the range of the other environmental samples. The on-site gardens are encased in small boxes to prevent animals from foraging, and, since the samples are not rinsed, the data indicates that the soil contaminated the broadleaf vegetation.

The maximum bounding dose from the contamination would be 0.16 mrem assuming that an individual consumed 26 kg (57 pounds) of the vegetation.

Dose measurements are made with quarterly passive dosimeters at onsite and offsite locations around the SGS/HCGS. The direct radiation component was determined by comparing badges on the site boundary (5S1, 10S1, 11S1, 15Sland 15S2) to the designated controls (3G1 and 14G1). The range of the site boundary dosimeters, with an annual dose between 43 and 51 mRad were lower than the control locations of 57 and 61mRad. The direct radiation dose is determined by subtracting the control data from the badge data, therefore, there is no measurable direct radiation to a Member of the Public at the site boundary. The reason that the site badges are lower is that the surrounding waters lower the radon concentration and limit terrestrial radiation. This was comparable to the levels prior to station operation which had an average of 55 milliroentgen per year for 1973 to 1976.

Following the guidance in Nuclear Energy Institute's (NEI) 07-07, the results of the annual report of the Radiological Groundwater Protection Program (RGPP), formerly reported in this report, has been moved to the Annual Radiological Effluent Release Report.

The Radiological Environmental Monitoring Program Lower Alloways Creek Township, Salem County, New Jersey is the site of SGS and HCGS. Salem Generating Station consists of two operating pressurized water nuclear power reactors. Salem Unit One has a net rating of 1180 megawatt electric (MWe) and Salem Unit Two has a net rating of 1178 MWe. The licensed core power for both units is 3460 megawatt thermal (MWt). Hope Creek Generating Station is a boiling water nuclear power reactor, which has a net rating of 1216 MWe (3840 MWt).

The Generating Stations are located on a man-made peninsula on the east bank of the Delaware River. It was created by the deposition of hydraulic fill from dredging operations. The surrounding environment is characterized mainly by the Delaware River Estuary and Bay, extensive tidal marshlands, and low-lying meadowlands. These land types make up approximately 85%

of the land area within five miles of the site. Most of the remaining land is used for agriculture. More specific information on the demography, hydrology, meteorology, and land use of the area may be found in the Environmental Reports, Environmental Statements and the Updated Final Safety Analysis Reports.

Since 1968, a radiological environmental monitoring program (REMP) has been conducted. Starting in December 1972, a more extensive radiological monitoring program was initiated in preparation for the operation of Salem Unit 1. The operational REMP was initiated in December 1976 when Salem Unit 1 achieved criticality.

An overview of the 2013 REMP is provided in Table B-2, Salem and Hope Creek Generating Stations Radiological Environmental Monitoring Program.

Radioanalytical data from samples collected under this program 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, 2013, for the SGS/HCGS REMP.

A.

Objectives of the Operational REMP

1.

To fulfill the requirements of the Radiological Surveillance sections of the Technical Specifications and the SGS and HCGS ODCMs.

2.

To determine whether any significant increase occurred in the concentration of radionuclides in critical pathways.

3.

To verify the models used by SGS and HCGS that predict the radioactive inventory in the surrounding environment.

4.

To detect any change in ambient gamma radiation levels.

5.

To verify that SGS and HCGS operations do not have detrimental effects on the health and safety of the public or on the environment.

B.

Implementation of the Objectives

1.

Samples of various media were selected for monitoring due to the radiological dose impact to human 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, Delaware River Bay estuarine hydrology, local demography, and land uses.

2.

Sampling locations are divided into two classes, indicator and control. Indicator stations are those which are expected to manifest station effects. Control samples are collected at locations which are believed to be unaffected by station operations, usually at 15 to 30 kilometers (9.3 to 18.6 miles) away from the generating stations. Fluctuations in the levels of radionuclides and direct radiation at indicator stations are evaluated with respect to analogous fluctuations at control stations. Indicator and control station data are also evaluated relative to preoperational data.

3.

Appendix A, Program Summary, describes and summarizes the analytical results in accordance with Section 6.9.1.7 of the Salem Technical Specifications and Section 6.9.1.6 of the Hope Creek Technical Specifications.

4.

Appendix B, Sample Designation, describes the coding system which identifies sample type and location. Table B-1 On-site Sampling Locations lists the station codes, locations, latitude, longitude and the types of samples collected at each station.

5.

The sampling locations are indicated on Maps B-I, Onsite Sampling Locations and B-2, Offsite Sampling Locations.

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 below the LLD.

The grouped data were averaged and standard deviations calculated.

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 On 06/28/13, sample 11A1, taken at the Salem plant discharge, indicted positive tritium results of 374 pCi/L. There was a permitted release from Salem during the time of sampling. The results support the predicted concentration of tritium from the plant effluent permit.

(80106424)

When changing the 16E1 air sampler on 11/18/13, the sampler was not running. The sampler ran for approximately 51.5 hours5.787037e-5 days 0.00139 hours 8.267196e-6 weeks 1.9025e-6 months . The motor in the sampler was replaced with another motor. During 2014, PSEG plans to systematically replace all of the sampler motors that have not already been replaced. (80106424)

The air sampler at station 6S1 had a 109.8 hour9.259259e-5 days 0.00222 hours 1.322751e-5 weeks 3.044e-6 months outage (fuse blown and replaced) for the week of 07/08/13 to 07/15/13. This temporary air sampler was replaced in December 2013. (80106424)

Two (2) of the monthly surface water samples taken on 02/05/13 had positive iodine-131 (1-131) results. Station 1F2 had 1-131 levels of 1.46 pCi/L (1.46E-9 uCi/mL) and station 16F1 had 1-131 levels of 1.74 pCi/L (1.74E-9 uCi/mL). Both of these locations are 7 miles upstream of Salem and Hope Creek plants and approximately a mile and a half apart. Liquid permits for the sampling period were reviewed and indicated no 1-131 was released from either Salem or Hope Creek.

Since these sample locations are upstream of the nuclear complex and taken in the latter part of the ebb (outgoing) tide, the most likely source of the contamination is the result of a medical procedure, similar to the positive 1-131 sample taken at SA-SWA-1 2C1 in April 2011. (70151909)

During the week of 04/22/13 to 05/06/13, the fuse blew in the temporary air sampler installed at station 16S1. Due to the low air volume for sample SA-AIO-16S1 the vendor lab could not meet the LLD of 7 E-2 pCi/m3. A value of <8.34E-02 for 1-131 will be reported.

A new fuse was installed and the air sampler is working. Permanent air samplers were installed in December of 2013. (70154305)

Cesium-1 37 (Cs-1 37) was detected in two of the site garden December 2013 samples. Stations 15S1 and 1S1 had detectable concentrations of 12.9 and 19.2 pCi/L, respectively, of Cs-137. If the cesium was from the plant effluents, there would be other isotopes detected, notably cobalt-60 (Co-60), that are more prevalent in the effluent streams. Cesium-137, attributed to the atomic bomb testing, was detected in the garden soil samples earlier this year. Since the samples are not washed, it is likely that the contamination was from the soil, similar to Cs-137 found in 2012 in the site garden samples.

(70163130)

During the 4 th quarter, TLDs from station 7F2 and station 16S3 could not be located. They have been replaced and the location of the dosimeter moved slightly to prevent further loss. (80106424)

C.

Program Changes PSEG installed more passive dosimeters during 2013. Two of the new locations (12S and 13S1) were close to the site boundary, but became inaccessible during the summer months because of heavy vegetation. Consequently, they were relocated inside of the protected area.

In January 2013, two new air samplers at locations 6S1 and 16S1 were added to the program. Permanent air samplers for these two locations were installed in December 2013.

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 testing laboratory analyzed Performance Evaluation (PE) samples of air particulate, air iodine, milk, soil, vegetation and water matrices, as appropriate for 185 analyses. (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 For the TBE laboratory, 178 out of 185 analyses performed met the specified acceptance criteria. Seven analyses (Sr-89 and Sr-90 in milk, Co-57, Zn-65 and Sr-90 in soil, Cs-134 in air particulate and Sr-90 in vegetation [two low warning in a row]) did not meet the specified acceptance criteria or internal QA requirements for the following reason:

1.

Teledyne Brown Engineering's Analytics September 2013 Sr-89 in milk result of 63.9 pCi/L was lower than the known value of 96.0 pCi/L. The failure was a result of analyst error and was specific to the Analytics sample. Client samples for the associated time period were evaluated and no client samples were affected by this failure. Nonconformance Report (NCR) 13-15

2.

Teledyne Brown Engineering's Analytics September 2013 Sr-90 in milk result of 8.88 pCi/L was lower than the known value of 13.2 pCi/L. The failure was a result of analyst error and was specific to the Analytics sample. Client samples for the associated time period were evaluated and no client samples were affected by this failure. NCR 13-15

3. & 4. Teledyne Brown Engineering's MAPEP September 2013 Co-57 and Zn-65 in soil were evaluated as failing the false positive test. While MAPEP evaluated the results as failures, the gamma software listed the results as non identified nuclides.

The two nuclides would never have been reported as detected nuclides to a client. MAPEP does not allow laboratories to put in qualifiers for the submitted data nor "less than" results.

MAPEP evaluates results based on the relationship between the activity and the uncertainty. MAPEP spiked the soil sample with an extremely large concentration of Eu-1 52, which was identified by the gamma software as an interfering nuclide, resulting in forced' activity results that were evaluated by MAPEP as detected Co-57 and Zn-65. No client samples were affected by these failures. NCR 13-14

5.

Teledyne Brown Engineering's MAPEP September 2013 Sr-90 in soil result of 664 Bq/kg was higher than the known value of 460 Bq/kg, exceeding the upper control limit of 598 Bq/kg. An incorrect Sr-90 result was entered into the MAPEP database.

The correct Sr-90 activity of 322 Bq/kg would have been evaluated as acceptable with warning.

No client samples were affected by this failure. NCR 13-14

6.

Teledyne Brown Engineering's MAPEP September 2013 Cs-134 in air particulate activity of -0.570 Bq/sample was evaluated as a failed false positive test, based on MAPEP's evaluation of the result as a significant negative value at 3 standard deviations. A negative number would never have been reported as a detected nuclide to a client, therefore no client samples were affected by this failure. NCR 13-14

7.

Teledyne Brown Engineering's MAPEP September 2013 Sr-90 in vegetation result was investigated due to two low warnings in a row. It appears the September sample was double spike with carrier, resulting in a low activity. With a recovery of around 50% lower, the Sr-90 result would have fallen within the acceptance range. No client samples were affected by this issue. NCR 13-14 IV.

Results and Discussion The analytical results of the 2013 REMP samples are divided into categories based on exposure pathways: atmospheric, direct radiation, terrestrial, and aquatic. The analytical results for the 2013 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 pre-operational environmental monitoring program data (1973-1976) and to historical data during operations. The data collected demonstrates that the SGS's and HCGS's REMP was conducted in compliance with the Technical Specifications and SGS's and HCGS's ODCM.

The REMP for the SGS/HCGS Site has historically included samples and analyses not specifically required by the Station's Technical Specifications and SGS's and HCGS's ODCM. These analyses are referenced throughout the report as Management Audit samples. Laboratory Testing Services continues to collect these samples. The summary tables in this report include these additional samples and analyses.

These Management Audit Samples are samples that are taken to augment the radiological effluent monitoring program, but do not have a regulatory basis nor do they fulfill any regulatory requirement. The following is a list and quantity of the Management audit samples:

Food crops (12)

Milk samples (2)

Well water (1)

Potable water (2)

Fodder crops (4)

Soil (9)

Beef and game (2), dependent upon availability A.

Atmospheric Air particulates were collected on Schleicher-Schuell No. 25 glass fiber filters with low-volume air samplers.

Iodine was collected from the air by adsorption on triethylene-diamine (TEDA) impregnated charcoal cartridges connected in series after the air particulate filters. Air sample volumes were measured with calibrated dry-gas meters. The displayed volumes were corrected to standard temperature and pressure.

1.

Air Particulates Air particulate samples were collected weekly at seven indicator locations, one duplicate station and one control location. Each of the samples collected for the year were analyzed for gross beta. Quarterly composites of the weekly samples from each station were analyzed for specific gamma emitters.

Gross Beta Gross beta activity was detected in 355 of 356 of the indicator station samples collected at concentrations ranging from 5 to 30 E-3 pCi/m 3 with an average concentration of 13 E-3 pCi/m 3, and in 52 of 52 of the control station samples at concentrations ranging from 8 to 26 E-3 pCi/m 3 with an average of 15 E-3 pCi/m 3. The maximum preoperational level detected was 920 E-3 pCi/m 3 with an average concentration of 74 E-3 pCi/m 3.

(Table C-2, Appendix C) [Figure 1 - Results for gross beta analysis from 1990 to current year are plotted as quarterly averages, with an inset depicting the period 1973 to 2013].

Gamma Spectrometry Gamma spectroscopy was performed on each of the 32 quarterly composite samples.

Beryllium-7, attributed to cosmic ray activity in the atmosphere, was detected in all 28 indicator station composites at concentrations ranging from 66 E-3 to 159 E-3 pCi/m 3 with an average concentration of 103 E-3 pCi/m 3, and in the four control station composites ranging in concentration from 69 to 151 E-3 pCi/m 3 with an average concentration of 105 E-3 pCi/m 3. The maximum preoperational level detected was 330 E-3 pCi/m 3 with an average concentration of 109 E-3 pCi/m 3.

(Table C-I, Appendix C).

Naturally occurring Potassium-40 was detected in one of 28 indicator station composites at a concentration of 56 E-3 pCi/m 3.

All other gamma emitters were less than the LLD.

2.

Air Iodine Filtered air iodine samples were collected weekly at seven indicator locations, one duplicate location and one control location. Each of the samples collected for the year was analyzed for 1-131. Iodine-1 31 was not detected in any indicator station samples or control station samples. The maximum preoperational level detected was 42 E-3 pCi/m 3.

(Table C-3, Appendix C)

B.

Direct Radiation Ambient radiation levels in the environs were measured with a pair of thermoluminescent dosimeters supplied and processed by Mirion Technologies. Packets containing these passive dosimeters were placed in the owner-controlled area and around the Site at various distances and in each land based meteorological sector and analyzed quarterly. Emphasis was placed on special interest areas such as population centers, nearby residences, and schools.

A total of 58 locations were monitored for direct radiation during 2013, including 20 on-site locations, 33 off-site locations within the 10 mile zone and locations with two control locations beyond 10 miles.

Each location has two TLDs, with two calcium fluoride (CaF) thermoluminescent phosphors and two Lithium Fluoride phosphors in each TLD.

The average dose rate for the quarterly off-site dosimeters was 14.1 milliroentgen per standard quarter and the 5 quarterly on-site indicators dose rate was 11.9 milliroentgen per standard quarter. The average control dose rate was 14.8 milliroentgen per standard quarter.

The preoperational average for the quarterly TLD readings was 4.4 milliroentgen per standard month or 13.2 milliroentgen per standard quarter. The results of the direct radiation measurements for 2013 confirmed that the radiation levels in the vicinity of the Salem and Hope Creek Generating Stations were similar to previous years.

(Table C-4, Appendix C)

C.

Terrestrial Terrestrial REMP sampling includes the collection of milk, well water, potable water, vegetation, fodder crop and soil samples.

Milk samples were taken 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 November of each year.

Samples were collected in new polyethylene containers and transported in ice chests with no preservatives added to the milk.

One well water sample was collected monthly. Separate raw and treated potable water samples were composited daily at the City of Salem Water and Sewer Department. All samples were collected in new polyethylene containers.

Locally grown vegetables were collected at the time of harvest at 14 locations, fodder crops and broad leaf vegetation at 4 locations. The vegetables and fodder samples are additional samples (Management Audit) taken to enhance the radiological monitoring program. There is no dairy farm within three miles of SGS and HCGS and there is only one dairy within 5 miles. Therefore, broadleaf vegetation is grown, maintained and harvested by LTS personnel in the late summer and early fall. All samples were weighted, packaged and shipped to TBE for analysis.

1.

Milk Milk samples were collected at four local dairy farms (two farms in NJ and two in Delaware). Each sample was analyzed for 1-131 and gamma emitters.

Iodine-131 Iodine-1 31 was not detected above minimum detectable concentration in any of the 80 samples analyzed. The maximum preoperational level detected was 65 pCi/L, which occurred following a period of atmospheric nuclear weapons tests. (Table C-5, Appendix C) [Figure 3 - results from 1990 to 2013 are plotted as quarterly averages, with an inset graph depicting the period 1973 to 2013.]

Gamma Spectrometry Naturally occurring K-40 was detected in all 80 samples with concentrations for the 60 indicator station samples ranging from 1,162 to 1,564 pCi/L with an average concentration of 1,344 pCi/L, and the 20 control station sample concentrations ranging from 1,149 to 1,417 pCi/L, with an average concentration of 1,273 pCi/L. The maximum preoperational level detected was 2,000 pCi/L with an average concentration of 1,437 pCi/L.

(Table C-5, Appendix C)

All other gamma emitters were less than the LLD.

2.

Well Water (Ground Water)

Although wells in the vicinity of SGS/HCGS are not directly affected by plant operations, water samples were collected monthly from one farm's well (3E1). This well is located up gradient of the stations aquifer. Samples from this well are considered Management Audit samples.

Gross Alpha Gross alpha activity was not detected above the minimum detectable concentration in any of the well water samples. The maximum preoperational level detected was 9.6 pCi/L. (Table C-6, Appendix C)

Gross Beta Gross beta activity was detected in one of 13 well water samples at a concentration of 1.8 pCi/L. As with the 2012 gross beta results, the 2013 results are lower than the preoperational results which ranged from <2.1 to 38 pCi/L, with an average value of 9 pCi/L. The downward trend may be attributed to the REMP participant installing a water treatment system for this well in February, 2009. (Table C-6, Appendix C)

Tritium Tritium activity was not detected above the minimum detectable concentration in any of the well water samples. The maximum preoperational level detected was 380 pCi/L. (Table C-6, Appendix C)

Gamma Spectrometry Potassium-40 was not detected in any of the well water samples. The maximum preoperational level detected was 30 pCi/L.

Radium (Natural) was not detected in any of the well water samples. The maximum preoperational level detected was 2.0 pCi/L. (Table C-7, Appendix C)

All other gamma emitters were less than the LLD.

3.

Potable Water (Drinking Water)

Both raw and treated potable water samples were collected and composited by The City of Salem Water and Sewer Department personnel. Each sample consisted of daily aliquots composited into a monthly sample. The raw water source for this plant is Laurel Lake and its adjacent wells. These are Management Audit samples as no liquid effluents discharged from SGS/HCGS directly affect this pathway.

Gross Alpha No gross alpha activity was detected in any of the raw or treated water samples. The maximum preoperational level detected was 2.7 pCi/L. (Table C-8, Appendix C)

Gross Beta Gross beta activity was detected in 11 of the 12 raw water samples and 11 of the 12 treated water samples. The concentrations for the raw samples ranged from 3.4 to 7.3 pCi/L. Concentrations for the treated water ranged from 2.9 to 5.9 pCi/L. The average concentration for both raw and treated water was 4.7 pCi/L. The maximum preoperational level detected was 9.0 pCi/L with an average concentration of 4.2 pCi/L. (Table C-8, Appendix C)

Tritium Tritium activity was not detected in any of the raw or treated water samples. The maximum preoperational level detected was 350 pCi/L with an average of 179 pCi/L. (Table C-8, Appendix C)

Iodine-1 31 Iodine-131 measurements were performed to an LLD of 1.0 pCi/L. Iodine-1 31 activity was not detected in any of the raw or treated water samples. No preoperational data is available for comparison since 1-131 was not analyzed as a specific nuclide until 1989. Since that time all results have been below the LLD.

(Table C-9, Appendix C)

Gamma Spectrometry Naturally occurring K-40 was not detected in any of the raw or treated water samples. No preoperational data is available for comparison.

Naturally occurring Radium (Natural) was not detected in any raw or treated water samples. The maximum preoperational level detected was 1.4 pCi/L. (Table C-9, Appendix C)

All other gamma emitters were less than the LLD.

4.

Vegetables There are no farm products that are irrigated with water in which liquid plant effluents have been discharged.

A variety of food products are sampled from around the plant:

the variety is dependent on the farmer's preference. These vegetables are collected as Management Audit samples. In addition, broadleaf vegetation was grown by LTS personnel and planted at three onsite locations and one offsite location in Delaware at 3.9 miles SSW.

These broad leaf vegetable samples are collected since there are no milk farms operating within the 5 km radius of SGS/HCGS. The closest milk farm (13E3) is located in Odessa, DE at 4.9 miles (7.88 km). All samples (vegetable and broadleaf) were analyzed for gamma emitters and included asparagus, cabbage, sweet corn, peppers, tomatoes and soy beans. These samples were from eight indicator stations (20 samples) and three control stations (10 samples). The results for these samples are discussed below.

Gamma Spectrometry Naturally occurring Be-7, attributed to cosmic ray activity in the atmosphere, was detected in four of the 20 indicator station samples (cabbage), with concentrations ranging from 228 to 372 pCi/kg wet, with an average concentration of 279 pCi/kg wet. It was not detected in any of the control locations. No preoperational data is available for comparison.

Naturally occurring K-40 was detected in all 20 indicator samples, with concentrations ranging from 1,603 to 13,750 pCi/kg wet with an average concentration of 3,100 pCi/kg wet, and in all 10 control station samples at concentrations ranging from 1,269 to 2,433 pCi/kg wet with an average concentration of 1,963 pCi/kg wet. The maximum preoperational level detected was 4,800 pCi/kg wet with an average concentration of 2,140 pCi/kg wet. (Table C-10, Appendix C).

Cesium-1 37 was detected in two indicator samples (cabbage) with concentrations of 13 and 19 pCi/kg wet, with an average concentration of 16 pCi/kg wet, which is below the SGS's and HCGS's ODCM LLD value of 80 pCi/kg wet. The results of this sample are discussed in the beginning summary section.

All other gamma emitters were less than the LLD.

5.

Fodder Crops Although not required by the SGS or HCGS Technical Specifications and SGS's and HCGS's ODCM, four samples of silage normally used as cattle feed were collected from three indicator stations and one control station. It was determined that these products could be an element in the food-chain pathway. These fodder crops are collected as Management Audit samples and analyzed for gamma emitters. All four locations from which samples were collected are milk sampling stations.

Gamma Spectrometry Naturally occurring Be-7, attributed to cosmic ray activity in the atmosphere, was detected in all three indicator samples at concentrations ranging from 196 to 249 pCi/kg wet with an average concentration of 231 pCi/kg wet, and in the control station sample at 249 pCi/kg wet. The maximum preoperational level detected for silage was 4,700 pCi/kg wet with an average concentration of 2,000 pCi/kg wet.

Naturally occurring K-40 was detected in all three indicator samples at concentrations ranging from 2,968 to 4,052 pCi/kg wet with an average concentration of 3,554 pCi/kg wet, and in the control station sample at a concentration of 713 pCi/kg wet.

Preoperational results averaged 7,000 pCi/kg wet. (Table C-11, Appendix C)

All other gamma emitters were less than the LLD.

6.

Soil Soil is sampled every three years at nine stations, and analyzed for gamma emitters. These Management Audit samples were collected in areas that have been relatively undisturbed since the last collection in order to determine any change in the radionuclide inventory of the area. (Table C-12, Appendix C)

Gamma Spectrometry Naturally occurring K-40 was detected in all nine indicator samples at concentrations ranging from 5,038 to 18,510 pCi/kg dry with an average concentration of 10,980 pCi/kg dry. The maximum preoperational level detected was 24,000 pCi/kg dry with an average of 10,000 pCi/kg dry.

Cesium-1 37 was detected in six of the nine indicator samples at concentrations ranging from 45 to 227 pCi/kg dry with an average concentration of 130 pCi/kg dry. The maximum preoperational level detected was 2,800 pCi/kg dry with an average of 800 pCi/kg dry. [Figure 7 - Results for the Cs-137 analyses from 1973 to current year are plotted as the triennial average.] (Table C-12, Appendix C)

Naturally occurring Ra-226 was detected in five of the nine indicator samples at concentrations ranging from 1,324 to 2,595 pCi/kg dry with an average concentration of 2,100 pCi/kg dry. The maximum preoperational level detected was 1,500 pCi/kg dry with an average of 870 pCi/kg dry.

Naturally occurring Th-232 was detected in all of the nine indicator samples at concentrations ranging from 350 to 1,207 pCi/kg dry with an average concentration of 702 pCi/kg dry.

The maximum preoperational level detected was 1,400 pCi/kg dry with an average of 740 pCi/kg dry. (Table C-12, Appendix C)

7. Beef and Game Although not required by the SGS or HCGS Technical Specifications and SGS's and HCGS's ODCM, one muskrat sample was collected from one indicator station. The game sample was collected as a Management Audit sample and analyzed for gamma emitters.

Gamma Spectrometry Naturally occurring K-40 was detected in one of three indicator samples at a concentration of 3,307 pCi/kg wet. No preoperational data is available for comparison. (Table C-13, Appendix C)

All other gamma emitters were less than the LLD.

D.

Aquatic Environmental Consulting Services, Inc (ECSI) collected all aquatic samples (with the exception of the 6S2 shoreline sediment). This sample set includes edible fish, shoreline and riverbed sediment, surface water and crab.

Surface water samples were collected offshore. The technicians collect the samples in new polyethylene containers that were rinsed twice with the sample medium prior to collection. The surface water samples were transported to TBE for analysis.

Edible fish were taken by gill nets while crabs were caught in commercial traps. These samples were processed by separating the flesh from the bone and shell. The flesh was placed in sealed containers and frozen before being transported in ice chests to TBE for analysis.

Sediment samples collected by ECSI were taken with a bottom grab sampler and frozen in sealed polyethylene containers before being transported in ice chests to TBE. For the river bottom sediment, a marine GPS was used to locate the correct site and the sampling boat was maneuvered over the area until the correct amount of sample was obtained (grabbed) with the sediment dredge. Personnel from LTS collected and prepared the location 6S2 shoreline sediment sample (an onsite location).

For this location, a square area, measuring one meter on each side was staked out and then divided into a grid of nine smaller boxes, three per side. A one inch deep scoop from the center of each of the small grids was taken. All the aliquots were combined and the total sample transported in the ice chest to TBE.

1.

Surface Water Surface water samples were collected monthly at four indicator stations and one control station in the Delaware River Bay estuary. One location (1 1A1) is at the outfall area (which is the area where liquid radioactive effluents from the Salem Station are discharged into the Delaware River), one is downstream from the.outfall area (7E1), and one is directly west of the outfall area at the mouth of the Appoquinimink River (1 2C1).

Two upstream locations are in the Delaware River (11F2) and at the mouth of the Chesapeake and Delaware Canal (16F1), the latter being sampled when the flow is from the Canal into the river.

Station 12C1, directly west, at the mouth of the Appoquinimink River, serves as the operational control. Location 12C1 was chosen as the control location because the physical characteristics of this station more closely resemble those of the outfall area than do those at the farther upstream location (1 F2). As discussed in the pre-operational summary report, due to the tidal nature of this Delaware River Bay estuary, there are flow rate and salinity variations. These variations will account for differences in concentrations of potassium and associated gross beta from K-40.

Gross Beta Gross beta activity was detected in all of the 48 indicator station samples with concentrations ranging from 5 to 264 pCi/L and an average concentration of 94 pCi/L, and in all 12 of the control station samples with concentrations ranging from 4 to 264 pCi/L and an average concentration of 102 pCi/L. The maximum preoperational level detected was 110 pCi/L with an average concentration of 32 pCi/L. (Table C-14, Appendix C)

[Figure 4 - Quarterly results for all locations are plotted for the years 1990 to 2013, with an inset graph depicting the current period 1973 to 2013.]

Tritium Tritium activity was detected in one of 48 indicator samples with a concentration of 265 pCi/L and was not detected in any of the control samples. The maximum preoperational level detected was 600 pCi/L, with an average concentration of 210 pCi/L.

There is no dose from this radioactive material because the exposure pathway is drinking water and the Delaware River is salt/brackish at this point. (Table C-15, Appendix C) [Figure 5

- Quarterly positive results from 1990 to 2013 are plotted, with an inset graph depicting the period 1973 to 2013.]

Gamma Spectrometry Naturally occurring K-40 was detected in 20 of the 48 indicator station samples at concentrations ranging from 47 to 177 pCi/L with an average concentration of 97 pCi/L, and in five of the 12 control station samples at concentrations ranging from 60 to 137 pCi/L and an average of 104 pCi/L. The maximum preoperational level detected for K-40 was 200 pCi/L with an average concentration of 48 pCi/L.

Iodine-131 Iodine-1 31 was not detected in any 46 of the 48 indicator samples or the 12 control samples. See Program Exceptions Section for explanation. (Table C-16, Appendix C)

All other gamma emitters were less than the LLD.

2.

Fish Edible species of fish were collected semi-annually at two indicator stations and one control station and analyzed for gamma emitters in edible flesh.

Samples included channel catfish, white perch, black drum and striped bass.

Gamma Spectrometry Naturally occurring K-40 was detected in all four indicator station samples at concentrations ranging from 3,480 to 4,755 pCi/kg wet with an average concentration of 3,963 pCi/kg wet, and all three control station samples at concentrations ranging from 3,407 to 4,705 pCi/kg wet with an average concentration of 4,132 pCi/kg wet. The maximum preoperational level detected was 13,000 pCi/kg wet with an average concentration of 2,900 pCi/kg wet. (Table C-17, Appendix C)

All other gamma emitters were less than the LLD.

3.

Blue Crab Blue crab samples were collected twice during the season at one indicator and one control station. The edible portions were analyzed for gamma emitters.

Gamma Spectroscopy Naturally occurring K-40 was detected in both indicator station samples at concentrations of 2,599 and 4,316 pCi/kg wet with an average concentration of 3,458 pCi/kg wet, and in both control station samples at concentrations of 2,803 and 2,868 pCi/kg wet with an average concentration of 2,836 pCi/kg wet.

The maximum preoperational level detected was 12,000 pCi/kg wet with an average concentration of 2,835 pCi/kg wet. (Table C-18, Appendix C)

All other gamma emitters were less than the LLD.

4.

Sediment Sediment samples were collected semi-annually from six indicator stations and one control station. Location 6S2 is the only shoreline sediment sample location and is directly subject to tidal fluctuations.

Gamma Spectroscopy Naturally occurring K-40 was detected in all 12 indicator station samples at concentrations ranging from 2,662 to 20,940 pCi/kg dry, with an average concentration of 11,078 pCi/kg dry, and at both control stations samples at concentrations of 16,470 and 17,430 pCi/kg dry with an average concentration of 16,950 pCi/kg dry. The maximum preoperational level detected was 21,000 pCi/kg dry with an average concentration of 15,000 pCi/kg dry.

Cesium-1 37 was not detected in any of the indicator or control samples. The maximum preoperational level detected was 400 pCi/kg dry with an average concentration of 150 pCi/kg dry.

(Figure 6 - Semi-annual positive results from 1990 to 2013 are plotted, with an inset graph depicting the current period 1977 to 2013.)

Naturally occurring Radium (Natural) was detected in five of the 12 indicator station samples at concentrations ranging from 2,403 to 3,441 pCi/kg dry with an average concentration of 2,792 pCi/kg dry, and in one of the two control station samples at a concentration of 3,228 pCi/kg dry. The maximum pre-operational level detected was 1,200 pCi/kg dry with an average concentration of 760 pCi/kg dry.

Naturally occurring Th-232 was detected in five of the 12 indicator station samples at concentrations ranging from 166 to 1,233 pCi/kg dry with an average concentration of 802 pCi/kg dry, and in both of the two control station samples at concentrations of 869 and 1168 pCi/kg dry with an average concentration of 1,019 pCi/kg dry. The maximum pre-operational level detected was 1,300 pCi/kg dry with an average concentration of 840 pCi/kg dry. (Table C-1 9, Appendix C)

All other gamma emitters were less than the LLD.

E.

Land Use Survey SYNOPSIS OF 2013 LAND USE CENSUS A land use census was conducted in each of the 16 meteorological sectors to identify, within a distance of 8 km (5 miles), the location of the nearest milk animal, the nearest residence and the nearest garden of greater than 50 m 2 (500 ft2) producing broad leaf vegetation. In accordance with Salem and Hope Creek ODCMs, the census was performed using a door to door survey, visual survey, Google Earth and by consulting with local agricultural authorities.

Milk Animal August, 2013 Km (miles)

Nearest Residence August, 2013 Km (miles)

Vegetable Garden August, 2013 Km (miles)

Meat Animal August, 2013 Km (miles)

Meteorological Sector N

NNE NE ENE E

ESE SE SSE S

SSW SW WSW W

WNW NW NNW None None None None None None None None None None None None 7.8 (4.9)

None None None None 8.0 (5.0) 6.2 (3.9) 6.2 (3.9)

None None None None None 6.2 (3.9) 6.9 (4.3) 7.1 (4.4) 6.5 (4.0) 5.5 (3.4) 5.9 (3.7) 6.8(4.2)

None None None None None None None None None None 7.3 (4.6)

None None None None None None 6.8 (4.2)

None None None None None None None None 7.3 (4.6)

None None None None None The 2013 Land Use Census results are summarized in the above table. A comparison of the identified locations from the 2013 table with the 2012 table shows that there is no change to the nearest milk animal, nearest resident, or nearest vegetable garden (>500 ft2) with broadleaf vegetation identified. Therefore, no formal dose evaluation or changes to the SGS and HCGS ODCMs are required.

V.

Annotations to Previous AREOR In the 2012 Annual Radiological Environmental Operating Report Table C-3, the air sample results for the SA-AIO-5S2 for the week of 04/09/12 -

04/16/12 were incorrectly reported as <0, instead of <14.

The "control station" notation in Table C-4 of the 2012 AREOR incorrectly lists six control stations. Only stations 3G1 and 14G1 should have been labeled as controls. (70151506)

In the 2012 Annual Radiological Environmental Operating Report Table C-16, the reported values for 1-131 for July through December were incorrectly reported. All values for 1-131 were below the LLD value of 1 pCi/L.

(70157113)

VI.

Hope Creek Technical Specification Limit for Primary Water Iodine Concentrations The Hope Creek primary water chemistry results for 2013 were reviewed.

The specific activity of the primary coolant did not exceed 0.2 microcuries per gram Dose Equivalent 1-131 (DEI), and the DEI generally ranged from 1 to 2 E-5 microcuries per gram. Therefore, the iodine concentrations in the primary coolant did not exceed the Tech Spec limit specified in section 3.4.5.

VII.

Conclusions The Radiological Environmental Monitoring Program for Salem and Hope Creek Generating Stations was conducted during 2013 in accordance with the SGS and HCGS Technical Specifications and SGS's and HCGS's ODCM. The LLD values required by the Technical Specifications and SGS's and HCGS's ODCM were achieved for this reporting period (See Appendix A and Appendix C). The objectives of the program were also met during this period. The data collected assists in demonstrating that SGS and HCGS were operated in compliance with Technical Specifications and SGS's and HCGS's ODCM requirements.

The concentration of radioactive material in the environment that could be attributable to Salem and Hope Creek stations 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 1973 to 1976, and with historical results collected since commercial operation, PSEG Nuclear Personnel have concluded that the operation of the Salem and Hope Creek Stations had no significant radiological impact on the environment.

From the results obtained, it can be concluded that the levels and fluctuations of radioactivity in environmental samples were as expected for an estuarine environment.

VIII.

References

[1]

Radiation Management Corporation. "Artificial Island Radiological Environmental Monitoring Program - Preoperation Summary - 1973 through 1976". RMC-TR-77-03, 1978.

[2]

Public Service Enterprise Group. "Offsite Dose Calculation Manual"-

Salem Generating Station. Revision 26.

[3]

Public Service Enterprise Group. "Offsite Dose Calculation Manual"-

Hope Creek Generating Station. Revision 26.

[4]

U.S. Nuclear Regulatory Commission: Branch Technical Position -

Regulatory Guide 4.8, "An Acceptable Radiological Monitoring Program", Revision 1, November 1979.

APPENDIX A PROGRAM

SUMMARY

A-1

Intentionally left blank A-2

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY DOCKET NO. 50-272/-311 DOCKET NO. 50-354 January 1, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)

OF ANALYSES DETECTION (RANGE)

DISTANCE AND DIRECTION (RANGE)

(RANGE)

REPORTED PERFORMED (LLD)*

MEASUREMENTS

1. AIRBORNE AIR PARTICULATE (E-3 pCi/mr)

GR-B GAMMA BE-7 408 10 13(355/356)

(5/30) 103(28/28)

(66/159) 32 K-40 w.

NA NA 50 60 SA-APT-14GI C 11.8 MILES WNW SA-APT-1 6S1 0.53 MILES NNW SA-APT-16SI 0.53 MILES NNW 15(52/52)

(8/26) 116(4/4)

(89/144) 56(1/4) 56(1/28)

CS-134 CS-137 15 (52/52)

(8/26) 105 (4/4)

(69/151)

<LLD

<LLD 0

0 0

AIR IODINE (E-3 pCi/rn)

GAMMA 408 1-131 TLD-QUARTERLY 218 70

<LLD

11. DIRECT DIRECT RADIATION (mR/standard quarter)

III. TERRESTRIAL MILK (pCi/L)

NA 13.8 (210/210)

(7/21)

SA-IDM-IFI 5.8 MILES N OF SITE 18.3 (4/4)

(16/20) 14.8 (8/8)

(13/17) 1-131 80 80 NA

<LLD

<LLD GAMMA K-40 1344 (60/60)

SA-MLK-14F4 (1162/1564) 7.6 MILES WNW 1367 (20/20) 1273 (20/20)

(1200/1564)

(1149/1417)

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY DOCKET NO. 50-272/-311 DOCKET NO. 50-354 January 1, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)

OF ANALYSES DETECTION (RANGE)

DISTANCE AND DIRECTION (RANGE)

(RANGE)

REPORTED PERFORMED (LLD)*

MEASUREMENTS MILK (cont'd)

(pCi/L)

CS-134 CS-137 BALA140 RA-226 15 18 15

<LLD

<LLD 0

0 NA 0

WELL WATER (pCi/L)

GR-A GR-B 13 3

13 4

1.8 (1/13)

SA-WWA-3 EI 4.2 MILES NE 1.8(1/13)

H-3 13 200 GAMMA K-40 13

<LLD

<LLD NA NA NA NA NA 0

0 0

NA 0

0 MN-54 CO-58 15 is

<LLD NA 0

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY DOCKET NO. 50-272/-311 DOCKET NO. 50-354 January 1, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)

OF ANALYSES DETECTION (RANGE)

DISTANCE AND DIRECTION (RANGE)

(RANGE)

REPORTED PERFORMED (LLD)*

MEASUREMENTS WELL WATER (cont'd)

(pCi/L)

FE-59 CO-60 ZN-65 ZRNB-95 30 15 30 15 1-131

<LLD

<LLD NA NA NA NA NA NA NA NA NA NA 0

0 0

CS-134 CS-137 BALA140 RA-226 GR-A 15-18 15 0

0 0

0 NA 0

0 POTABLE WATER (pCi/L) 24 3

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION DOCKET NO. 50-272/-311 DOCKET NO. 50-354 January 1, 2013 to December 31, 2013 SALEM COUNTY, NEW JERSEY MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)

OF ANALYSES DETECTION (RANGE)

DISTANCE AND DIRECTION (RANGE)

(RANGE)

REPORTED PERFORMED (LLD)*

MEASUREMENTS POTABLE WATER (cont'd)

(pCi/L)

GR-B 24 4

4.7 (22/24)

(2.9/7.3) 2F3 8.0 MILES NNE 4.8 (I1/12)

(3.4/7.3)

H-3 24 200 GAMMA 24 K-40 NA MN-54 15 CO-58 15 FE-59 30 CO-60 15 ZN-65 30 ZRNB-95 15

<LLD

<LLD NA NA NA NA NA NA NA NA NA 0

0 0

1-131 NA 0

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY DOCKET NO. 50-272/-311 DOCKET NO. 50-354 January 1, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)

OF ANALYSES DETECTION (RANGE)

DISTANCE AND DIRECTION (RANGE)

(RANGE)

REPORTED PERFORMED (LLD)*

MEASUREMENTS POTABLE WATER (cont'd)

(pCi/L)

CS-134 CS-137 BALA 140 RA-226 VEGETATION (pCi/kg wet)

GAMMA 30 BE-7 is 18 15 NA NA NA 60 60 80 NA

<LLD

<LLD NA NA NA NA 0

0 0

279 (4/20)

(228/372)

K-40 1-131 CS-134 CS-137 RA-226 TH-232 3100 (20/20)

(1603/13750)

<LLD

<LLD SA-FPL-IODI 3.9 MILES SSW SA-VGT-14F4 7.6 MILES WNW SA-FPL-ISI 0.57 MILES N 372(1/1) 13750(1/1) 1963 (10/10)

(1269/2433)

<LLD 16 (2/20)

(13/19) 19(1/I)

<LLD

<LLD 0

0 0

<LLD NA

<LLD

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY DOCKET NO. 50-272/-311 DOCKET NO. 50-354 January 1, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN, CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)

OF ANALYSES DETECTION (RANGE)

DISTANCE AND DIRECTION (RANGE)

(RANGE)

REPORTED PERFORMED (LLD)*

MEASUREMENTS FODDER CROPS (pCi/kg wet)

GAMMA BE-7 4

K-40 1-131 00 CS-134 CS-137 RA-226 TH-232 NA NA 60 60 80 NA NA NA 231 (3/3)

(196/249) 3554(3/3)

(2968/4052)

<LLD

<LLD SA-VGT-2G3 11.8 MILES NNE SA-VGT-14F4 7.6 MILES WNW SA-SOL-13E3 5.0 MILES W

<LLD

<LLD 249(1/1) 4052(1/1) 193(I/I) 713(I/1) 0 0

0 0

0 SOIL (pCi/kg dry)

GAMMA 9

BE-7 K-40 NA NA NA 10980 (9/9)

(5038/18510) 18510(I/1)

CS-134 150

<LLD NA 0

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY DOCKET NO. 50-272/-311 DOCKET NO. 50-354 January 1, 2013 to December 31. 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)

OF ANALYSES DETECTION (RANGE)

DISTANCE AND DIRECTION (RANGE)

(RANGE)

REPORTED PERFORMED (LLD)*

MEASUREMENTS SOIL (cont'd)

(pCi/kg dry)

CS-137 RA-226 TH-232 BEEFANDGAME (pCi/kg wet) 180 NA NA NA NA 60 130 (6/9)

(45/227) 2100 (5/9)

(1324/2595) 702 (9/9)

(350/1207)

SA-SOL-10DI 3.9 MILES SSW SA-SOL-3G I 16.5 MILES NE SA-SOL-3G I 16.5 MILES NE 227(1/I) 2595(I/I) 12070(/I)

GAMMA BE-7

<LLD NA NA NA NA NA NA NA NA K-40 1-131 CS-134 CS-137 3307(1/I)

SA-GAM-5C 1 3.14 MILES ENE 3307(1/I) 0 0

0 0

0 60 80

<LLD

<LLD IV. AQUATIC SURFACE WATER (pCi/L)

GR-B 60 4

94 (48/48)

(5/264) 265 (1/48)

SA-SWA-7EI 4.5 MILES SE SA-SWA-I IAI 0.2 MILES SW 145 (12/12)

(22/264) 265 (1/12) 102(12/12)

(4/264)

<LLD H-3 60 200

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY DOCKET NO. 50-272/-311 DOCKET NO. 50-354 January 1, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)

OF ANALYSES DETECTION (RANGE)

DISTANCE AND DIRECTION (RANGE)

(RANGE)

REPORTED PERFORMED (LLD)*

MEASUREMENTS SURFACE WATER (cont'd)

(pCi/L)

GAMMA 60 K-40 MN-54 CO-58 0D FE-59 CO-60 ZN-65 ZRNB-95 1-131 CS-134 NA 15 15 30 15 30 15 97 (20/48)

(47/177)

SA-SWA-7E I 4.5 MILES SE

<LLD

<LLD 112(5/12)

(84/177) 104 (5/12)

(60/137) 0 0

0 0

0 1.6(2/48)

(I.5/I.7)

.SA-SWA-16FI 6.9 MILES NNW 1.7 (1/12) 15

<LLD CS-137 18

<LLD

<LLD 0

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY DOCKET NO. 50-272/-311 DOCKET NO. 50-354 January I, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)

OF ANALYSES DETECTION (RANGE)

DISTANCE AND DIRECTION (RANGE)

(RANGE)

REPORTED PERFORMED (LLD)*

MEASUREMENTS SURFACE WATER (cont'd)

(pCi/L)

FISH (pCi/kg wet)

BALA140 15

<LLD

<LLD 0

GAMMA K-40 7

MN-54 CO-58 FE-59 CO-60 ZN-65 CS-134 CS-137 RA-226 NA 130 130 260 130 260 130 150 3963 (4/4)

(3480/4755)

SA-ESF-7EI 4.5 MILES SE 4402 (2/2)

(4048/4755) 4132 (3/3)

(3407/4705)

<LLD

<LLD 0

0 0

0 NA

<LLD

<LLD 0

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY DOCKET NO. 50-272/-3 11 DOCKET NO. 50-354 January I, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)

OF ANALYSES DETECTION (RANGE)

DISTANCE AND DIRECTION (RANGE)

(RANGE)

REPORTED PERFORMED (LLD)*

MEASUREMENTS BLUE CRABS (pCi/kg wet)

GAMMA 4

K-40 MN-54 CO-58 FE-59 CO-60 ZN-65 CS-134 CS-137 RA-226 NA 130 130 260 130 260 130 150 NA 3458(2/2)

(2599/4316)

SA-ECH-I IA I 0.2 MILES SW 3458(2/2)

(2599/4316) 2836 (2/2)

(2803/2868)

<LLD

<LLD 0

0 0

SEDIMENT (pCi/kg dry)

GAMMA BE-7 14 NA

<LLD

<LLD 0

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SALEM GENERATING STATION HOPE CREEK GENERATING STATION SALEM COUNTY, NEW JERSEY DOCKET NO. 50-272/-311 DOCKET NO. 50-354 January I, 2013 to December 31, 2013 MEDIUM OR PATHWAY ANALYSIS AND LOWER ALL INDICATOR LOCATIONS LOCATION WITH HIGHEST MEAN CONTROL LOCATION NUMBER OF SAMPLED TOTAL NUMBER LIMIT OF MEAN NAME MEAN MEAN NONROUTINE (UNIT OF MEASUREMENT)

OF ANALYSES DETECTION (RANGE)

DISTANCE AND DIRECTION (RANGE)

(RANGE)

REPORTED.

PERFORMED (LLD)*

MEASUREMENTS SEDIMENT (cont'd)

(pCi/kg dry)

K-40 CS-134 CS-137 RA-226 TH-232 NA 150 180 NA NA 11078 (12/12)

(2662/20940)

SA-ESS-16F1 6.9 MILES NNW 20485(2/2) 16950 (2/2)

(20030/20940)

(16470/17430)

<LLD

<LLD 0

0 0

2792(5/12)

(2403/3441) 802(5/12)

(166/1233)

SA-ESS-12CI C 2.5 MILES WSW SA-ESS-16F I 6.9 MILES NNW 3228 (1/2) 1093 (2/2)

(1017/1168) 3228(1/2) 1019 (2/2)

(869/1168)

LLD LISTED IS THE LOWER LIMIT OF DETECTION WHICH WE ENDEAVORED TO ACHIEVE DURING THIS REPORTING PERIOD.

- MEAN CALCULATED USING VALUES ABOVE LLD ONLY. FRACTION OF MEASUREMENTS ABOVE LLD ARE IN PARENTHESES.

Intentionally left blank

APPENDIX B SAMPLE DESIGNATION AND LOCATIONS B-I

Intentionally left blank B-2

SAMPLE DESIGNATION The PSEG's Laboratory Testing Services (LTS) identifies samples by a three part code.

The first two letters are the program identification code. Because of the proximity of the Salem and Hope Creek Stations a common environmental surveillance program is being conducted. The identification code, "SA", has been applied to Salem and Hope Creek stations. The next three letters are for the media sampled.

AIO =

APT =

ECH =

ESF =

ESS =

FPL =

FPV =

GAM =

Air Iodine Air Particulate Hard Shell Blue Crab Edible Fish Sediment Green Leaf Vegetables Vegetables (Various)

Game (Muskrat)

IDM =

MLK =

PWR =

PWT =

SOL =

SWA =

VGT =

WWA=

Immersion Dose (TLD)

Milk Potable Water (Raw)

Potable Water (Treated)

Soil Surface Water Fodder Crops (Various)

Well Water The last four symbols are a location code based on direction and distance from a standard reference point. The reference point is located at the midpoint between the center of the Salem 1 and Salem 2 containments. Of these, the first two represent each of the sixteen angular sectors of 22.5 degrees centered about the reactor site. Sector one is divided evenly by the north axis and other sectors are numbered in a clockwise direction as follows:

I=N 2 = NNE 3 =NE 4 = ENE 5=E 6 = ESE 7 =SE 8 = SSE 9=S 10 = SSW 11 =SW 12 = WSW 13=W 14 = WNW 15= NW 16 = NNW The next digit is a letter which represents the radial distance from the reference point:

S A

B C

D

= On-site location

= 0-1 miles off-site

= 1-2 miles off-site

= 2-3 miles off-site

= 3-4 miles off-site E

=

4-5 miles off-site F

=

5-10 miles off-site G

=

10-20 miles off-site H

=

>20 miles off-site The last number is the station numerical designation within each sector and zone; e.g.,

1,2,3,...etc. For example, the designation SA-WWA-3E1 would indicate a sample in the Salem and Hope Creek program (SA), consisting of well water (WWA), which had been collected in sector number 3, centered at 45 degrees (north east) with respect to the midpoint between Salem 1 and 2 containments at a radial distance of 4 to 5 miles off-site, (therefore, radial distance E). The number 1 indicates that this is sampling station

1 in that particular sector.

B-3

TABLE B-1 SAMPLING LOCATIONS Specific information about the individual sampling locations are given in Table B-I. Maps B-1 and B-2 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 iSi 2S2 2S4 3S1 4S1 5S1 5S2 6S1 6S2 7S1 8S1 9S1 10Sl 11Sl 12S1 13S1 14S1 15S1 15S2 16S1 16S2 16S3 11A1 IIA1A STATION LOCATION 0.57mi. N 0.4 mi. NNE; Lamp Pole 65 Near HC Switch Yard 0.6 mi. NNE 0.58 mi. NE 0.60 mi. ENE 0.86 mi. E; site access road 0.86 mi. E; site access road, Duplicate sample 0.17mi. ESE; area around Helicopter Pad 0.23mi. ESE; area around Helicopter Pad 0.12 mi. SE; station personnel gate 0.14 mi. SE; station personnel gate 0.17 mi. SSE 0.14 mi. SSW; inlet cooling water bldg.

0.09 mi. SW; service water inlet bldg.

0.09 mi. W 0.11 mi. WNW 0.17.mi. NNW 0.57 mi. NW 0.61 mi. NNW 0.57 mi. NNW 0.60 mi. N 0.74 mi. NNW 0.2 mi. SW; outfall area

0. 15 mi. SE; Located at the plant barge slip LATITUDINAL DEG. MIN. FT 39 260 39 98 39-28-110 39 140 39-28-023 39-27-668 39 668 39-27-698 39 719 39 720 39 676 39-27-636 39 700 39 719 39 756 39 801 39-27-893 39 161 39-28-12 39 215 39-28-16 39 350 39 59 39-27-41 LONGITUDINAL DEG. MIN. FT 75 222 75 10 75-31 -992 75 678 75 544 75-31 -187 75-31 -187 75 979 75-31 -912 75 15 75 055 75 091 75 160 75 225 75 236 75 267 75 280 75 525 75 32 75 432 75 17 75 550 75 25 75 02 IDM,VGT IDM IDM IDM IDM AIO,APT,IDM AIO, APT IDM,SOL,ESS IDMSOL,ESS IDM IDM IDM IDM IDM IDM IDM IDM IDM,VGT IDM IDM,VGT IDM IDM ECH,ESF,ESS,SWA Alternate SWA SAMPLE TYPE

TABLE B-1 (cont'd)

STATION CODE 15A1 16A1 5C1 12C1 12C1A 4D2 5D1 10D1 14D1 15D1 2E1 3E1 7E1 7E1A 11E2 12E1 13E1 13E3 16E1 1F1 1F2 2F2 2F3 2F5 2F6 2F9 2F10 STATION LOCATION 0.65 mi. NW; cooling tower blow down discharge line outfall 0.24 mi. NNW; south storm drain discharge line 3.14 mi. ENE 2.5 mi. WSW; west bank of Delaware River 3.7 mi. WSW; Located at the tip of Augustine Beach Boat Ramp 3.7 mi. ENE; Alloway Creek Neck Road 3.5 mi. E; local farm 3.9 mi. SSW; Taylor's Bridge Spur 3.4 mi. WNW; Bay View, Delaware 3.8 mi NW; Rt. 9, Augustine Beach 4.4 mi. NNE; local farm 4.2 mi. NE; local farm 4.5 mi. SE; 1 mi. W of Mad Horse Creek 8.87 mi. SE; Located at the end of Bayside Road 5.0 mi. SW; Rt. 9 4.4 mi. WSW; Thomas Landing 4.2 mi. W; Silver Run Road (Rt. 9) 5.0 mi. W; Local Farm, Odessa, DE 4.1 mi. NNW; Port Penn 5.8 mi. N; Fort Elfsborg 7.1 mi. N; midpoint of Delaware River 8.5 mi. NNE; Pole at Comer of 5th & Howell, Salem 8.0 mi. NNE; Salem Water Company 7.4 mi. NNE; Salem High School 7.3 mi. NNE; Southern Training Center 7.5 mi. NNE; Local Farm, Tilbury Rd, Salem 9.2 mi. NNE; Local Farm, South Broadway (Rt. 49) Pennsville LATITUDINAL DEG. MIN. FT 39 67 39 24 39 250 39 22 39 17 39-29-292 39 396 39-24-613 39 26 39-30-125 39-31 -380 39 098 39 08 39 57 39 328 39 862 39 989 39 17 39 762 39 693 39 08 39 522 39 40 39 448 39-33-713 39 55 39-35-35 LONGITUDINAL DEG. MIN. FT 75-32-19 75 58 75-28-430 75 08 75 48 75 175 75 334 75-33-733 75 521 75-35-28 75 428 75 646 75 64 75 24 75 546 75 968 75 735 75 30 75 580 75-31 -124 75 54 75-28-120 75-27-18 75-28-514 75 819 75-29-30 75-29-35 SAMPLE TYPE ESS ESS GAM ECH,ESF,ESS,SWA Alternate SWA IDM AIO,APT,IDM IDM,SOL,VGT IDM IDM IDM IDMWWA ESF,ESS,SWA Alternate SWA IDM IDM IDM MLK,VGT,SOL AIO,APT,IDM,SOL AIO,APT, IDM SWA IDM PWR,PWT IDM AIO,APT, IDM FPV,FPL,SOL FPV,FPL

TABLE B-1 (cont'd)

STATION CODE 3F6 3F7 4F2 5F1 6F1 7F2 8F1 9F1 1 0F2 11F1 12F1 13F2 13F3 13F4 14F2 14F4 15F3 15F4 16F1 16F1A 16F2 1G1 1G3 2G2 2G3 2G4 STATION LOCATION 6.5 mi. NE; Local Farm, Salem/Hancocks Bridge Road 7.2 mi. NE; Local Farm, Beasley Neck Road, RD#3 6.0 mi. ENE; Mays Lane, Harmersville 6.5 mi. E; Canton 6.4 mi. ESE; Stow Neck Road 9.1 mi. SE; Bayside, New Jersey 9.7 mi. SE; Woodland Beach, DE 5.3 mi. S; D.P.A.L. 48912-30217 5.8 mi. SSW; Rt. 9 6.2 mi. SW; Taylor's Bridge Delaware 9.4 mi. WSW; Townsend Elementary School 6.5 mi W; Odessa, Delaware 9.3 mi. W; Redding Middle School, Middletown, Delaware 9.8 mi. W; Middletown, Delaware 6.7 mi. WNW; Boyds Comer 7.6 mi. WNW; local farm 5.4 mi. NW 7.0 mi. NW; local farm; Port Penn Road; Delaware 6.9 mi. NNW; C&D Canal 6.84 mi. NNW; Located at the C&D Canal tip 8.1 mi. NNW; Delaware City Public School 10.9 mi. NNE; Rte. 49, South Broadway 19 mi. N; N. Church St. Wilmington, Del (Old Swedish Church Yard Park) 13.5 mi. NNE; Local Farm; Pointers Auburn Road (Rt. 540), Salem, NJ 08079 11.8 mi. NNE; Local Milk Farm, Comer of Routes 540 & 45, Mannington, NJ 11.3 mi. NNE; large family garden; Rt 45 & Welchville Rd,Mannington, NJ LATITUDINAL DEG. MIN. FT 39 03 39-32-07 39-29-953 39-28-360 39-26-396 39-22-971 39-19-933 39-23-042 39-23-034 39 766 39-23-778 39-27-297 39-27-215 39-26-857 39-29-979 39-30-44 39-30-987 39-31-21 39-33-55 39-33-34 39-34-314 39-37-113 39-44-287 39-38-19 39-36-21 39-36-02 LONGITUDINAL DEG. MIN. FT 75-28-00 75-25-46 75-26-076 75-25-031 75-25-148 75-24-261 75-28-463 75-32-95 75-34-152 75-37-632 75-41 -311 75-39-372 75 543 75-43-111 75-39-042 75-40-52 75 586 75-38-31 75-34-25 75-33-56 75-35-429 75-30-178 75-32-512 75-26-10 75-24-53 75 21 SAMPLE TYPE FPV,FPL FPV,FPL IDM IDM,SOL IDM IDM IDM IDM IDM IDM IDM IDM IDM IDM IDM MLK,VGT,SOL IDM FPV ESS,SWA Alternate SWA IDM FPV IDM FPV MLK,FPV,VGT,SOL FPV

TABLE B-1 (cont'd)

STATION CODE STATION LOCATION 9G1 9G2 10G1 14G1 16G1 3H1 3H5 10.3 mi. S; Local Farm, Woodland Beach Rd., Smyrna, Delaware 10.7 mi. S; Local Farm, Woodland Beach Road, Smyrna, Delaware 12 mi. SSW; Smyma, Delaware 11.8 mi. WNW; Rte. 286/Bethel Church Road; Delaware 15 mi. NNW; Across from Greater Wilmington Airport 32 mi. NE; National Park, New Jersey 25 mi. NE; Farm Market, Rt 77 LATITUDINAL DEG. MIN. FT 39-18-47 39-18-39 39 223 39-31 -290 39-40-637 39 599 39 040 LONGITUDINAL DEG. MIN. FT 75 50 75-34-11 75 095 75 495 75 570 75 96 75 380 SAMPLE TYPE FPV FPV,FPL IDM AIO,APT, IDM IDM IDM FPL,FPV NOTE: All station locations are referenced to the midpoint of the two Salem Units' Containments. The coordinates of this location are: Latitude N 390 - 27' -46.5" and Longitude W 750 - 32' - 10.6".

All Vegetables (FPV & FPL) and Vegetation (VGT), are management audit samples. They are not required by the Salem & Hope Creek Stations' Tech Specs nor listed in the Stations ODCMs. Vegetable samples are not always collected in consecutive years from the same farmer due to crop rotation.

-4

TABLE B-2 SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (Program Overview)

EXPOSURE PATHWAY NUMBER OF REPRESENTATIVE SAMPLES AND SAMPLING AND AND/OR SAMPLE SAMPLE LOCATIONS COLLECTION TYPE/FREQUENCY* OF FREQUENCY ANALYSIS

1. DIRECT RADIATION Fifty-eight routine monitoring stations with two or Quarterly Gamma dose/ quarterly more dosimeters placed as follows:

Dosimeters An inner ring of stations, one in each land based meteorological sector (not bounded by water) in the general area of the site boundary.

WAn outer ring of stations, one in each land-based cmeteorological sector in the 5 - 11 km range (3.1 -

6.9 miles) from the site (not bounded by or over water).

The balance of the stations placed in special interest areas such as population centers, nearby residences, and schools and in two areas to serve as control stations: 3G1, 14G1.

TABLE B-2 (cont'd)

SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM EXPOSURE PATHWAY NUMBER OF REPRESENTATIVE SAMPLES AND SAMPLING AND AND/OR SAMPLE SAMPLE LOCATIONS COLLECTION TYPE/FREQUENCY* OF FREQUENCY ANALYSIS

2. ATMOSPHERIC

a. Air Particulate

b.

Air Iodine

3. TERRESTRIAL

a. Milk 7 Samples from 6 locations:

1 sample from close to the Site Boundary: 5S1.

1 duplicate: close to the Site Boundary: 5S2.

3 Samples in different land based sectors: 1 F1, 2F6, 5D1.

1 Sample from the vicinity of a community: 16E1.

1 Sample from a control location, as for example 15 - 30 km distant (9.3 - 18.6 miles) and in the least prevalent wind direction: 14G1.

Samples from milking animals in 3 locations within 5 km distance (3.1 miles). If there are none, then, 1 sample from milking animals in each of 3 areas between 5 - 8 km distant (3.1 - 5.0 miles): 13E3, 14F4, 2G3(1).

1 Sample from milking animals at a control location 15 -

30 km distant (9.3 - 18.6 miles): 3G1.

Samples from one or two sources only if likely to be affected. (Although wells in the vicinity of SGS/HCGS are not directly affected by plant operations, 3E1 farm's well, is sampled as management audit sample).

Continuous sampler operation with sample collection weekly or more frequently if required by dust loading Semi-monthly (when animals are on pasture)

Monthly (when animals are on pasture)

Gross Beta / weekly Gamma isotopic analysis /

quarterly composite Iodine-1 31 / weekly Gamma scan / semi-monthly Iodine-1 31 / semi-monthly Gamma scan / monthly Iodine-131 / monthly

b. Well Water (Ground)

Monthly Gamma Scan / monthly Gross alpha / monthly Gross beta / monthly Tritium / monthly

TABLE B-2 (cont'd)

SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM EXPOSURE PATHWAY NUMBER OF REPRESENTATIVE SAMPLES AND SAMPLING AND AND/OR SAMPLE SAMPLE LOCATIONS COLLECTION TYPE/FREQUENCY*

FREQUENCY OF ANALYSIS

c. Potable Water (Drinking Water)

I

d. Vegetables

e. Fodder Crops One sample of the nearest water supply affected by its discharge (No potable water samples are required as liquid effluents discharged from SGS/HCGS do not directly affect this pathway). However, for management audit samples, one raw and one treated sample from a public water supply (City of Salem Water and Sewer Department) is collected:

2F3.

One sample of each principal class of food products from area that is irrigated by water in which liquid plant wastes have been discharged (The Delaware River at the location of SGS/HCGS is a brackish water source and is not used for irrigation of food products). Management audit samples are collected from various locations during harvest: 2F9, 2F10, 3F6, 3F7, 2G2, 9G1, 9G2, and 3H5. In addition, Broad leaf vegetation (cabbage and kale) was planted &

collected onsite (1S1, 15S1, 16S1) and across the river, 10DI, in lieu of having a milk farm within 5 km (3.1 miles) of the Site(1).

Although not required by SGS/HCGS ODCM, a sample of crops normally used as cattle feed (silage) were collected from our milk farms as management audit samples: 14F4, 3G1, 2G3, 13E3.

Monthly (composited daily)

Annually (at harvest)

Gross alpha / monthly Gross beta / monthly Tritium / monthly Gamma scan / monthly lodine-131 / monthly Gamma scan / on collection Gamma scan / on collection

TABLE B-2 (cont'd)

SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM EXPOSURE PATHWAY NUMBER OF REPRESENTATIVE SAMPLES AND SAMPLING AND AND/OR SAMPLE SAMPLE LOCATIONS COLLECTION TYPE/FREQUENCY*

FREQUENCY OF ANALYSIS

f. Soil

4. AQUATIC ENVIRONMENT

a. Surface Water

b. Edible Fish Although not required by SGS/HCGS ODCM, samples of soil are collected as management audit samples: 6S2, 2F9, 5F1, 1OD1, 16E1, 13E3, 14F4, 2G3, 3G1 (Samples were collected in 2010).

One sample upstream: 1F2.

One sample downstream: 7E1.

One sample outfall: 1 1Al.

One sample cross-stream (mouth of Appoquinimink River):

12 (2).

12C1 2.

And an additional location in the Chesapeake & Delaware Canal: 16F1.

One sample of each commercially and recreationally important species in vicinity of plant discharge area: 1 lA1.

One sample of same species in area not influenced by plant discharge: 2C1 (2).

And an additional location downstream: 7E1.

One sample of each commercially and recreationally important species in vicinity of plant discharge area: 1 lAl.

One sample of same s ecies in area not influenced by plant discharge: 12C1P2)

Every 3 years (2010-2013-2016)

Monthly Gross Beta / monthly Gamma scan / monthly Tritium / monthly**

Gamma scan / on collection Semi-annually Gamma scan (flesh) / on collection

c. Blue Crabs Semi-annually Gamma scan (flesh) / on collection

TABLE B-2 (cont'd)

SALEM AND HOPE CREEK GENERATING STATIONS RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SAMPLING AND NUMBER OF REPRESENTATIVE SAMPLES AND SAMPLE COLLECTION TYPE/FREQUENCY*

EXPOSURE PATHWAY LOCATIONS FREQUENCY OF ANALYSIS AND/OR SAMPLE

d. Sediment One sample from downstream area: 7E1.

One sample from cross-stream area and control location:

12Cl1t2.

One sample from outfall area: 1 1A1.

One sample from upstream, the C & D Canal: 16F1.

One sample from shoreline area: 6S2.

One sample from Cooling Tower Blowdown discharge:

15A1.

One sample south storm drain discharge line: 16A1.

Semi-annually Gamma scan / on collection K)

Except for Dosimeters, the quarterly analysis is performed on a composite of individual samples collected during the quarter.

- Tech Specs and ODCM require quarterly analysis but due to the tritium leak at Salem, it was decided to analyze surface waters on a monthly basis for tritium.

(1) While these milk locations are not within the 5 km range, they are the closest farms in the Site vicinity.

Since broad leaf vegetation is acceptable in lieu of milk collections, LTS personnel planted and harvested cabbage at three locations on Site (1S1, 15S1, 16S1) and one in Delaware (10D1).

(2)Station 12C1 was made the operational control (1975) for aquatic samples since the physical characteristics of this station more closely resemble those of the outfall area than do those at the upstream location originally chosen. This is due to the distance from Liston Point, which is the boundary between the Delaware River and Delaware Bay. As discussed extensively in the SGS/HCGS Pre-operational reports, the sampling locations further upstream show significantly lower background levels due to estuarine tidal flow.

MAP B-1 SALEM AND HOPE CREEK GENERATING STATIONS' RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ON-SITE SAMPLING LOCATIONS B-13

MAP B-2 SALEM AND HOPE CREEK GENERATING STATIONS' RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM OFF-SITE SAMPLING LOCATIONS B-14

APPENDIX C DATA TABLES C-I

Intentionally left blank C-2

TABLE C-I CONCENTRATIONS OF GAMMA EMITTERS IN QUARTERLY COMPOSITES OF AIR PARTICULATES, 2013 Results in Units of 10-3 pCi/m3 +/- 2 Sigma STATION ID SA-APT-14G1 (C)

COLLECTION PERIOD START STOP 01/02113 - 04/01/13 04/01/13 - 07/01/13 07/01/13 - 09/30/13 09/30/13 - 12/30/13 AVERAGE*

Be-7 69 +/- 27 151 +/- 32 96 +/- 27 105 +/- 26 G A M M A E M IT T E R S......... >

K-40 Cs-134

<31

<2

<31

<2

<20

<2

<21

<1 Cs-137

<2

<1

<1 SA-APT-16E1 01/02/13 04/01/13 07/01/13 09/30/13 04/01/13 07/01/13 09/30/13 12/30/13 AVERAGE*

105 +/- 68 78 +/- 31 111 +/-47 146 +/- 32 108 +/- 30 110 +/- 56 125 +/- 42 144 +/- 37 107 +/- 22 89 34 116 +/- 47

< 21

< 16

31

< 11

<1

<2

<1

<2

<1

<2

<1

<2 SA-APT-16S1 01128/13 04/01/13 07/01/13 09/30/13 04/01/13 07/01/13 09/30/13 12/30/13

< 37

< 21

< 45

<3 56 +/-18

<3

<2

<3

<2

<2 SA-APT-1 F1 01/02/13 04/01/13 07/01/13 09/30/13 AVERAGE*

- 04/01/13

- 07/01/13

- 09/30/13

- 12/30/13 AVERAGE*

- 04/01/13

- 07/01/13

- 09/30/13

- 12/30/13 80 112 99 81

+/- 31

+/- 32

+/- 28

+/- 29

< 35

< 29

< 15

50

<2

<1

<2

<1

<2

<2 56 +/- 0 93 +/- 30 SA-APT-2F6 01/02/13 04/01/13 07/01/13 09/30/13 103 108 95 76

+/- 38

+/- 29

+/- 28

+/- 24

< 16

< 30

< 24

< 27

<2

<1

<2

<1

<1 AVERAGE*

96 +/- 28

THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES (C) CONTROL STATION C-3

TABLE C-1 CONCENTRATIONS OF GAMMA EMITTERS IN QUARTERLY COMPOSITES OF AIR PARTICULATES, 2013 Results in Units of 10-3 pCi/m3 +/- 2 Sigma STATION ID COLLECTION PERIOD START STOP SA-APT-5D1 01/02/13 04/01/13 07/01/13 09/30/13

- 04/01/13

- 07/01/13

- 09/30/13

- 12/30/13 AVERAGE*

- 04/01/13

- 07/01/13

- 09/30/13

- 12/30/13 AVERAGE*

Be-7 112 +/- 28 121 +/- 32 105 +/- 38 102 +/- 35 110 +/- 17

<.--------- GAMMA EMITTERS.-------->

K-40 Cs-134

<36

< 3

<44

< 2

< 24

<2

<24

<3 Cs-137

<2

<2 SA-APT-5S1 01/02/13 04/01/13 07/01/13 09/30/13 82 104 83 66

+/- 27

+/- 25

+ 27

+/- 23

< 29

< 21

< 31

< 28

<1

<2

<1

<2

<2 SA-APT-6S1 01/28/13 04/01/13 07/01/13 09/30/13 04/01/13 07/01/13 09/30/13 12/30/13 84 +/- 31 70 +/- 25 159 +/- 28 109 +/- 37 120 +/- 27 115 +/- 74

< 23

< 22

< 41

< 32

<2

<1

<2

<1

<2

<1 AVERAGE*

THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES C-4

TABLE C-2 CONCENTRATIONS OF GROSS BETA EMITTERS IN AIR PARTICULATES, 2013 Results in units of 10-3 pCi/rn3 +/- 2 sigma COLLECTION PERIOD START STOP UIIU-/ I j 01/07/13 01/14/13 01/21/13 01/28/13 02/04/13 02/11/13 02/19/13 02/27/13 03/04/13 03/11/13 03/18/13 03/25/13 04/01/13 04/08/13 04/15/13 04/22/13 04/29/13 05/06/13 05/13/13 05/20/13 05/28/13 06/03/13 06/10/13 06/17/13 06/24/13 07/01/13 07/08/13 07/15/13 07/22/13 07/29/13 08/06/13 08/13/13 08/19/13 08/26/13 09/03/13 09/09/13 09/16/13 09/23/13 09/30/13 10/08/13 10/16/13 10/21/13 10/28/13 11/04/13 11/12/13 11/18/13 11/25/13 12/02/13 12/09/13 12/16/13 12/23/13 UIIUIII1

- 01/14/13

- 01/21/13

- 01/28/13

- 02/04/13

- 02/11/13

- 02/19/13

- 02/27/13

- 03/04/13

- 03/11/13

- 03/18/13

- 03/25/13

- 04/01/13

- 04/08/13

- 04/15/13

- 04/22/13

- 04/29/13

- 05/06/13

- 05/13/13

- 05/20/13

- 05/28/13

- 06/03/13

- 06/10/13

- 06/17/13

- 06/24/13

- 07/01/13

- 07/08/13

- 07/15/13

- 07/22/13

- 07/29/13

- 08/06/13

- 08/13/13

- 08/19/13

- 08/26/13

- 09/03/13

- 09/09/13

- 09/16/13

- 09/23/13

- 09/30/13

- 10/08/13

- 10/16/13

- 10/21/13

- 10/28/13

- 11/04/13

- 11/12/13

- 11/18/13

- 11/25/13

- 12/02/13

- 12/09/13

- 12/16/13

- 12/23/13

- 12/30/13 CONTROL SA-APT-14G1 25+/-5 21 +/- 4 16 +/- 3 17 +/- 3 22 +/- 4 20 +/- 4 13 +/- 2 8+/-3 10 4

8+/-3 16+/- 4 9+/-3 8+/-3 22 +/-4 14+/- 3 10 +/- 4 15 +/- 3 9+/-3 8+/-3 14 3

13+/- 3 17 4

8+/-3 14+/- 3 12+/- 3 14+/- 3 8+/-3 13 +/- 3 13 +/- 3 13 +/- 3 16 +/- 3 16 +/- 3 10 +/- 3 13 +/- 3 19 +/- 3 17 +/- 3 20 +/- 3 12 +/- 3 11 +/-3 26 +/-3 16+/- 3 19 4

16+/- 3 18+/- 3 13+/- 3 17+/- 4 9+/-3 17+/- 3 20 +/-4 22 +/-4 19+/- 4 13+/- 3 U SA-APT-1 F1 27+/-5 23 +/- 4 15 +/- 3 13 +/- 3 21 +/- 3 17+/-3 14+/- 2 10+/- 3 8+/-4 7+/-3 16 +/-4 5+/-3 7+/-3 15+/- 3 12+/- 3 10+/- 4 13+/- 3 10+/- 3 7+/-3 13+/- 3 10 +/- 3 16 +/- 4 7+/-3 13+/- 3 10+/- 3 11+/- 3 7+/-3 13+/- 3 13+/- 3 12+/- 3 14 +/-3 13+/- 3 10 +/- 3 12 +/- 3 18 +/- 3 15 +/- 3 21 +/- 3 15 +/- 5 9+/-3 25 +/-4 16+/- 3 15 4

10+/- 3 21 +/-4 14+/- 3 12+/- 3 8+/-3 15+/- 3 17+/- 3 16 3

17 +/- 3 18 +/- 3 SA-APT-2F6 24 +/- 4 23 +/- 3 11+/- 3 17+/- 3 20 +/-3 16+/- 3 13+/- 2 8+/-3 9+/-4 6+/-3 14+/- 3 7+/-3 7+/-2 16+/- 3 10+/- 3 10+/- 3 14+/- 3 9+/-3 8+/-3 12+/- 3 9+/-3 15+/- 4 10+/- 3 11+/- 3 10+/- 3 13+/- 3 6+/-3 12+/- 3 14 +/- 3 12 +/- 3 15 +/- 3 16 +/- 3 12 +/- 3 10 +/- 3 19 +/- 3 16 +/- 3 20 +/- 3 13 +/- 3 11+/- 3 29 +/-3 16+/- 3 11 4

13+/- 3 22 +/-3 15+/- 3 10+/- 3 6+/-2 14+/- 3 21 +/-4 20 +/-3 19 +/- 3 13 +/- 3 GROUP I SA-APT-5D1 30 +/- 5 22 +/- 4 16 +/- 3 12 +/- 3 21 +/- 4 16 +/- 3 11 2

6+/-3 7+/-4 7+/-3 17+/- 4 7+/-3 8+/-3 16+/- 3 11+/- 3 8+/-3 16+/- 3 8+/-3 7+/-3 15+/- 4 10+/- 3 16.+/- 4 7+/-3 12+/- 3 7+/-3 10+/- 3 6+/-3 9+/-3 15+/- 3 13+/- 3 17+/- 3 16+/- 3 10+/- 3 10+/- 3 16+/- 3 16+/- 3 19+/- 3 11+/- 3 10 +/- 3 26 +/- 4 16 +/- 3 13 +/- 4 16 +/- 3 17 +/- 3 15 +/- 3 15 +/- 4 8+/-3 12+/- 3 15 4

20 +/- 3 20 +/- 4 12 +/- 3 SA-APT-5S1 21 +/-4 20 +/- 3 11+/- 3 14 3

19+/- 3 13+/- 3 13+/- 2 7+/-3 6+/-4 8+/-3 11+/- 3 5+/-3 8+/-2 10 3

13+/- 3 8+/-3 14+/- 3 9+/-3 7+/-3 12+/- 3 10 3

16+/- 4 6+/-3 14 3

6+/-3 6+/-3 6+/-2 7+/-3 12+/- 3 11+/- 3 15 +/- 3 13 +/- 3 11+/- 3 9+/-3 18+/- 3 14+/- 3 22 +/-4 11+/- 3 8+/-3 22 +/- 3 12 +/- 3 16 +/- 4 9+/-3 18 3

13 3

6+/-2 11+/- 3 18 +/- 3 16 +/- 3 15 +/- 3 14 +/- 3 SA-APT-6S1 (1)

(1)

(1) 24 +/- 3 10 +/- 2 7+/-1 7+/-2 6+/-3 9+/-3 13+/- 3 10+/- 3 8+/-2 18 +/- 3 13 +/- 3 8+/-3 17+/- 3 7+/-3 8+/-3 12+/- 3 11+/- 3 12+/- 3 8+/-3 16+/- 3 9+/-3 12+/- 3 7+/-2 14+/- 7 14 +/- 3 10 +/- 3 18 +/- 3 15 +/- 3 9+/-3 9+/-3 15+/- 3 16+/- 3 19+/- 3 14+/- 3 12+/- 3 26 +/- 3 16 +/- 3 15 +/- 4 12 +/- 3 24 +/- 4 16 +/- 3 13 +/- 3 10 +/- 3 16 +/- 3 14 +/- 3 18 +/- 3 20 +/- 4 12 +/- 3 AVERAGE*

15 +/- 9 14 +/- 10 14 +/- 10 13 +/- 10 12 +/- 9 13 +/- 9

THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES (1) SEE PROGRAM CHANGES SECTION FOR EXPLANATION C-5

TABLE C-2 TABL C-2CONCENTRATIONS OF GROSS BETA EMITTERS IN AIR PARTICULATES, 2013 Results in units of 10-3 pCi/rn 3 +/-2 sigma COLLECTION GROUP I PERIOD SA-APT-16E1 SA-APT-16S1 01/02/13

-01/07/13 23 +/- 4 (1) 01/07/13

-01/14/13 23 +/- 3 (1) 01/14/13

-01/21/13 15 +/- 3 (1) 01/21/13

-01/28/13 13 +/- 3.

(1) 01/28/13

-02/04/13 19 +/- 3 22 +/- 3 02/04/13

-02/11/13 19 +/- 3 14 +/- 3 02/11/13

-02/19/13 12 +/- 2 10 +/- 2 02/19/13 -02/27/13 6 +/- 3 11 +/- 3 02/27/13 -03/04/13 8 +/- 4 12 +/- 4 03/04/13

-03/11/13 9 +/- 3 7 +/- 3 03/11/13

-03/18/13 12 +/- 3 17 +/- 3 03/18/13

-03/25/13 9 +/- 3 9 +/- 3 03/25/13 -04/01/13 10 +/- 3 8 +/- 2 04/01/13

-04/08/13 17 +/- 3 16 +/- 3 04/08/13

-04/15/13 11 +/- 3 12 +/- 3 04/15/13

-04/22/13 11 +/- 4 12 +/- 3 04/22/13

-04/29/13 15 +/- 3 17 +/- 3 04/29/13

-05/06/13 15 +/- 4

< 17 (2) 05/06/13

-05/13/13 8 +/- 3 8 +/- 3 05/13/13

-05/20/13 12 +/- 3 14 +/- 3 05/20/13 -05/28/13 9 +/- 2 13 +/- 3 05/28/13 -06/03/13 14 +/- 4 12 +/- 3 06/03/13

-06/10/13 9 +/- 3 8 +/- 3 06/10/13

-06/17/13 13 +/- 3 12 +/- 3 06/17/13

-06/24/13 7 +/- 3 9 +/- 3 06/24/13

-07/01/13 10 +/- 3 11 +/- 3 07/01/13

-07/08/13 8 +/- 3 9 +/- 3 07/08/13

-07/15/13 12 +/- 3 14 +/- 3 07/15/13

-07/22/13 13 +/- 3 20 +/- 3 07/22/13 -07/29/13 12 +/- 3 12 +/- 3 07/29/13

-08/06/13 13 +/- 3 17 +/- 3 08/06/13

-08/13/13 15 +/- 3 17 +/- 3 08/13/13

-08/19/13 12 +/- 3 12 +/- 3 08/19/13

-08/26/13 11 +/- 3 16 +/- 3 08/26/13

-09/03/13 21 +/- 3 19 +/- 3 09/03/13

-09/09/13 16 +/- 3 18 +/- 3 09/09/13

-09/16/13 21 +/- 4 26 +/- 4 09/16/13

-09/23/13 11 +/- 3 13 +/- 3 09/23/13

-09/30/13 10 +/- 3 11 +/- 3 09/30/13

-10/08/13 26 +/- 4 29 +/- 4 10/08/13

-10/16/13 15 +/- 3 22 +/- 4 10/16/13

-10/21/13 17 +/- 4 15 +/- 4 10/21/13

-10/28/13 13 +/- 3 13 +/- 3 10/28/13

-11/04/13 20 +/- 4 24 +/- 4 11/04/13

-11/12/13 14 +/- 3 12 +/- 3 11/12/13

-11/18/13 12 +/- 6 13 +/- 4 11/18/13

-11/25/13 11 +/- 3 8 +/- 3 11/25/13

-12/02/13 16 +/- 3 15 +/- 3 12/02/13

-12/09/13 19 +/- 3 18 +/- 3 12/09/13

-12/16/13 16 +/- 3 18 +/- 3 12/16/13

-12/23/13 23 +/- 3 23 +/- 4 12/23/13

-12/30/13 16 +/- 3 14 +/- 3 AVERAGE*

14 +/- 9 14 +/- 10 THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES (1) SEE PROGRAM CHANGES SECTION FOR EXPLANATION (2) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-6

TABLE C-3 CONCENTRATIONS OF IODINE-131* IN FILTERED AIR, 2013 Results in units of 10-3 pCi/m* +/- 2 sigma COLLECTION PERIOD START STOP U IIUI Ij 01/07/13 01/14/13 01/21/13 01/28/13 02/04/13 02/11/13 02/19/13 02/27/13 03/04/13 03/11/13 03/18/13 03/25/13 04/01/13 04/08/13 04/15/13 04/22/13 04/29/13 05/06/13 05/13/13 05/20/13 05/28/13 06/03/13 06/10/13 06/17/13 06/24/13 07/01/13 07/08/13 07/15/13 07/22/13 07/29/13 08/06/13 08/13/13 08/19/13 08/26/13 09/03/13 09/09/13 09/16/13 09/23/13 09/30/13 10/08/13 10/16/13 10/21/13 10/28/13 11/04/13 11/12/13 11/18/13 11/25/13 12/02/13 12/09/13 12/16/13 12/23/13 UIIUII 1

- 01/14/13

- 01/21/13

- 01/28/13

- 02/04/13

- 02/11/13

- 02/19/13

- 02/27/13

- 03/04/13

- 03/11/13

- 03/18/13

- 03/25/13

- 04/01/13

- 04/08/13

- 04/15/13

- 04/22/13

- 04/29/13

- 05/06/13

- 05/13/13

- 05/20/13

- 05/28/13

- 06/03/13

- 06/10/13

- 06/17/13

- 06/24/13

- 07/01/13

- 07/08/13

- 07/15/13

- 07/22/13

- 07/29/13

- 08/06/13

- 08/13/13

- 08/19/13

- 08/26/13

- 09/03/13

- 09/09/13

- 09/16/13

- 09/23/13

- 09/30/13

- 10/08/13

- 10/16/13

- 10/21/13

- 10/28/13

- 11/04/13

- 11/12/13

- 11/18/13

- 11/25/13

- 12/02/13

- 12/09/13

- 12/16/13

- 12/23/13

- 12/30/13 CONTROL SA-AIO-14G1

< 31

< 23

< 14

< 20

< 17

< 21

< 10

< 30

< 28

<8

< 14

< 21

< 17

< 20

< 17

< 18

< 19

< 18

< 16

< 25

< 39

< 29

< 25

< 17

< 38

< 37

< 17

< 30

< 28

< 25

< 29

< 26

< 59

< 45

< 43

< 32

< 26

<34

< 50

< 38

< 42

< 55

< 30

< 32

< 38

< 50

< 45

< 68

< 55

< 32 SA-AIO-1F1

< 27

< 20

< 15

< 16

< 19

< 12

< 26

< 25

<8

< 16

< 28

< 16

< 15

< 16

< 13

< 20

< 22

< 17

< 38

< 30

< 38

< 23

< 22

< 42

< 44

< 23

< 31

< 28

< 17

< 35

< 32

< 28

< 47

< 41

< 42

< 55

< 33

< 43

< 48

< 46

< 39

< 69

< 32

< 37

< 41

< 43

< 31

< 56

< 59

< 29 SA-AIO-2F6

< 25

< 19

< 14

< 15

< 19

< 12

< 26

< 24

<7

< 15

< 27

< 15

< 14

< 15

< 21

< 22

< 18

< 38

< 30

< 38

< 23

< 21

< 41

< 45

< 23

< 32

< 28

< 17

< 35

< 32

< 28

< 46

< 41

< 30

< 29

< 38

< 41

< 35

< 60

< 28

< 35

< 40

< 31

< 59

< 27 GROUP I SA-AIO-5D1

< 31

< 23

< 13

< 20

< 19

< 12

< 27

< 26

<8

< 17

< 26

< 15

< 16

< 15

< 20

< 23

< 18

< 39

< 31

< 37

< 23

< 20

< 39

< 43

< 23

<34

< 29

< 18

< 36

< 35

< 30

< 52

< 45

< 46

< 33

< 32

< 43

< 47

< 39

< 69

< 32

< 39

< 44

< 33

< 62

< 63

< 29 U SA-AIO-5S1

< 25

< 18

< 14

< 15

< 18

< 11

< 28

< 24

<7

< 15

< 25

< 14

< 13

< 14

< 14 14

< 20

< 23

< 17

< 38

< 29

< 36

< 21

< 19

< 37

< 40

< 22

< 33

< 31

< 19

< 32

< 31

< 27

< 50

< 44

< 46

< 32

< 30

< 40

< 42

< 43

< 35

< 61

< 29

< 35

< 39

< 40

< 29

< 58

< 56

< 26 SA-AIO-6S1 (1)

(1)

< 12

< 11

<5

< 23

< 24

<8

< 14

< 21

< 20

< 15

< 18

< 15

< 18

< 17

< 16

< 14

< 22

< 32

< 26

< 22

< 18

<34

< 32

< 46

< 27

< 31

< 27

< 31

< 30

< 26

< 59

< 46

< 41

< 38

< 27

< 35

< 53

< 40

< 44

< 56

< 30

< 32

< 38

< 47

< 41

< 68

< 50

< 29 AVERAGE

IODINE-1 31 RESULTS ARE CORRECTED FOR DECAY TO STOP DATE OF COLLECTION PERIOD & ANALYZED TO AN LLD OF 70 10-3 pCi/mr (1) SEE PROGRAM CHANGES SECTION FOR EXPLANATION C-7

TABLE C-3 iCONCENTRATIONS OF pODINE/131* IN FILTERED AIR, 2013 Results in units of 1 0-3 pCi/rn4 +/- 2 sigma COLLECTION PERIOD 01/02/13-01107113 01/07/13 -

01/14/13 01/14/13-01/21/13 01/21/13 -

01/28/13 01/28/13 -

02/04/13 02/04/13 -

02/11/13 02/11/13-02/19/13 02/19/13 -

02/27/13 02/27/13-03/04/13 03/04/13-03/11/13 03/11/13 -

03/18/13 03/18/13 -

03/25/13 03/25/13 -

04/01/13 04/01/13-04/08/13 04108/13-04/15/13 04/15/13 -

04/22/13 04/22/13-04/29/13 04/29/13-05/06/13 05/06/13-05/13/13 05/13/13 -

05/20/13 05/20/13-05/28/13 05/28/13-06/03/13 06/03/13 -

06/10/13 06/10/13-06/17/13 06/17/13-06/24/13 06/24/13 -

07/01/13 07/01/13 -

07/08/13 07/08/13 -

07/15/13 07/15/13 -

07/22/13 07/22/13 -

07/29/13 07/29/13 -

08/06/13 08/06113-08/13/13 08/13/13-08/19/13 08/19/13 -

08/26/13 08/26/13 -

09/03/13 09/03/13-09/09/13 09/09/13-09/16/13 09/16/13 -

09/23/13 09/23/13 -

09/30/13 09/30/13 -

10/08/13 10/08/13-10/16/13 10/16/13-10/21/13 10/21/13 -

10/28/13 10/28/13-11/04/13 11/04/13-11/12/13 11/12/13-11/18/13 11/18/13 -

11/25/13 11/25/13 -

12/02/13 12/02/13-12/09/13 12/09/13-12116/13 12/16/13-12/23/13 12/23/13 -

12/30/13 GROUP I SA-AIO-16E1 SA-AIO-16S1

< 29 (1)

< 21 (1)

< 13 (1)

< 19 (1)

< 16

< 12

< 19

< 16

<9

<7

<29

<6

< 27

< 25

<7

< 14

< 13

< 21

< 19

< 17

< 15

< 20

< 18

< 15

<20

< 18

< 20

< 83 (2)

< 17

< 16

< 15

< 14

< 23

< 22

< 36

< 32

< 26

< 25

< 22

< 17

< 16

< 38

< 33

< 38

< 33

< 17

< 30

< 29

< 27

< 25

< 26

< 29

< 30

< 27

< 61

< 59

< 46

<44

< 45

< 43

< 33

< 28

< 27

< 35

< 53

< 67

< 39

< 37

<44

< 42

<54

<52

< 29

< 30

< 38

< 33

< 39

<42

<44

< 37

< 38

<61

<64

<44

<47

< 27

< 31 AVERAGE IODINE-131 RESULTS ARE CORRECTED FOR DECAY TO STOP DATE OF COLLECTION PERIOD & ANALYZED TO AN LLD OF 70 10-3 pCi/ma.

(1) SEE PROGRAM CHANGES SECTION FOR EXPLANATION (2) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-8

TABLE C-4 DIRECT RADIATION MEASUREMENTS - QUARTERLY DOSIMITRY RESULTS*, 2013 Results in units of mR/standard quarter STATION ID AVERAGE

+/-2 S.D.

JAN - MAR APR - JUN JUL - SEP OCT - DEC SA-IDM-1F1 18.3 +/- 4.1 16.0 20.0 17.0 20.0 SA-IDM-1G3 13.8 +/- 3.4 12.0 14.0 13.0 16.0 SA-IDM-2E1 13.8 t 2.5 12.0 14.0 14.0 15.0 SA-IDM-2F2 13.5 +/- 4.8 12.0 16.0 11.0 15.0 SA-IDM-2F5 14.5 +/- 3.5 13.0 14.0 14.0 17.0 SA-IDM-2F6 13.0 +/- 3.7 11.0 14.0 12.0 15.0 SA-IDM-2S2 14.5 +/- 3.8 15.0 17.0 13.0 13.0 SA-IDM-2S4 15.0 +/- 4.3 12.0 15.0 16.0 17.0 SA-IDM-3E1 11.8 +/- 3.0 11.0 11.0 11.0 14.0 SA-IDM-3F2 12.8 +/- 2.5 11.0 13.0 13.0 14.0 SA-IDM-3F3 12.3 +/- 3.0 11.0 13.0 11.0 14.0 SA-IDM-3H1 12.0 +/- 4.6 10.0 14.0 10.0 14.0 SA-IDM-3S1 11.3 +/- 3.0 10.0 13.0 10.0 12.0 SA-IDM-4D2 15.0 +/- 3.7 13.0 14.0 16.0 17.0 SA-IDM-4F2 12.8 +/- 3.0 11.0 14.0 12.0 14.0 SA-IDM-4S1 12.5

+ 2.6 11.0 13.0 12.0 14.0 SA-IDM-5D1 13.8 +/- 3.4 12.0 14.0 13.0 16.0 SA-IDM-5F1 12.5 +/- 2.6 11.0 12.0 13.0 14.0 SA-IDM-5S1 12.3 +/- 3.0 11.0 13.0 11.0 14.0 SA-IDM-6F1 11.3 +/- 1.0 11.0 11.0 11.0 12.0 SA-IDM-6S2 17.8 +/- 3.8 15.0 18.0 19.0 19.0 SA-IDM-7F2 9.7 +/- 2.3 9.0 11.0 9.0 (1)

SA-IDM-7S1 10.8 +/- 2.5 9.0 11.0 11.0 12.0 SA-IDM-8F1 14.8 +/- 6.2 13.0 12.0 15.0 19.0 SA-IDM-8S1 10.3 +/- 5.5 12.0 7.0 9.0 13.0 SA-IDM-9F1 17.3 +/- 5.5 14.0 19.0 16.0 20.0 SA-IDM-9S1 10.8 +/- 4.4 13.0 8.0 10.0 12.0 SA-IDM-10D1 15.0 +/- 3.7 13.0 14.0 16.0 17.0 SA-IDM-10F2 15.0 +/- 3.7 13.0 16.0 14.0 17.0 SA-IDM-10G1 15.3 +/- 3.4 13.0 16.0 15.0 17.0 SA-IDM-10S1 11.8 +/- 2.5 10.0 13.0 12.0 12.0 SA-IDM-11E2 16.3 +/- 5.3 14.0 18.0 14.0 19.0 SA-IDM-11F1 15.3 +/- 4.1 13.0 17.0 14.0 17.0 SA-IDM-11S1 10.8 +/- 3.0 9.0 12.0 10.0 12.0 SA-IDM-12E1 15.8 +/- 4.4 13.0 17.0 15.0 18.0 SA-IDM-12F1 14.5 +/- 4.2 14.0 15.0 12.0 17.0 SA-IDM-12S1 13.5 +/- 4.2 12.0 (1)

(1) 15.0 SA-IDM-13E1 12.8 +/- 4.1 11.0 14.0 11.0 15.0 SA-IDM-13F2 14.3 +/- 5.3 12.0 17.0 12.0 16.0 SA-IDM-13F3 14.0 +/- 4.3 12.0 14.0 13.0 17.0 SA-IDM-13F4 16.3 +/- 3.4 14.0 17.0 16.0 18.0 SA-IDM-13S1 18.0 +/- 8.5 15.0 (1)

(1) 21.0 SA-IDM-14D1 13.5 +/- 2.6 12.0 13.0 14.0 15.0 SA-IDM-14F2 15.8 +/- 3.4 14.0 16.0 15.0 18.0 SA-IDM-14S1 17.8 +/- 4.7 21.0 18.0 16.0 16.0 SA-IDM-15D1 15.3 +/- 4.4 14.0 16.0 13.0 18.0 SA-IDM-15F3 14.8 +/- 3.0 13.0 16.0 14.0 16.0 SA-IDM-15S1 11.8 +/- 3.0 10.0 13.0 11.0 13.0 SA-IDM-15S2 13.0 +/- 2.3 12.0 14.0 12.0 14.0 SA-IDM-16E1 15.0 +/- 2.8 15.0 16.0 13.0 16.0 SA-IDM-16F2 13.3 +/- 4.4 12.0 14.0 11.0 16.0 SA-IDM-16G1 14.0 +/- 3.7 12.0 15.0 13.0 16.0 SA-IDM-16S1 14.3 +/- 3.4 12.0 14.0 15.0 16.0 SA-IDM-16S3 13.0 +/- 7.2 17.0 12.0 10.0 (1)

SA-IDM-3G1 (C) 14.3 +/- 3.0 13.0 15.0 13.0 16.0 SA-IDM-14G1 (C) 15.3 +/- 3.0 14.0 16.0 14.0 17.0 SA-IDM-1S1 **

34.3 +/- 5.0 33.0 38.0 33.0 33.0 SA-IDM-16S2 37.0 +/- 5.4 38.0 38.0 33.0 39.0

QUARTERLY ELEMENT TLD RESULTS BY MIRION SAMPLE RESULTS ARE AFFECTED BY THE ISFSI (C) CONTROL STATION (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION C-9

TABLE C-5 CONCENTRATIONS OF IODINE-131* AND GAMMA EMITTERS IN MILK, 2013 Results in units of pCi/L +/- 2 sigma STATION ID COLLECTION PERIOD

< --...---- GAMMA EMITTERS ----------

START STOP 1-131 K-40 Cs-134 Cs-137 BaLa-140 Ra-226 CA HREI Id 42*;2 n41flnll 1'd f1f14:2 nl 7 1,g,.1.

VJA

t.

R e

4An

/ oll r-I 0F--

SA-MLK-14F4 SA-MLK-2G3 SA-MLK-3G1 (C)

SA-MLK-13E3 SA-MLK-14F4 SA-MLK-2G3 SA-MLK-3G1 (C)

SA-MLK-13E3 SA-MLK-14F4 SA-MLK-2G3 SA-MLK-3G1 (C) 01/20/13 I

01/21/13 01/20/13 - 01/21/13 01/20/13 - 01/21/13 02/03/13 - 02/04/13 02/03/13 - 02/04/13 02/03/13 - 02/04/13 02/03/13 - 02/04/13 03/03/13 - 03/04/13 03/03/13 - 03/04/13 03/03/13 - 03/04/13 03/03/13 - 03/04/13 04/08/13 - 04/08/13 04/08/13 - 04/08/13 04/08/13-04/08/13 04/08/13 - 04/08/13 04/21/13 - 04/22/13 04/21/13

- 04/22/13 04/21/13 - 04/22/13 04/21/13 - 04/22/13 05/05/13 - 05/06/13 05/05/13 - 05/06/13 05/05/13 - 05/06/13 05/05/13 - 05/06/13 05/19/13 - 05/20/13 05/19/13 - 05/20/13 05/19/13 - 05/20/13 05/19/13 - 05/20/13 06/02/13 - 06/03/13 06/02/13 - 06/03/13 06/02/13 - 06/03/13 06/02/13 - 06/03/13 06/16/13 - 06/17/13 06/16/13 - 06/17/13 06/16/13 - 06/17/13 06/16/13 - 06/17/13 07/07/13 - 07/08/13 07/07/13 - 07/08/13 07/07/13 - 07/08/13 07/07/13 - 07/08/13

0.7

0.7

0.7

< 0.6

0.9

0.9

0.6

0.8

0.8

< 0.6

0.9

0.4

0.5

0.5

0.5

< 0.4

0.6

0.5

0.5

< 0.6

0.7

0.7

0.8

0.5

0.5

0.4

< 0.5

< 0.6

< 0.9

0.8

0.5

0.8

0.9

0.8

0.9

0.7

0.6

0.5

0.6 1254 +/- 181 1387 +/- 155 1241 +/- 162 1312 +/- 132 1289 +/- 117 1173 +/- 158 1156 +/- 117 1217 +/- 116 1392 +/- 117 1381 +/- 118 1190 +/- 112 1409 +/- 160 1200 +/- 174 1235 +/- 155 1403 +/- 138 1302 +/- 129 1313 +/- 123 1181 +/- 107 1417 +/- 125 1383 +/- 140 1441 +/- 117 1251 +/- 104 1362 +/- 130 1243 +/- 175 1359 +/- 148 1440 +/- 130 1328 +/- 142 1425 +/- 127 1408 +/- 124 1398 +/- 99 1266 +/- 97 1268 +/- 171 1564 +/- 172 1428 +/- 182 1291 +/- 150 1221 +/- 144 1362 +/- 129 1263 +/- 162 1308 +/- 134

<8

<5

<6

<5

<6

<4

<5

<4

<5

<8

<7

<5

<4

<6

<5

<4

<6

<7

<6

<5

<4

<5

<6

<5

<7

<6

<9

<6

<7

<6

<5

<6

<5

<4

<6

<9

<7

<9

<6

<5

<4

<7

<6

<5

<6

<10

<6

<5

<3

<4

<8

<7

<6

<7

<6

<8

<6

<12

<7

<9

<7

<8

<9

<8

<14

<9

< 12

<11

<9

< 13

<9

<8

<6

<9

<11

< 10

<5

<10

<8

<5

<6

<13

<9

<11

<7

<8

<9

10

13

169

182

168

128

137

135

184

< 111

124

121

110

151

167

153

199

119

133

92

159

130

141

117

160

168

150

144

136

132

127

100

118

191

163

193

176

141

140

< 150

< 163 IODINE-131 RESULTS ARE CORRECTED FOR DECAY TO STOP DATE OF OF 1.0 pCi/L (C) CONTROL STATION COLLECTION PERIOD & ANALYZED TO AN LLD C-10

TABLE C-5 CONCENTRATIONS OF IODINE-131* AND GAMMA EMITTERS IN MILK, 2013 Results in units of pCi/L +/- 2 sigma STATION ID COLLECTION PERIOD

<-------.GAMMA EMITTERS --..----- >

START STOP 1-131 K-40 Cs-134 Cs-137 BaLa-140 Ra-226 SA-MLK-13E3 07/21/13 - 07/22/13

< 0.9 1389 +/- 152

< 6

< 7

< 10

< 166 SA-MLK-14F4 07/21/13 - 07/22/13

< 0.7 1488 +/- 159

< 5

< 7

< 9

< 150 SA-MLK-2G3 07/21/13 - 07/22/13

< 0.6 1480 +/- 150

< 5

< 6

< 9

< 166 SA-MLK-3G1 (C) 07/21/13 - 07/22/13

< 0.8 1349 +/- 131

< 5

< 6

< 9

< 150 SA-MLK-13E3 08/18/13 - 08/19/13

< 0.8 1396 +/- 102

< 4

< 5

< 7

< 110 SA-MLK-14F4 08/18/13 - 08/19/13

< 0.8 1312 +/- 103

< 4

< 5

< 7

< 115 SA-MLK-2G3 08/18/13 - 08/19/13

< 0.8 1383 +/- 103

< 4

< 5

< 7

< 103 SA-MLK-3G1 (C) 08/18/13 - 08/19/13

< 0.7 1297 +/- 105

< 3

< 4

< 7

< 86 SA-MLK-13E3 08/25/13 - 08/26/13

< 0.8 1273 +/- 182

< 7

< 8

< 11

< 167 SA-MLK-14F4 08/25/13 - 08/26/13

< 0.9 1256 +/- 162

< 7

< 8

< 9

< 159 SA-MLK-2G3 08/25/13 - 08/26/13

< 0.9 1553 +/- 173

< 7

< 6

< 11

< 156 SA-MLK-3G1 (C) 08/25/13

- 08/26/13

< 0.7 1268 +/- 146

< 6

< 12

< 133 SA-MLK-13E3 09/02/13

- 09/03/13

< 0.7 1277 +/- 131

< 4

< 5

< 11

< 118 SA-MLK-14F4 09/02/13

- 09/03/13

< 0.8 1530 +/- 149

< 6

< 13

< 149 SA-MLK-2G3 09/02/13 - 09/03/13

< 0.7 1261 +/- 146

< 5

< 6

< 9

< 145 SA-MLK-3G1 (C) 09/02/13 - 09/03/13

< 0.7 1194 +/- 136

< 6

< 10

< 151 SA-MLK-13E3 09/15/13 - 09/16/13

< 0.6 1468 +/- 170

< 7

< 9

< 12

< 173 SA-MLK-14F4 09/15/13 - 09/16/13

< 0.7 1506 +/- 187

< 7

< 9

< 155 SA-MLK-2G3 09/15/13 - 09/16/13

< 0.7 1397 +/- 160

< 7

< 12

< 166 SA-MLK-3G1 (C) 09/15/13 - 09/16/13

< 0.7 1188 +/- 160

< 6

< 12

< 150 SA-MLK-13E3 10/07/13 - 10/08/13

< 0.8 1162 +/- 143

< 6

< 7

< 13

< 164 SA-MLK-14F4 10/07/13 - 10/08/13

< 0.7 1315 +/- 138

< 6

< 8

< 12

< 166 SA-MLK-2G3 10/07/13 - 10/08/13

< 0.7 1401 +/- 162

< 6

< 7

< 9

< 186 SA-MLK-3G1 (C) 10/07/13

- 10/08/13

< 0.6 1325 +/- 174

< 5

< 7

< 9

< 165 SA-MLK-13E3 10/20/13 - 10/21/13

< 0.5 1388 +/- 172

< 7

< 8

< 176 SA-MLK-14F4 10/20/13 - 10/21/13

< 0.6 1368 +/- 164

< 6

< 14

< 149 SA-MLK-2G3 10/20/13 - 10/21/13

< 0.6 1302 +/- 171

< 7

< 8

< 11

< 182 SA-MLK-3G1 (C) 10/20/13 - 10/21/13

< 0.5 1149 +/- 166

< 5

< 6

< 14

< 122 SA-MLK-13E3 11/17/13 - 11/18/13

< 0.7 1328 +/- 106

< 3

< 4

< 11

< 69 SA-MLK-14F4 11/17/13 - 11/18/13

< 0.7 1444 +/- 91

< 3

< 4

< 11

< 88 SA-MLK-2G3 11/17/13 - 11/18/13

< 0.7 1300 +/- 95

< 4

< 11

< 102 SA-MLK-3G1 (C) 11/17/13 - 11/18/13

< 0.7 1222 +/- 101

< 3

< 11

< 87 SA-MLK-13E3 11/24/13 - 11/25/13

< 0.8 1412 +/- 155

< 5

< 7

< 13

< 132 SA-MLK-14F4 11/24/13 - 11/25/13

< 0.7 1285 +/- 133

< 6

< 12

< 124 SA-MLK-2G3 11/24/13 - 11/25/13

< 0.8 1201 +/- 145

< 5

< 7

< 11

< 146 SA-MLK-3G1 (C) 11/24/13 - 11/25/13

< 0.7 1162 +/- 142

< 6

< 7

< 13

< 179 SA-MLK-13E3 12/01/13 - 12/02/13

< 0.7 1256 +/- 159

< 7

< 8

< 13

< 170 SA-MLK-14F4 12/01/13 - 12/02/13

< 0.7 1261 +/- 148

< 6

< 5

< 10

< 126 SA-MLK-2G3 12/01/13 - 12/02/13

< 0.9 1336 +/- 166

< 6

< 7

< 13

< 178 SA-MLK-3G1 (C) 12/01/13 - 12/02/13

< 0.9 1343 +/- 140

< 8

< 13

<214 ANNUAL AVERAGE 1326 +/- 196 IODINE-131 RESULTS ARE CORRECTED FOR DECAY TO STOP DATE OF COLLECTION PERIOD & ANALYZED TO AN LLD OF 1.0 pCi/L (C) CONTROL STATION C-1l

TABLE C-6 CONCENTRATIONS OF GROSS ALPHA AND GROSS BETA EMITTERS AND TRITIUM IN WELL WATER*, 2013 Results in units of pCi/liter +/- 2 sigma STATION ID SA-WWA-3E1 COLLECTION PERIOD START STOP 01/21/13 - 01/21/13 02/19/13 - 02/19/13 03/11/13 - 03/11/13 03/25/13 - 03/25/13 04/22/13 - 04/22/13 05/28/13 - 05/28/13 06/24/13 - 06/24/13 07/15/13 - 07/15/13 08/21/13 - 08/21/13 09/23/13 - 09/23/13 10/28/13 - 10/28/13 11/25/13 - 11/25/13 12/09/13 - 12/09/13 Gr-A

< 2.1

< 1.6

< 2.7

< 1.7

< 2.6

< 2.5

< 1.0

< 1.3

< 1.7

< 0.8

< 1.6

< 1.3 Gr-B 3.3 1.6 2.3 1.9 2.2 2.3 2.2 1.8 + 1.1 1.5 4.0 1.2 2.0 1.6 1.8+/- 0.0 H-3 155 175 191 169 171 176 169 186 167 196 177 191 192 AVERAGE**

MANAGEMENT AUDIT SAMPLE: NOT REQUIRED BY ODCM

- THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES c-12

TABLE C-7 CONCENTRATIONS OF GAMMA EMITTERS IN WELL WATER*, 2013 Results in units of pCi/L +/- 2 sigma, 2013 STATION ID COLLECTION PERIOD GAMMA EMITTERS->

START STOP K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 ZrNB-95 1-131 Cs-134 Cs-137 BaLA140 Ra-226 SA-WWA-3E1 01/21/13 - 01/21/13

< 43

< 3

< 6

< 3

< 6

< 3

< 0.6

< 3

< 5

< 72 02/19/13 - 02/19/13 03/11/13 - 03/11/13 03/25/13 - 03/25/13 04/22/13 - 04/22/13 05/28113 - 05/28/13 06/24/13 - 06/24/13 07/15/13 - 07/15/13 08/21/13 - 08/21/13 09/23/13 - 09/23/13 10/28/13 - 10/28/13 11/25113 -

11/25/13 12/09/13 - 12/09/13

< 54

< 38

< 47

< 44

< 50

< 56

< 80

< 48

< 156

< 60

< 61

< 52

<3

<5

<4

<6

<7

<5

<3

<4

<5

<6

<4

<7

<9

<7

<8

<5

<6

< 10

< 11

< 10

< 12

< 11

< 10

< 12

< 16

< 15

< 14

< 12

<3

<5

<6

<5

<4

<5

<9

<8

<7

<5

<6

< 10

<9

< 11

< 10

<9

< 13

<4

<5

<6

<7

<5

<8 0.6 0.7 0.4 0.6 0.8 0.4 0.6 0.7 3

4 5

5 6

5 4

7

<3

<5

< 5

<6

<5

<7

< 10

<8

< 7

<6

<7

<9

<8

<9

<11

<7

< 14

10 81 130 128 121 179 130 119 158 148 160 149 130

<14

<8

<0.6

<5

< 13

< 8

< 0.8

< 7

< 14

< 8

< 0.6

< 5

< 12

< 6

< 0.8

< 6 AVERAGE

MANAGEMENT AUDIT SAMPLE: NOT REQUIRED BY ODCM

TABLE C-8 CONCENTRATIONS OF GROSS ALPHA AND GROSS BETA EMITTERS AND TRITIUM IN RAW AND TREATED POTABLE WATER (2F3), 2013 Results in units of pCi/L +/- 2 sigma STATION ID COLLECTION PERIOD START STOP RAW 01/01113 - 01/31/13 02/01/13 - 02/28/13 03/01113 - 03/31/13 04/01/13 - 04/30/13 05/01/13 - 05/31/13 06/01/13 - 06/30/13 07/01/13 - 07/31/13 08/01/13 - 08/31/13 09/01/13 - 09/30/13 10/01/13 - 10/31/13 11/01/13 - 11/30/13 12/01/13 - 12/31/13 GR-A

< 0.8

2.7

< 0.9

0.5

1.0

1.9

2.3

2.5

1.4

<1.1

1.6

1.5 GR-B

< 1.8 3.5 +/- 1.7 3.6 +/- 1.2 3.4 +/- 1.0 4.6 +/- 1.1 4.4 + 1.2 3.5 +/- 1.1 6.5 + 1.4 4.9 +/- 1.2 6.1 +/- 1.6 5.6 + 1.1 7.3 + 1.4 H-3

176

166

199

180

186

<184

160

190

179

177

178

162 I

AVERAGE*

4.8 +/- 2.7 TREATED 01/01/13 - 01/31/13 02/01/13 - 02/28/13 03/01/13 - 03/31/13 04/01/13 - 04/30/13 05/01/13 - 05/31/13 06/01/13 - 06/30/13 07/01/13 - 07/31/13 08/01/13-08/31/13 09/01/13-09/30/13 10/01/13-10/31/13 11/01/13-11/30/13 12/01/13-12/31/13

<1.1

1.2

1.3

0.4

1.0

< 2.4

2.6

< 2.2

1.2

< 0.6

< 1.5

1.0

< 1.9 3.2 +/- 1.3 3.1 +/- 1.3 2.9 +/- 1.0 3.7 +/- 1.1 5.8 + 1.3 5.9 +/- 1.3 5.9 +/- 1.2 4.3 ::1.0 5.2 +/- 1.0 5.0 +/- 1.1 5.8 +/- 1.0

176

168

170

180

92

182

160

186

177

< 173

< 177

< 168 AVERAGE*

4.6 +/- 2.4

THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES C-14

TABLE C-9 CONCENTRATIONS OF IODINE-131* AND GAMMA EMITTERS IN RAW AND TREATEDPOTABLE WATER (2F3), 2013 Results in units of pCi/L +/- 2 sigma STATION ID COLLECTION PERIOD START STOP 1-131 SA-PWR-2F3 01/01/13 - 01131/13

< 0.7 SA-PWT-2F3 01/01/13 - 01/31/13

< 0.6 SA-PWR-2F3 02101113 - 02/28113

< 0.8 SA-PWT-2F3 02/01/13 - 02/28/13

< 0.7 SA-PWR-2F3 03/01/13 - 03/31/13

< 0.7 SA-PWT-2F3 03/01/13 - 03/31/13

< 0.8 SA-PWR-2F3 04/01/13 - 04/30/13

< 0.7 SA-PWT-2F3 04/01113 - 04/30/13

< 0.9 SA-PWR-2F3 05/01/13 - 05/31/13

< 0.6 SA-PWT-2F3 05/01/13 - 05/31/13

< 0.4 SA-PWR-2F3 06/01/13 - 06/30/13

< 0.8 SA-PWT-2F3 06/01/13 - 06/30113

< 0.5 SA-PWR-2F3 07/01/13 - 07/31/13

< 0.7 SA-PWT-2F3 07/01/13 - 07/31113

< 0.5 SA-PWR-2F3 08/01/13 - 08/31/13

< 0.7 SA-PWT-2F3 08/01/13 - 08/31/13

< 0.7 SA-PWR-2F3 09/01/13 - 09/30/13

< 0.4 SA-PWT-2F3 09/01/13 - 09/30/13

< 0.4 SA-PWR-2F3 10/01/13 - 10/31/13

< 0.5 SA-PWT-2F3 10/01/13 - 10/31/13

< 0.5 SA-PWR-2F3 11/01/13 - 11/30/13

< 0.8 SA-PWT-2F3 11/01/13 - 11/30/13

< 0.8 SA-PWR-2F3 12/01/13 - 12/31/13

< 0.4 SA-PWT-2F3 12/01/13 - 12/31/13

< 0 AVERAGE K-40

56

< 39

24

< 53

78

30

17

14

< 22

36

107

89

< 97

< 73

< 94

50

< 46

< 27

< 55

< 120

< 49

< 32

< 35

< 75 Mn-54 Co-58 Fe-59

<5

<13

<4

<8

<3

<4

<9

<3

<6

<4

<10

<3

<9

<2

<4

<1

<4

<2

<5

<2

<4

<5

<4

<9

<4

<5

<11

<4

<3

<8

<4

<8

<5

<14

<6

<7

<16

<5

<7

<11

<4

<5

<11

<6

<12

<6

<12

<6

<13

<3

<4

<9

<4

<10

<3

<4

<9

-GAMMA EMITTERS--->

Co-60 Zn-65 ZrNb-95 1-131 Cs-134 Cs-137 BaLa-140 Ra-226

<6

< 10

< 6

< 0.7

< 5

< 6

< 101

<4

<3

<5

<3

<2

<6

<5

<3

<4

<6

<7

<6

<5

<6

<4

<3

<8

<7

<6

<8

<6

<4

<3

<5

<4

< 10

<7

<9

< 10

< 13

< 10

< 13

< 11

<7

<8

<7

<4

<2

<1

<2

<6

<4

<5

<8

<7

<4

<7

<6

<7

<4

<5

<4

<0.6

<4

<0.8

<3

<0.7

<3

<0.7

<4

<0.8

<3

<0.7

<2

<0.9

<1

<0.6

<2

<0.4

<2

<0.8

<5

<0.5

<4

<0.7

<4

<0.5

<5

<0.7

<4

<0.7

<6

<0.4

<5

<0.4

< 5

<0.5

<6

<0.5

<6

<0.8

<5

<0.8

<3

<0.4

<4

<0.4

<3

<4

<5

<4

<2

<1

<2

<5

<4

<5

<6

<5

<6

<7

<6

<4

<6

<89

<6

<80

<6

<93

< 9

< 116

<7

<79

<5

<49

<3

<30

<5

<50

<4

<56

< 10

< 138

<9

<134

<6

< 108

<7

< 137

< 13

< 149

< 13

< 121

< 11

< 117

<*8

< 137

< 14

< 162

< 13

< 186

< 14

< 133

<9

<82

< 11

< 109

< 9

<97 IODINE-131 RESULTS ARE CORRECTED FOR DECAY TO STOP DATE OF COLLECTION PERIOD & ANALYZED TO AN LLD OF 1.0 pCi/L.

TABLE C-10 CONCENTRATIONS OF GAMMA EMITTERS* IN VEGETABLES*, 2013 Results in units of pCi/kg (wet) +/- 2 sigma STATION ID COLLECTION SAMPLE

-GAMMA EMITTERS---. >

PERIOD TYPE Be-7 K-40 1-131 Cs-134 Cs-137 Ra-226 Th-232 SA-FPV-2F9 SA-FPV-2F9 04/27/13 04/28/13 AVERAGE**

05/27/13 AVERAGE**

Asparagus Asparagus

134

156 2338 +/- 380 2054 +/- 359 2196 +/- 402

< 48

46

< 14

20

16

21

356

323

67

78 SA-FPV-3H5 (C)

Asparagus

< 132 1949 +/- 319

< 35

< 15

< 16

< 346

< 61 1949 +/- 0 SA-FPV-15F4 SA-FPV-1G1 (C)

SA-FPV-1G1 (C)

SA-FPV-IG1 (C)

SA-FPV-2F9 SA-FPV-2F9 SA-FPV-2G2 (C)

SA-FPV-2G2 (C)

SA-FPV-3F6 07/24/13 07/24/13 07/24/13 07/24/13 07/24/13 07/24/13 07/24/13 07/24/13 07/24/13 07/24/13 Corn Corn Peppers Tomatoes Corn Tomatoes Corn Peppers Tomatoes Peppers

< 29

< 39

56

< 34

58

< 56

36

< 50

< 51

< 73 2235 2107 2025 1850 1972 2415 2051 1984 1904 2418 80 108 124 93 125 130 84 122 110 162 11 14 20 13 20 19 13 17 18 26 3

4 6

6 4

5 5

7

<3

<4

<6

<4

<7

<6

<4

<5

<9 68 108 146 74 123 121 81 129 127 189

13

18

<24

14

26

25

16

22

< 21

< 30 AVERAGE**

2096 +/- 398 MANAGEMENT AUDIT SAMPLE: NOT REQUIRED BY ODCM

- THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES (C) CONTROL STATION

TABLE C-10 CONCENTRATIONS OF GAMMA EMITTERS* IN VEGETABLES*, 2013 Results in units of pCi/kg (wet) +/- 2 sigma STATION ID COLLECTION SAMPLE

<--GAMMA EMITTERS---->

PERIOD.

TYPE Be-7 K-40 1-131 Cs-134 Cs-137 Ra-226 Th-232 SA-FPV-15F4 08/19/13 Tomatoes

< 120 2083 +/- 306

< 29

< 14

< 310

< 61 SA-FPV-2F9 08/19/13 Peppers

< 152 2157 +/- 356

< 33

< 19

< 424

< 84 SA-FPV-3F6 08/19/13 Tomatoes

< 102 2709 +/- 273

< 23

< 10

< 224

< 43 SA-FPV-15F4 08/20/13 Peppers

< 134 2261 +/- 275

< 28

< 14

< 291

< 54 SA-FPV-2F9 08/20/13 Peaches

< 121 1603 +/- 264

< 30

< 14

< 325

< 60 SA-FPV-3F6 08/20/13 Corn

< 131 1908 +/- 242

< 21

< 12

< 15

< 315

< 50 SA-FPV-3F8 08/20/13 Peaches

< 86 1704 +/- 247

< 22

< 10

< 12

< 295

< 39 SA-FPV-3H5 (C) 08/20/13 Corn

< 174 2061 +/- 337

< 38

< 18

< 20

< 383

< 82 SA-FPV-3H5 (C) 08/20/13 Peppers

< 181 2433 +/- 420

< 41

< 22

< 21

< 547

< 85 SA-FPV-3H5 (C) 08/20/13 Tomatoes

< 103 1269 +/- 236

< 26

< 12

< 15

< 289

< 52 SA-FPV-13E3 08/26113 Corn

< 150 2038 +/- 334

< 41

< 17

< 18

< 348

< 64 AVERAGE**

2021 +/- 795 SA-VGT-14F4 11/01/13 soybeans

< 140 13750 +/- 556

<.60

< 15

< 17

< 229

< 73 SA-FPL-10D1 12/30/13 Cabbage 372 +/- 131 3428 +/- 321

< 57

< 14

< 16

< 290

< 52 SA-FPL-15S1 12130113 Cabbage 228 +/- 81 3697 +/- 201

< 37

< 9 13 +/- 7

< 157

< 39 SA-FPL-16S1 12/30/13 Cabbage 269 +/- 101 3866 +/- 220

< 46

< 10

< 12

< 228

< 39 SA-FPL-1S1 12/30/13 Cabbage 249 +/- 111 3665 +/- 239

< 52

< 11 19 +/- 12 < 269

< 46 SA-FPL-6S1 12/30/13 Cabbage

< 116 3699 +/- 310

< 56

< 11

< 13

< 315

< 47 AVERAGE**

279 +/- 128 3671 +/- 314 16 +/- 9 MANAGEMENT AUDIT SAMPLE: NOT REQUIRED BY ODCM THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES (C) CONTROL STATION

TABLE C-11 CONCENTRATIONS OF GAMMA EMITTERS IN FODDER CROPS*, 2013 Results in units of pCi/kg (wet) +/- 2 sigma STATION ID COLLECTION SAMPLE GAMMA EMITTERS-----. >

DATE TYPE Be-7 K-40 1-131 Cs-134 Cs-137 Ra-226 Th-232 SA-VGT-13E3 SA-VGT-14F4 SA-VGT-2G3 SA-VGT-3G1 (C) 12/20/13 12/20/13 12/18/13 12/18/13 AVERAGE Silage Silage Silage Silage 196 249 249 193

+/- 88

+/- 106

+/- 102

+/- 102 2968 +/- 224 4052 +/- 325 3643 +/- 219 713 +/- 132 2844 +/- 2979

< 55

60

< 52

< 59

<8

<11

<8

10

<13

<9

230

283

216

191

< 38

< 57

< 33

< 26 222 +/- 63 00

MANAGEMENT AUDIT SAMPLE: NOT REQUIRED BY ODCM

TABLE C-12 CONCENTRATIONS OF GAMMA EMITTERS IN SOIL, 2013 Results in units of pCi/kg (dry) +/- 2 sigma STATION ID SA-SOL-10D1 SA-SOL-13E3 SA-SOL-14F4 SA-SOL-16E1 SA-SOL-2F9 SA-SOL-2G3 (C)

SA-SOL-3G1 (C)

SA-SOL-5F1 SA-SOL-6S2 COLLECTION DATE 09/11/13 09/11/13 09/11/13 09/11/13 09/11/13 09/11/13 09/11/13 09/11/13 09/11/13 AVERAGE*

Be-7

710

369

451

< 299

< 597

< 349

< 584

< 358

< 375 K-40 12230 +/- 1317 18510 +/- 1189 12820 +/- 1024 15360 +/- 885 6663 + 922 GAMMA EMITTERS Cs-1 34 Cs-137

< 20 227 +/- 76

< 33

< 38

< 43

< 46

< 29 45 +/- 27

< 46 169 +/- 77 9139 12440 5038 6619 809 1147 787 872

< 37

< 53

< 37

< 38 (I~

78 +/- 34 150 +/- 92 111 +/- 48

< 46 130 +/- 131 Ra-226

< 1534

< 703 2511

+/- 1112 1324

+/- 740 2172

+/- 1153 1898

+/- 913 2595 +/- 1406

< 767

< 1029 2100 +/- 1031 Th-232 1053 +/- 170 361 +/- 92 979 +/- 126 648 +/- 90 644 +/- 128 584 +/- 100 1207 +/- 178 489 +/- 115 350 +/- 115 702 +/- 617 10980 +/- 8925

THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES (C) CONTROL STATION

TABLE C-13 STATION ID SA-GAM-5C1 CONCENTRATIONS OF GAMMA EMITTERS IN BEEF AND GAME*, 2013 Results in units of pCi/kg (wet) +/- 2 sigma COLLECTION SAMPLE TYPE GAMMA EMITTERS-DATE Be-7 1-131 K-40 01/22/13 Muskrat

< 117

< 29 3307 +/- 376 AVERAGE 3307 +/- 0.0 Cs-134,

<14 Cs-1 37

< 17 0

MANAGEMENT AUDIT SAMPLE: NOT REQUIRED BY ODCM

TABLE C-14 CONCENTRATIONS OF GROSS BETA EMITTERS IN SURFACE WATER, 2013 Results in Units of pCi/L +/- 2 sigma COLLECTION PERIOD CONTROL START STOP SA-SWA-1 1A1 SA-SWA-12C1 SA-SWA-16F1 SA-SWA-1F2 SA-SWA-7E1 01108113 - 01108/13 93 +/- 25 118 +/- 34 39 +/- 11 2V +/- 6 60 +/- 24 02/05/13 03/05/13 04/03/13 05/06/13 06/05/13 07/06/13 08/15/13 09/03/13 10/08/13 11/05/13 12/02/13 02/05/13 03/05/13 04/03/13 05/06/13 06/05/13 07/06/13 08/15/13 09/03/13 10/08/13 11/05/13 12/02/13 AVERAGE 35 128 130 78 49 12 83 87 205 208 239

+/- 14

+/- 22

+/- 21

+/- 10

+/- 15

+3

+/-7

+/- 14

+/- 18

+/- 28

+/- 27 17 91 88 67 76 4

32 74 189 264 198

+/- 11

+/- 18

+/- 17

+/-9

+/- 14

+/-2

+/-6

+/- 12

+/- 16

+/- 30

+/- 25 11 25 89 40 49 7

25 58 137 144 173

+/-5

+/-14

+/-6

+/- 10

+/-4

+9

+/- 12

+/- 20

+ 20 10 +/- 3 43 +/- 14 47 +/- 9 34 +/- 5 36 +/- 7 5+/-3 20 +/-3 38 +6 125 +/- 10 119 +/- 15 114 +/- 16 51 +86 66 187 172 103 123 22 81 150 255 257 264

+/- 14

+/- 32

+/- 30

+/- 13

+/- 30

+/-6

+9

+/-122

+/- 21

+/- 34

+ 32 112 +/- 145 102 +/- 157 66 +/- 112 145 +/- 167 C-21

TABLE C-15 CONCENTRATIONS OF TRITIUM IN SURFACE WATER, 2013 Results in Units of pCi/L +/- 2 sigma U

COLLECTION PERIOD START STOP 01/08/13 -

01/08/13 02/05/13 -

02/05/13 03/05/13 -

03/05/13 04/03/13 -

04/03/13 05/06/13-05/06/13 06/05/13 -

06/05/13 07/06/13-07/06/13 08/15/13 -

08115/13 09/03/13 -

09/03/13 10/08/13 -

10/08/13 11/05/13 -

11/05/13 12/02/13-12/02/13 AVERAGE*

CONTROL SA-SWA-1 1A1 SA-SWA-12C1 SA-SWA-16F1 SA-SWA-1F2 SA-SWA-7E1

< 156

< 181

< 184

< 182

< 178

< 173 265 + 120 162 170 190 164 160

< 159

< 181

< 187

< 178

176

< 171

< 165

< 170

< 193

< 163

< 186

< 157

< 188

< 186

< 185

< 177

< 176

< 169

< 164

< 167

< 191

< 163

< 160

< 161

< 189

< 188

< 183

< 178

< 176

< 173

< 166

167

< 192

< 166

< 164

< 156

< 189

< 182

< 177

< 174

< 170

< 168

< 165

< 188

< 160

< 162 265 +/- 0

THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES C-22

TABLE C-16 CONCENTRATIONS OF GAMMA EMITTERS IN SURFACE WATER, 2013 Results in Units of pCi/L +/- 2 Sigma, 2013 STATION ID COLLECTION GAMMA EMITTERS---->

PERIOD K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 ZrNb-95 1-131" Cs-134 Cs-137 BaLa-140 SA-SWA-11A1 01/08/13

< 25

< 4

<10

< 5

< 10

< 4

< 0.7

< 5

< 12 02/05/13 03/05/13 04/03/13 05/06/13 06/05/13 07/06/13 08/15/13 09/03/13 10/08/13 11/05/13 12/02/13

130 81 +/- 31

16 93 +/- 50 109 +/- 62

15

< 43

< 40 114 +/- 63

< 47 104 +/-49

< 10

<2

<4

<6

<2

<5

<4

<5

<7

<4

<11

<2

<4

<6

<2

<4

<3

<6

<7

<4

< 21

<4

<5

< 10

<11

<4

10

10

< 11

< 16

<9

<8

<2

<4

<6

<2

<5

<3

<6

<8

<4

< 18

<4

<3

<8

<9

<4

<8

<7

13

13

<9

< 12

<2

<4

<5

<2

<5

<6

<7

<5

0.6

0.7

0.6

0.8

0.7

0.6

0.6

0.7

0.7

0.7

0.7

< 10

<2

<3

<5

<2

<4

<5

<6

<4

< 12

<2

<3

<6

<2

<5

<4

<6

<8

<4

< 20

<4

<6

10

10

<3

<8

14

12

<11 AVERAGE**

100 +/- 26 w

SA-SWA-12C1 (C) 01/08/13 02/05/13 03/05/13 04/03/13 05/06113 06/05/13 07/06/13 08/15/13 09/03/13 10/08/13 11/05/13 12/02/13

< 37

< 46 63 +/- 30 60 +/- 28

< 43

< 55

14

50

< 47 123 +/- 64 137 +/- 60 137 +/- 44

<5

<2

<4

<6

<1

<5

<4

<5

<3

<4

<6

<2

<5

<6

<2

<7

<6

<5

<4

<9

< 13

<5

12

<15

<4

15

< 12

12

14

<8

<5

<7

<2

<5

<2

<6

<5

<6

<5

<4

<11

< 10

<4

<8

< 14

<3

< 12

<11

<9

<7

<6

<7

<2

<4

<6

<2

<7

<5

<6

<4

0.8

0.6

0.8

0.7

0.6

0.6

0.7

0.7

0.8

0.6

0.7

0.8

< 3.9

< 5.3

< 2.0

1.9

< 4.1

5.2

1.4

< 4.7

< 4.3

< 4.5

< 3.9

2.9

<4

<6

<2

<5

<6

<2

<5

<6

<3

<11

< 13

<5

<6

<13

12

<3

<11

< 14

< 11

<9 AVERAGE**

104 +/- 78 IODINE-131 RESULTS ARE CORRECTED FOR DECAY TO STOP DATE OF COLLECTION & ANALYZED TO AN LLD OF 1.0 pCi/L THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES (C) CONTROL STATION

TABLE C-16 CONCENTRATIONS OF GAMMA EMITTERS IN SURFACE WATER, 2013 Results in Units of pCi/L +/- 2 Sigma, 2013 STATION ID COLLECTION GAMMA EMITTERS PERIOD K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 ZrNb-95 1-131" Cs-134 Cs-137 BaLa-140 SA-SWA-16F1 01/08/13 76 +/- 49

< 6

< 5

< 12

< 5

< 9

< 5

< 0,8

< 5

< 11 02/05/13 03/05/13 04/03/13 05/06/13 06/05/13 07/06/13 08/15/13 09/03/13 10/08/13 11/05/13 12/02/13

< 99 58 +/- 27 50 +/- 30

< 32

< 62

< 15

< 122 101 +/- 53

< 43 134 +/- 77

< 43

<5

<2

<4

<5

<2

<7

<5

<3

<6

<4

<5

<2

<4

<5

<2

<5

<4

<6

<5

< 14

<4

<6

< 10

15

<3

< 14

< 13

<9

< 12

< 13

<5

<2

<4

<7

<1

<7

<5

<4

<5

<4

<6

<9

<2

<4

<2

<6

<5

<4

< 10

<3

<4

<8

< 15

<3

< 11

<8

< 10

<6

< 10

15

<4

<3

<9

<4

< 14

< 11

< 10

12

<7

<5

<2

<4

<5

<2

<7

<5

<7

<5 (1) 1.7 +/- 0.5

< 0.7

< 0.6

< 0.7

< 0.6

< 0.7

< 1.0

< 0.6

< 0.7

< 0.5

< 0.7

<4

<2

<4

<5

<2

<5

<4

<5

<4

<5

<2

<4

<6

<2

<6

<4

<6

<5

<9

<2

<4

<5

<2

<5

<6

<4

< 10

<4

<7

<9

< 14

<3

<11

< 14

<8

< 13

<9

< 13

< 16

<5

< 11

<8

<4

< 13

< 10

< 11

< 10 AVERAGE**

84 +/- 69 1.7 +/- 0.0 IQ,.

SA-SWA-1 F2 411.

01/08/13 02/05/13 03/05/13 04/03/13 05/06/13 06/05/13 07/06/13 08/15/13 09/03/13 10/08/13 11/05/13 12/02/13

< 48

< 83 47 +/- 30 93 +/- 27

< 40

< 30 71 +/- 33

< 55

< 39 149 +/- 62

< 44 104 +/- 54

<5

<9

<2

<4

<2

<6

<4

<5

<4

<5

< 10

<2

<4

<2

<6

<5

<6

<4

< 12

< 21

<5

<9

<7

<4

< 14

< 11

< 12

<9

<6

<8

<2

<4

<5

<2

<6

<5

< 0.7 (1) 1.5

< 0.6

< 0.7

< 0.5

< 0.7

< 1.0

< 0.7

< 0.6

<5

+/-0.5

<7

<2

<3

<4

<2

<6

<4

<5

<4 AVERAGE**

93 +/- 77 IODINE-131 RESULTS ARE CORRECTED FOR DECAY TO STOP DATE OF COLLECTION AND ANALYZED TO AN LLD OF 1.0 pCi/L THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES (C) CONTROL STATION (1) SEE PROGRAM EXCEPTIONS SECTION FOR EXPLANATION 1.5 +/- 0.0

TABLE C-16 CONCENTRATIONS OF GAMMA EMITTERS IN SURFACE WATER, 2013 Results in Units of pCi/L +/- 2 Sigma, 2013 STATION ID COLLECTION

<..----GAMMA EMITTERS--->

PERIOD K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 ZrNb-95 1-131*

Cs-134 Cs-137 BaLa-140 SA-SWA-7E1 01/08/13 84 +/- 55

< 3.5

< 3.9

< 7

< 4

< 7

< 4

< 0.7

< 3.6

< 4.3

< 8 02/05/13 03/05/13 04/03/13 05/06/13 06/05/13 07/06/13 08/15/13 09/03/13 10/08/13 11/05/13 12/02/13

< 36 86 t 27

<34

< 43

< 37

< 20

< 46

50 120 t 67 177 +/- 83 94 +/- 50

< 5.5

< 1.4

< 1.6

<4.1

< 4.9

< 2.2

< 4.3

< 5.6

< 5.1

<6.1

< 3.9

6.2

< 1.5

< 1.9

< 5.2

< 5.0

< 2.3

< 5.7

< 6.3

< 5.6

< 5.5

< 3.7

< 15

<4

<5

< 11

< 12

<5

< 12

< 11

< 14

<9

<6

<2

<4

<6

<2

<4

<6

<5

<4

< 11

<3

<8

< 10

<4

< 11

< 10

<9

<12

<9

<7

<2

<5

<2

<5

<6

<7

<4

< 0.8

< 0.9

< 0.7

< 0.8

< 0.6

< 0.9

< 0.7

0.7

< 0.7

< 5.3

< 1.4

< 1.6

< 3.9

< 4.9

2.0

< 4.4

< 5.2

< 5.5

< 5.6

< 3.5

< 5.8

< 1.7

< 1.8

< 4.3

< 5.5

< 2.3

< 5.6

< 5.2

< 5.3

< 6.3

< 3.9

< 15

<3

<6

< 13

< 11

<4

< 11

< 12

< 14

< 12

< 10 AVERAGE**

112 +/- 78 I'.)K-4r IODINE-131 RESULTS ARE CORRECTED FOR DECAY TO STOP DATE OF COLLECTION AND ANALYZED TO AN LLD OF 1.0 pCi/L THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES (C) CONTROL STATION

TABLE C-17 CONCENTRATIONS OF GAMMA EMITTERS IN EDIBLE FISH, 2013 Results in Units of pCi/kg (wet) +/- 2 sigma STATION ID COLLECTION

-GAMMA EMITTERS--->

PERIOD K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 Cs-1 34 Cs-137 Ra-226 SA-ESF-11A1 05/16/13 3480 +/- 797

< 48

< 66

< 150

< 52

< 124

< 61

< 66

< 1322 09/23/13 3569 +/- 773

< 52

< 57

< 125

< 41

< 94

< 52

< 53

< 1206 AVERAGE 3525 +/- 126 SA-ESF-12C1 (C) 05/16/13 09/24/13 09/25/13 4705 +/- 964 4283 +/- 823 3407 +/- 882

60

52

< 55

< 59

< 53

65

< 82

< 142

< 122

< 48

58

< 46

135

119

< 93

< 44

< 45

< 48

51

< 47

58

< 1010

< 755

< 1140 AVERAGE 4132 +/- 1324 05/16/13 4048 +/- 884

< 49 09/23/13 4755 +/- 1062

< 61 SA-ESF-7E1 I-),

50

63

122

165

< 33

< 72

< 109

117

< 46

63

< 46

< 60

< 1104

< 1423 AVERAGE 4402 +/- 1000 (C) CONTROL STATION

TABLE C-18 CONCENTRATIONS OF GAMMA EMITTERS IN CRABS, 2013 Results in Units of pCi/kg (wet) +/- 2 sigma STATION ID COLLECTION GAMMA EMITTERS--

PERIOD K-40 Mn-54 Co-58 Fe-59 Co-60 Zn-65 Cs-134 Cs-137 Ra-226 SA-ECH-11A1 07/22/13 2599 +/- 1164

< 92

< 96

< 251

< 78

< 176

< 88

< 86

< 1930 08/26/13 4316 +/- 1244

< 70

< 79

< 167

< 68

< 129

< 75

< 77

< 1933 AVERAGE 3458 +/- 2428 SA-ECH-12C1 (C) 07/22/13 08/26/13 2868 +/- 940

< 60 2803 +/- 1069

< 95

< 67

88

171

170

< 53

< 77

< 97

< 155

< 45

80

63

< 77

< 1015

< 1365 AVERAGE 2836 +/- 92 n-)

(C) CONTROL STATION

TABLE C-19 CONCENTRATIONS OF GAMMA EMITTERS IN SEDIMENT, 2013 Results in Units of pCi/kg (dry) +/- 2 Sigma

<-----GAMMA EMITTERS---...>

C) 00 STATION ID SA-ESS-1 WA SA-ESS-12C1 (C)

SA-ESS-15A1 SA-ESS-16A1 SA-ESS-16F1 SA-ESS-6S2 SA-ESS-7E1 COLLECTION PERIOD 06/28/13 11/25/13 AVERAGE*

06/28/13 11/25/13 AVERAGE*

07/08/13 12/16/13 AVERAGE*

06/28/13 11/25/13 AVERAGE*

Be-7

293

713

720

< 1185

< 533

< 593

< 409

< 575

< 1030

< 1175

< 291

< 397

507

< 1063 K-40 3104 +/- 562 10170 +/- 1256 6637 +/- 9993 17430 +/- 1819 16470 +/- 2034 16950 +/- 1358 14080 +/- 1632 9689 +/- 1329 11885 +/- 6210 5742 +/- 873 8501 +/- 1241 7122 +/- 3902 20030 +/- 2340 20940 +/- 2416 20485 +/- 1287 2662 +/- 474 5257 +/- 705 3960 +/- 3670 14680 +/- 1353 18080 +/- 2010 16380

+/- 4808 Cs-134

30

< 79

< 74

< 105

< 61

<54 Cs-137

< 35

67 Ra-226

756

< 1802

81

126

87

< 73

< 1541 3228 3228 2549

< 1258 2549 2898 2669 2784

< 2247

< 1965

+/- 2014

+0

+/- 1699

+/-0

+/- 1062

+/- 1241

+/- 324

40

< 55

< 51

58 Th-232 252 +/- 92 987 +/- 194 620 +/- 1040 1168 +/- 206 869 +/- 258 1019 +/- 422 1014 +/- 226 812 +/- 161 913 +/- 285 701 +/- 202 1094 +/- 182 897 +/- 556 1168 +/- 317 1017 +/- 288 1093 +/- 214 166 +/- 63 347 +/- 100 257 +/- 256 829 +/- 245 1233 +/- 232 1031 +/- 571

< 87

< 94

< 119

< 103

< 27

< 31

< 36

< 578

< 755 2403 +/- 1019 3441 +/- 1914 2922 +/- 1468

< 49

< 89

< 71

< 108

THE AVERAGE AND 2 STANDARD DEVIATION VALUES ARE CALCULATED USING THE POSITIVE VALUES (C) CONTROL STATION

FIGURE 1 GROSS BETA ACTIVITY IN AIR PARTICULATE 1990 THROUGH 2013 1000.0 100.0 C1.

m 10.0 GROSS BETA IN AIR PARTICULATE (1) (2)(3)(4)

(5)

(6) 1973 THROUGH 2013 1ii 1 1 1000 100 10 1976 1979 1982 1985 1988 1991 1994 1997 2000 2003 2006 2009 2012 1.0 1-Weapons Test 1974 2-Weapons Test 1976 3-Weapons Test 1977 4-Weapons Test 1978 5-Weapons Test 1981 6-Chernobyl 1986 I QUARTERLY AVERAGE I

FIGURE 2 IODINE - 131 ACTIVITY IN MILK 1990 THROUGH 2013 20 10 IODINE-131 ACTVTY IN MILK (1) (2) (3)(4) (5)

(6) 1973 THROUGH 2013 I I I I I I 25 20 15 10 5

0

-5 7,1, 1A,',o

,o..

2 1"*

0

-J 0a-0

-10 1

1-Weapons Test 1974 2-Weapons Test 1976 3-Weapons Test 1977 4-Weapons Test 1978 5-Weapons Test 1981 6-Chernobyl 1986 1,QUARTERLY AVERAGE

FIGURE 3 GROSS BETA ACTIVITY IN SURFACE WATER 1990 THROUGH 2013 10000 1000

.J 100 CL 10 10 1QUARTERLY AVERAGE

FIGURE 4 TRITIUM ACTIVITY IN SURFACE WATER 1990 THROUGH 2013 10000.00 TRITIUM ACTIVITY IN SURFACE WATER 1973 Through 2013 10000 1000 100 10 1000.00 Effluent Discharge near time of sampling: 07-07-05 C.,

100.00 1 0.0 0 1-Weapons Test 1974 2-Weapons Test 1976 3-Weapons Test 1977 4-Weapons Test 1978 5-Weapons Test 1981 6-Chernobyl I QUARTERLY AVERAGE]

1986

FIGURE 5 CESIUM-137 & COBALT-60 ACTIVITY IN AQUATIC SEDIMENT 1990 THROUGH 2013 10000 1000 100 10 Data collection started in 1977.

I eli A Iii IAI AI~I~

AF*,I IEIM~I4M orm-mm m AI-%% r

FIGURE 6 CESIUM -137 ACTIVITY IN SOIL 1974 THROUGH 2013 (TRIENNIAL) 800 700 600 500 400 300 200 100 0

1974 1977 1980 1983 1986 1989 1992 1995 1998 2001 2004 2007 2010 2013

APPENDIX D

SUMMARY

OF RESULTS FROM ANALYTICS, ENVIRONMENTAL RESOURCE ASSOCIATES (ERA),

AND DEPARTMENT OF ENERGY (DOE) - MIXED ANALYTE PERFORMANCE EVALUATION PROGRAM (MAPEP)

D-1

Intentionally left blank D-2

ANALYTICS ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING ENVIRONMENTAL SERVICES (PAGE 1 OF 3)

Identification Reported Known Ratio (c)

Month/Year Number Matrix Nuclide Units Value (a)

Value (b)

TBE/Analytics Evaluation (d)

March 2013 E10477 E10478 E10480 E10479 Milk Milk Sr-89 Sr-90 1-131 Ce-141 Cr-51 Cs-1 34 Cs-1 37 Co-58 Mn-54 Fe-59 Zn-65 Co-60 pCi/L 120 99.7 pCi/L 9.21 11.0 pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi pCi pCi pCi pCi pCi pCi pCi pCi 87.1 186 463 201 262 200 215 266 311 384 95.3 264 123 142 112 115 139 163 212 100 187 472 214 266 208 208 252 301 400 95.6 241 109 136 106 106 129 153 204 AP Ce-141 Cr-51 Cs-1 34 Cs-137 Co-58 Mn-54 Fe-59 Zn-65 Co-60 Charcoal 1-131 Water Fe-55 June 2013 E10481 E10564 E10545 E10547 E10546 pCi 90.1 92.6 pCi/L 1840 1890 pCi/L 110 95.0 pCi/L 15.8 17.0 1.20 0.84 0.87 0.99 0.98 0.94 0.98 0.96 1.03 1.06 1.03 0.96 1.00 1.10 1.13 1.04 1.06 1.08 1.08 1.07 1.04 0.97 0.97 1.16 0.93 0.97 0.92 1.01 0.94 0.95 0.93 0.99 1.04 1.01 0.97 1.00 1.07 1.09 1.07 1.06 1.16 1.14 1.24 1.05 0.96 A

Milk Milk Sr-89 Sr-90 1-131 Ce-141 Cr-51 Cs-134 Cs-137 Co-58 Mn-54 Fe-59 Zn-65 Co-60 pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi pCi pCi pCi pCi pCi pCi pCi pCi 92.6 83.1 253 118 143 87.1 171 125 220 169 56.8 168 85.2 101 62.7 125 85.7 169 116 95.5 90.4 250 125 151 94.0 172 120 217 175 56.7 157 78.4 94.6 58.9 108 75.0 136 110 AP Ce-141 Cr-51 Cs-134 Cs-137 Co-58 Mn-54 Fe-59 Zn-65 Co-60 Charcoal 1-131 pCi 86.5 89.7 D-3

ANALYTICS ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING ENVIRONMENTAL SERVICES (PAGE 2 OF 3)

Identification Reported Known Ratio (c)

Month/Year Number Matrix Nuclide Units Value (a)

Value (b)

TBE/Analytics Evaluation (d)

June 2013 E10549 Water Fe-55 pCi/L 1610 1610 pCi/L 63.9 96.0 pCi/L 8.88 13.2 September2013 E10646 E10647 E10672 Milk Milk Sr-89 Sr-90 1-131 Ce-141 Cr-51 Cs-1 34 Cs-1 37 Co-58 Mn-54 Fe-59 Zn-65 Co-60 pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi pCi pCi pCi pCi pCi pCi pCi pCi 93.9 98.3 272 150 125 105 138 125 264 187 208 143 106 97.0 116 98.6 219 166 277 172 131 108 139 130 266 196 223 139 105 86.5 112 105 214 158 AP Ce-141 Cr-51 Cs-1 34 Cs-1 37 Co-58 Mn-54 Fe-59 Zn-65 Co-60 Charcoal 1-131 Water Fe-55 E10648 E10673 pCi 76.3 71.7 pCi/L 1790 1690 pCi/L 97.3 93.8 pCi/L 13.3 12.9 1.00 0.67 0.67 0.96 0.98 0.87 0.95 0.97 0.99 0.96 0.99 0.95 0.93 1.03 1.01 1.12 1.04 0.94 1.02 1.05 1.06 1.06 1.04 1.03 0.93 0.91 1.00 0.91 1.00 1.04 0.99 1.06 1.02 0.96 0.97 1.17 1.08 1.01 0.94 0.98 1.14 0.85 1.00 N (1)

N (1)

A NA (2)

A A

NA (2)

A A

A December2013 E10774 E10775 E10777 Milk Milk Sr-89 Sr-90 1-131 Ce-141 Cr-51 Cs-134 Cs-1 37 Co-58 Mn-54 Fe-59 Zn-65 Co-60 pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi/L pCi pCi pCi pCi pCi pCi pCi pCi pCi 89.7 99.8 297 129 126 116 167 117 757 141 85.1 278 123 102 84.4 132 101 506 118 96.1 110 297 142 126 112 168 110 741 147 88.0 238 114 101 89.9 135 88.3 595 118 AP Ce-141 Cr-51 Cs-1 34 Cs-137 Co-58 Mn-54 Fe-59 Zn-65 Co-60 D-4

ANALYTICS ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING ENVIRONMENTAL SERVICES (PAGE 3 OF 3)

Identification Reported Known Ratio (c)

Month/Year Number Matrix Nuclide Units Value (a)

Value (b)

TBE/Analytics Evaluation (d)

December 2013 E10776 E10778 Charcoal 1-131 Water Fe-55 pCi 84.7 80.5 pCi/L 2010 1910 1.05 1.05 A

A (1)

(2)

(a)

(b)

(c)

(d)

Milk, Sr-89/90 - The failure was due to analyst error. No client samples were affected by this failure. NCR 13-15 The sample was not spiked with Ce-141.

Teledyne Brown Engineering reported result.

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.

Ratio of Teledyne Brown Engineering to Analytics results.

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 < 0. 70 and > 1.30.

D-5

DOE's MIXED ANALYTE PERFORMANCE EVALUATION PROGRAM (MAPEP)

TELEDYNE BROWN ENGINEERING ENVIRONMENTAL SERVICES (PAGE 1 OF 2)

Identification Reported Known Acceptance Month/Year Number Media Nuclide Units Value (a)

Value (b)

Range Evaluation (c)

March 2013 13-MaW28 Water Cs-1 34 Cs-1 37 Co-57 Co-60 H-3 Mn-54 K-40 Sr-90 Zn-65 Water Gr-A Gr-B Bq/L 21.0 24.4 17.1-31.7 Bq/L 0.0446 (1)

Bq/L 28.3 30.9 21.6-40.2 Bq/L 18.2 19.56 13.69 - 25.43 Bq/L 506 507 355 - 659 Bq/L 25.7 27.4 19.2 - 35.6 Bq/L 2.09 (1)

Bq/L 10.5 10.5 7.4-13.7 Bq/L 29.2 30.4 21.3-39.5 A

A A

13-GrW28 13-MaS28 13-RdF28 Bq/L 2.74 2.31 Bq/L 15.6 13.0 0.69 - 3.93 6.5-19.5 Soil Cs-1 34 Cs-1 37 Co-57 Co-60 Mn-54 K-40 Sr-90 Zn-65 13-GrF28 13-RdV28 September 2013 13-MaW29 13-GrW29 AP Cs-134 Cs-137 Co-57 Co-60 Mn-54 Sr-90 Zn-65 AP Gr-A Gr-B Vegetation Cs-1 34 Cs-1 37 Co-57 Co-60 Mn-54 Sr-90 Zn-65 Water Cs-1 34 Cs-1 37 Co-57 Co-60 H-3 Mn-54 K-40 Sr-90 Zn-65 Water Gr-A Gr-B Bq/kg 859 887 621-1153 Bq/kg 633 587 411 -763 Bq/kg 0.256 (1)

Bq/kg 738 691 484-898 Bq/kg 0.671 (1)

Bq/kg 714 625.3 437.7 - 812.9 Bq/kg 442 628 440-816 Bq/kg 1057 995 697-1294 Bq/sample 1.73 1.78 1.25-2.31 Bq/sample 2.73 2.60 1.82 - 3.38 Bq/sample 2.38 2.36 1.65 - 3.07 Bq/sample 0.0302 (1)

Bq/sample 4.36 4.26 2.98 - 5.54 Bq/sample 1.43 1.49 1.04 - 1.94 Bq/sample 3.14 3.13 2.19-4.07 Bq/sample 0.767 1.20 0.36-2.04 Bq/sample 0.871 0.85 0.43-1.28 Bq/sample

-0.197 (1)

Bq/sample 7.39 6.87 4.81 - 8.93 Bq/sample 9.87 8.68 6.08 - 11.28 Bq/sample 6.08 5.85 4.10-7.61 Bq/sample -0.0104 (1)

Bq/sample 1.28 1.64 1.15-2.13 Bq/sample 6.84 6.25 4.38-8.13 Bq/L 29.1 30.0 21.0-39.0 Bq/L 34.5 31.6 22.1-41.1 Bq/L 0.0358 (1)

Bq/L 24.6 23.58 16.51 - 30.65 Bq/L 2.45 (1)

Bq/L 0.0337 (1)

Bq/L 0.193 (1)

Bq/L 9.12 7.22 5.05-9.39 Bq/L 38.1 34.6 24.2 - 45.0 Bq/L 1.13 0.701 0.210 - 1.192 Bq/L 7.61 5.94 2.97 - 8.91 A

A A

A W

A A

A W

A A

W A

A A

D-6

DOE's MIXED ANALYTE PERFORMANCE EVALUATION PROGRAM (MAPEP)

TELEDYNE BROWN ENGINEERING ENVIRONMENTAL SERVICES (PAGE 2 OF 2)

Identification Reported Known Acceptance MonthfYear Number Media Nuclide Units Value (a)

Value (b)

Range Evaluation (c)

September 2013 13-MaS29 13-RdF29 Soil Cs-134 Cs-137 Co-57 Co-60 Mn-54 K-40 Sr-90 Zn-65 Bq/kg Bq/kg Bq/kg Bq/kg Bq/kg Bq/kg Bq/kg Bq/kg Bq/sample Bq/sample Bq/sample Bq/sample Bq/sample Bq/sample Bq/sample 1150 1100 670 502 758 796 664 210

-0.570 2.85 3.30 2.41 3.65 1.40 2.90 1172 820-1524 977 684-1270 (1) 451 316-586 674 472-876 633 443-823 460 322-598 (1)

A A

N (2)

A A

W N (2)

N (2)

A A

W A

13-GrF29 13-RdV29 AP Cs-134 Cs-137 Co-57 Co-60 Mn-54 Sr-90 Zn-65 AP Gr-A Gr-B Vegetation Cs-134 Cs-1 37 Co-57 Co-60 Mn-54 Sr-90 Zn-65 2.7 3.4 2.3 3.5 1.81 2.7 (1) 1.9-3.5 2.4-4.4 1.6 - 3.0 2.5-4.6 1.27 -2.35 1.9-3.5 0.3-1.5 0.82 - 2.45 Bq/sample 0.872 0.9 Bq/sample 1.57 1.63 A

A Bq/sample Bq/sample Bq/sample Bq/sample Bq/sample Bq/sample Bq/sample 5.29 7.48 0.0129 0.0523 8.78 1.63 3.18 5.20 3.64 - 6.76 6.60 4.62 - 8.58 (1)

(1) 7.88 5.52 - 10.24 2.32 1.62-3.02 2.63 1.84 - 3.42 A

A A

W (2)

W (1) False positive test.

(2) Soil, Co-57 & Zn-65 identified by gamma software as not detected, MAPEP evaluated as failing the false positive test. A large concentration of Eu-152 was spiked into the sample, causing interference in the analysis. Gamma software recognized the interference and identified them as not detected. MAPEP does not allow clients to enter non-detect designation. NCR 13-04 Soil, Sr incorrect results were submitted to MAPEP. Should have been 332 bq/kg, which would have passed. NCR 13-04 AP, Cs-134 - MAPEP evaluated the -0.570 as a failed false positive test. No client samples were affected by these failures. NCR 13-04 Vegetation, Sr it appears that the carrier was double spiked into the sample, resulting in the low activity for this sample. NCR 13-04 (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-7

ERA ENVIRONMENTAL RADIOACTIVITY CROSS CHECK PROGRAM TELEDYNE BROWN ENGINEERING ENVIRONMENTAL SERVICES (PAGE 1 OF 1)

Identification Reported Known Acceptance Month/Year Number Media Nuclide Units Value (a) Value (b)

Limits Evaluation (c)

May 2013 RAD-93 MRAD-1 8 Water Sr-89 Sr-90 Ba-1 33 Cs-1 34 Cs-137 Co-60 Zn-65 Gr-A Gr-B 1-131 U-Nat H-3 Filter Gr-A Water Sr-89 Sr-90 Ba-133 Cs-134 Cs-137 Co-60 Zn-65 Gr-A Gr-B 1-131 U-Nat H-3 Filter Gr-A pCi/L 48.3 pCi/L 19.3 pCi/L 81.9 pCi/L 40.9 pCi/L 44.0 pCi/L 61.9 pCi/L 202 pCi/L 34.2 pCi/L 18.0 pCi/L 23.8 pCi/L 60.4 pCi/L 3970 41.3 31.6-48.4 23.9 17.2 - 28.0 82.1 69.0-90.3 42.8 34.2-47.1 41.7 37.0-48.8 65.9 59.3 - 75.0 189 170-222 40.8 21.1-51.9 21.6 13.0-29.7 23.8 19.7-28.3 61.2 49.8 -67.9 4050 3450-4460 pCi/filter Lost during processing A

A A

November 2013 RAD-95 pCi/L 25.5 pCi/L 14.3 pCi/L 57.2 pCi/L 83.3 pCi/L 201 pCi/L 104 pCi/L 361 pCi/L 29.5 pCi/L 30.1 pCi/L 23.1 pCi/L 5.53 pCi/L 17650 pCi/filter 33.0 21.9 18.1 54.2 86.7 206 102 333 42.8 32.2 23.6 6.24 17700 14.4 - 28.2 12.8-21.5 44.7 - 59.9 71.1 -95.4 185-228 91.8-114 300 - 389 22.2 - 54.3 20.8 - 39.9 19.6-28.0 4.70 - 7.44 15500 - 19500 MRAD-19 83.0 27.8-129 (a) Teledyne Brown Engineering reported result.

(b) The ERA 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) 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-8

LR-N14-0079, Annual Radiological Environmental Operating Report

Contents

Text

Subject:

Enclosure:

SUMMARY

SUMMARY

Navigation menu

LR-N14-0079, Annual Radiological Environmental Operating Report

Text

Subject:

Enclosure:

SUMMARY

SUMMARY

Navigation menu

Search