Text

Annual Radioactive Effluent Release Report
	ML14127A085
Person / Time
Site:	Indian Point
Issue date:	04/28/2014
From:	Robert Walpole; Entergy Nuclear Northeast
To:	; Document Control Desk, NRC/FSME, Office of Nuclear Reactor Regulation
References
	NL-14-039
	Download: ML14127A085 (66)
	v • d • e

SEntergy Enterav Nuclear Northeast Indian Point Energy Center 450 Broadway, GSB P.O. Box 249 Buchanan, N.Y. 10511-0249 Tel (914) 254-6710 Robert Walpole Licensing Manager NL-14-039 April 28, 2014 U.S. Nuclear Regulatory Commission ATTN: Document Control Desk 11555 Rockville Pike Rockville, MD 20852

SUBJECT:

2013 Annual Radioactive Effluent Release Report Indian Point Unit Nos. 1, 2 and 3 Docket Nos. 50-03, 50-247, 50-286 License Nos. DPR-5, DPR-26, DPR-64

Dear Sir or Madam:

to this letter provides Entergy Nuclear Operations, Inc.'s Annual Radioactive Effluent Release Report for 2013. This report is submitted in accordance with Technical Specification 5.6.3 and Regulatory Guide 1.21.

There are no new commitments contained in this letter. If you have any questions or require additional information, please contact me.

Sincerely, RW/ai cc: next page pIUY.

NL-14-039 Docket Nos. 50-03, 50-247, 50-286 Page 2 of 2

Enclosure:

1. Radioactive Effluent Release Report: 2013 cc:

Mr. William Dean, Regional Administrator, NRC Region 1 Mr. Douglas Pickett, Senior Project Manager, NRC NRR DORL IPEC NRC Resident Inspector's Office Mr. Stephen Giebel, IPEC NRC Unit 1 Project Manager Mr. John B. Rhodes, President and CEO, NYSERDA (w/o enclosure)

Ms. Bridget Frymire, New York State Department of Public Service (w/o enclosure)

Mr. Timothy Rice, Bureau of Hazardous Waste & Radiation Mgmt, NYSDEC Mr. Robert Snyder, NYS Department of Health Mr. Chuck Nieder, NYS Department of Environmental Conservation Mr. Jason Martinez, American Nuclear Insurers Chief, Compliance Section, New York State DEC, Division of Water Regional Water Engineer, New York State DEC

ENCLOSURE 1 TO NL-14-039 Radioactive Effluent Release Report: 2013 ENTERGY NUCLEAR OPERATIONS, INC.

INDIAN POINT UNIT 1, 2, and 3 NUCLEAR POWER PLANTS DOCKET Nos. 50-03, 50-247, and 50-286

Docket No. 50-3, 50-247, & 50-286 Page 1 of 63 Radioactive Effluent Release Report: 2013 Facility Indian Point Energy Center (Indian Point Units 1, 2, and 3)

Licensee Enterqy Nuclear Operations, Inc (Entergy)

This information is provided in accordance with the requirements of Regulatory Guide 1.21.

The numbered sections of this report reference corresponding sections of the subject Guide, pages 10 to 12.

This report includes effluent information from Indian Point Units 1, 2, and 3. Units 1 and 2 share effluent processing equipment and Technical Specifications.

In this site report, releases from Unit 1 are included with Unit 2, while Unit 3 releases are calculated and shown separately.

A.

Supplemental Information

1.

Regulatory Limits Indian Point Energy Center is subject to limits on radioactive waste releases that are set forth in the Offsite Dose Calculation Manual (ODCM), Parts I and II, as defined in the Technical Specifications. ODCM Part I, also known as the Radiological Effluent Controls (or RECS) contains the specific requirements and controls, while ODCM Part II (calculational methodologies) contains the details necessary to perform offsite dose calculations from the sampling and monitoring outlined in the RECS.

2.

Maximum Permissible Concentration a)

Airborne Releases Maximum concentrations and compliance with 10CFR20 release rate limits are controlled by the application of Radiation Monitor setpoints, preliminary grab sampling, and conservative procedural guidance for batch and continuous releases.

These measures, in conjunction with plant design, preclude approaching release rate limits, per the ODCM.

b)

Liquid Effluents Proximity to release rate and total release limits is controlled through the application of a calculated Allowed Diluted Concentration (ADC) and ALARA guidance with regard to dilution flow and maximum tank concentration. The ADC is used to determine a Radiation Monitor setpoint associated with an estimated amount of non-gamma activity (H-3, Ni-63, Fe-55, Sr-89/90 etc), as well as the measured gamma activity. ADC is defined in the station ODCM as a means of assuring compliance with the release rate limits of 10CFR20, as defined by the application of ten times the Effluent Concentrations of the new 10CFR20.

Liquid effluents are further controlled by the application of proceduralized ALARA limits such as a MINIMUM dilution flow of 100,000 gpm required for batch discharges, a maximum gamma concentration of 5E-5 uCi/mI (without gas) for routine effluents, and procedural guidance for optimizing decay and treatment of liquid waste.

3.

Average Energv This information is no longer used. It is available on site.

Docket No. 50-3, 50-247, & 50-286 Page 2 of 63

4.

Measurements and Approximations of Total Radioactivity a)

Fission and Activation Gases Analyses of effluent gases are performed in compliance with the requirements of the RECS (ODCM Part I). In the case of isolated tanks (batch releases), the total activity discharged is based on an isotopic analysis of each batch with the volume of gas in the batch corrected to standard temperature and pressure.

Vapor containment purge and pressure relief (vent) discharges, which routinely total less than 150 hour0.00174 days 0.0417 hours 2.480159e-4 weeks 5.7075e-5 months s/quarter in duration, have been treated as batch releases.

However, both types of releases from the Vapor Containment are performed randomly with regard to time of day and duration (release periods were not dependent solely on time of day or atmospheric condition). Therefore, determination of doses due to Vapor Containment releases includes the use of annual average dispersion data, as defined in NUREG 0133, Section 3.3.

At least one complete isotopic concentration analysis of containment air is performed monthly and compared to a process monitors reading. Pressure reliefs are quantified by scaling subsequent releases with the monitor's reading, applying the mixture from the grab sample. In this fashion, the base grab sample defines the mixture and the activity released. The monitor scales the release up or down and provides continuous indication of potential leaks.

Isotopic analyses for each vapor containment purge are taken prior to and during the purge. This information is combined with the volume of air in each discharge to calculate the quantity of activity released from these discharges.

The continuous building discharges are based on weekly samples of ventilation air analyzed for isotopic content. This information is combined with total air volume discharged and the process radiation monitor readings to determine the quantity of activity from continuous discharges.

b/c) lodines and Particulates Iodine and particulate releases are quantified by collecting a continuous sample of ventilation air on a Triethylenediamine (TEDA) impregnated, activated charcoal cartridge and a glass-fiber filter paper. These samples are changed weekly as required in the RECS. The concentration of isotopes found by analysis of these samples is combined with the volume of air discharged during the sampling period to calculate the quantity of activity discharged.

If no 1-131 is identified in weekly vent samples, "-" is entered in Table 1A. A typical Minimum Detectable Activity (MDA) for weekly 1-131 analyses is 1.OE-13 uCi/cc, which is 100 times lower than ODCM requirements.

If 1-131 is identified in any routine weekly sample, it is added to the table and other iodine isotopic concentrations (1-133, 1-135) are then determined on a 24-hour sample at least once per month.

The concentration of each isotope is analytically determined by ratioing the activities with weekly media for 1-131. This activity is combined with the volume of air discharged during the sampling period to calculate the quantity of activity discharged. A compositing method of analyzing for gross alpha, Sr-89, and Sr-90 is used per the station ODCMs. An absence of any positive activity is identified as "-".

Docket No. 50-3, 50-247, & 50-286 Page 3 of 63 d)

Carbon-14 C-14 release quantification details are discussed in Section E.

e)

Liquid Effluents A sample of each batch discharge is taken and an isotopic analysis is performed in compliance with requirements specified in the ODCM. Proportional composite samples of continuous discharges are taken and analyzed per the ODCM, as well. Isotopic concentration data are combined with the information on volume discharged to determine the amount of each isotope discharged.

A compositing method of analyzing for non-gamma emitters is used per the station ODCM (Gross Alpha, Sr-89, Sr-90, Fe-55 and Ni-63). When there has been no positive activity, "-" is entered.

Liquid Effluent volumes of waste released on Table 2A are differentiated between processed fluids (routine liquid waste and Unit l's North Curtain Drain), and water discharged through monitored pathways identified in the ODCM, but NOT processed (SG Blowdown and Unit l's Sphere Foundation Drain Sump). The unprocessed water may still contain trace levels of contamination (generally only tritium) and as such, is identified as liquid waste. Curie and dose data from unprocessed fluid is included in the following tables, along with all other liquid effluent, continuous or batch, processed or not. Processed and unprocessed water is differentiated only to prevent confusion with regard to measures undertaken to convert liquid to solid waste (resin cleanup). Therefore, volumes of processed and unprocessed liquid waste are reported separately on Table 2A.

Docket No. 50-3, 50-247, & 50-286 Page 4 of 63

5.

Batch Releases Airborne:

Unit I and 2 Airborne Releases Qtr 1 Qtr 2 Qtr 3 Qtr 4 2013 Number of Batch Releases 73 63 68 65 269 Total Time Period (min) 3830 3210 3290 3790 14100 Maximum Time Period (min) 89 89 107 121 121 Average Time Period (min) 52.5 51.0 48.4 58.3 52.5 Minimum Time Period (min) 25 1

2 2

1 Unit 3 Airborne Releases Qtr 1 Qtr 2 Qtr 3 Qtr 4 2013 Number of Batch Releases 37 29 19 16 101 Total Time Period (min) 3210 2440 1980 1910 9550 Maximum Time Period (min) 316 204 241 203 316 Average Time Period (min) 86.9 84.2 104 119 94.5 Minimum Time Period (min) 4 1

1 4

1 Liquid:

Unit I and 2 Liquid Releases Qtr I Qtr 2 Qtr 3 Qtr 4 2013 Number of Batch Releases 13 8

12 22 55 Total Time Period (min) 1410 822 1200 2310 5750 Maximum Time Period (min) 178 118 119 125 178 Average Time Period (min) 108 103 100 105 105 Minimum Time Period (min) 90 87 77 87 77 Unit 3 Liquid Releases Qtr 1 Qtr 2 Qtr 3 Qtr 4 2013 Number of Batch Releases 63 35 9

19 126 Total Time Period (min) 7000 3900 944 2060 13900 Maximum Time Period (min) 223 122 116 114 223 Average Time Period (min) 111 112 105 109 110 Minimum Time Period (min) 68 103 96 102 68 Average Stream Flow:

Regulatory Guide 1.21 includes a section to report average stream flows. This data, for some plants, is used to determine dilution volume. However, at IPEC, the Hudson River stream flow is not applied to dilution calculations, in favor of the more conservative method of using only the dilution in the discharge canal, running north to south, parallel to the river, and servicing the plant.

This conservative dilution volume is determined quarterly, applied for liquid offsite dose calculations (and all other determinations of diluted effluent), and reported on Tables 2A, in Section B of this report.

Hudson River flow information remains available, however, from the Department of the Interior, United States Geological Survey (USGS), or from web sites such as:

http://nywater.usqs,qov/proiects/djaler plots/Hudson R at Poughkeepsie Freshwater Discharqe.htm

Docket No. 50-3, 50-247, & 50-286 Page 5 of 63

6. Abnormal Releases a) Liqui General Groundwater IPEC's groundwater quantification model involves a verification/calibration such that the annual release to the environment remains a function of annual precipitation and source term. The 2013 effluent dose was similar to that of 2012.

The offsite dose associated with the groundwater pathway remains small (<0.01% of the NRC's annual limit), with routine liquid effluent contributing <0.1% of the annual limit.

Groundwater and storm water effluent flow rates and source term data are further described in Section H of this report. A breakdown of the total dose from the groundwater and storm water pathways is provided in Section E of this report (Radiological Impact on Man).

b) Airborne None

7.

ODCM Reportinq Requirements ODCM Part I requires reporting of various conditions during the year. These include effluent monitoring equipment out of service for periods exceeding 30 consecutive days, notification of any changes in the land use census, changes in the Radiological Environmental Monitoring Program (REMP), any time total curie content limitations in outdoor tanks is exceeded, or any other changes in the ODCM or Process Control Program (PCP).

During this reporting period, the following ODCM required effluent monitoring equipment was out of service (OOS) for periods greater than 30 consecutive days:

Effected Instrument Interval Details Unit 3 June 24 Condenser to Troubleshooting revealed a faulty detector.

The detector was Off-gas Aug 30 replaced and calibrated. The long outage was due to a complicated

Monitor, trouble shooting plan and emergent plant issues that received higher R-1 5 66 days priority.

Unit 3 July 16 Admin Bldg to Rate-meter failed and needed to be replaced. The repair delayed Vent Oct 4 due to obsolete parts. Original parts that were procured also failed.

Monitor, Both rate-meter drawers needed to be sent to vendor for R-46 79 days refurbishment.

Unitc2 S/G Eight pinhole leaks were discovered on the Unit 2 Radiation

& Service Sep 11 Water to Monitoring System piping in the Service Water pipe chase. Affected Dec 31 piping was isolated for repair. Since the piping was isolated, RMs 49, Monitors 46 and 53 were declared non-functional.

Initial piping repairs were R-49, R-46, 79 days completed in March during the 2014 refuel outage; additional repairs

& R-53 were noted and are still underway.

Docket No. 50-3, 50-247, & 50-286 Page 6 of 63 Unit 1 Sphere Oct 7 Foundation to Although RM was declared OOS, this pathway was diverted to the Drain Nov 22 North Curtain Drain. Therefore, this is not a radioactive effluent issue

Monitor, 45 days since this pathway was not used during the OOS time.

R-62 Unit 2 Oct 18 The vendor was brought in to repair the instrumentation.

Several Condenser to attempts to repair this instrument were unsuccessful. The entire Off-gas Dec 31 monitor detection circuit was replaced, including the power supplies.

Monitor, The detector was replaced and recalibrated. The long outage was R-45 73 days due the difficulty of diagnosis and repair and the fact that the failure I_ _

Iappeared to be intermittent.

Other Reporting Criteria:

Tank Curie Limits During this reporting period, no tank curie limits in outdoor tanks were exceeded.

Land Use Census During this reporting period, there were no changes to the Land Use Census.

PCP changes:

The Process Control Program document is a fleet procedure for Entergy.

An administrative update to this procedure was completed in 2013. See details in Section G.

ODCM changes:

During this reporting period, there were no changes to the ODCM.

Docket No. 50-3, 50-247, & 50-286 Page 7 of 63 Indian Point Energy Center (Units 1, 2, and 3)

RADIOACTIVE EFFLUENT RELEASE REPORT B. GASEOUS EFFLUENTS 2013

Docket No. 50-3, 50-247, & 50-286 Page 8 of 63 TABLE 1A INDIAN POINT 1 and 2 RADIOACTIVE EFFLUENT REPORT (Jan -

Dec 2013)

GASEOUS EFFLUENTS SUMMATION OF ALL RELEASES

.A. Fission & Activation Gases)

Units Qtr I Qtr 2 Year

Est. Total Qtr 3 Qtr4 2013

%Error

1. Total Release Ci 1.78E-01 3.98E-02 1.67E-01 9.73E-02 4.82E-01

+ 25

2. Average release rate uCi/sec 2.29E-02 5.06E-03 2.10E-02 1.22E-02 1.53E-02 B. lodines

1. Total Iodine-131 Ci

.0OOE+00

+/-25

2. Average release rate uCi/sec 0.OOE+00

.C. Particulates

1. Total Release, with Ci OOE+0O

+/- 25 half-life > 8 days

2. Average release rate uCi/sec 0.OOE+00

3. Gross Alpha Ci O.OOE+00

+/- 25

D. Tritium

1. Total release Ci 1.97E+00 5.05E+00 3.31E+00 2.70E+00 1.30E+01

+25

2. Average release rate uCi/sec 2.53E-01 6.42E-01 4.16E-01 3.40E-01 4.13E-01 E. Carbon-14

1. Total release Ci 2.75E+00 2.75E+00 2.75E+00 2.75E+00 1.10E+01

2. Average release rate uCi/sec 3.54E-01 3.50E-01 3.46E-01 3.46E-01 3.49E-01

- Indicates < MDA Qtr 1 Qtr 2

Qtr3 Qtr 4 2013

.20!3..

Docket No. 50-3, 50-247, & 50-286 Page 9 of 63 TABLE IC INDIAN POINT 1 and 2 CONTINUOUS GASEOUS EFFLUENTS RADIOACTIVE EFFLUENT REPORT (Jan -

Dec 2013)

Nuclides Released

1) Fission Gases Units Qtr I Year Qtr 2 Qtr 3 Qtr 4 2013 I Xe-133 I Ci I

I I

I I O.OOE+00 I Total for Period Ci O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 0.00E+00

......... i.......

2) lodines 1-131 Ci 0,0E+00 1-133 Ci O.OOE+00 1-135 Ci O.OOE+00 Total for Period Ci I 0.00E+09 0,00E+00 0.OOE+00 0.OOE+00

... ~ ~.

i......

3) Particulates Co-58 Ci 0.00E+O0 Ci O.OOE+O0 o.OOE+O0 O.OOE+O0 O.OOE+O0 O.OOE+O0 Indicates < MDA i..............

"i~~~~~~~~

~~~~

i......................

'i..............................................

7........

r............................. *........................,.................................... >.................

Docket No. 50-3, 50-247, & 50-286 Page 10 of 63 TABLE iC INDIAN POINT 1 and 2 BATCH GASEOUS EFFLUENTS RADIOACTIVE EFFLUENT REPORT (Jan -

Dec 2013)

Nuclides Released

1) Fission Gases Year Qtr 4 2013 Units Qtr 1 i

Qtr 2 Qtr 3 Ar-41 Ci 3.40E-02 2.75E-02 6.13E-02 6.34E-02 1.86E-01 Kr-85 Ci 0.OOE+00 Kr-85m Ci 3.32E-06 4.23E-04 2.19E-04 6.45E-04 Kr-87 Ci 2.74E-06 2.98E-04 1.83E-04 4.84E-04 Kr-88 Ci 5.95E-06 7.73E-04 3.77E-04 1.16E-03 Xe-131m Ci 2.49E-05 2.49E-05 Xe-133 Ci 1.40E-01 1.22E-02 9.22E-02 2.91E-02 2.74E-01 Xe-1 33m Ci 7.88E-06 7.88E-06 Xe-135 Ci 3.83E-03 5.13E-05 1.09E-02 3.53E-03 1.83E-02 Xe-135m Ci 6.51E-06 6.77E-04 4.02E-04 1.09E-03 Xe-1 38 Ci 1.49E-06

1.

17E-04

1. 18E-04 Total for Period Ci 1.78E-01 3.98E-02 1.67E-01 9.73E-02 4.82E-01

2) lodines Not Applicable for Batch Particulates Not Applicable for Batch 3)

Releases R e s............

Releases S

indicates <MDA

Docket No. 50-3, 50-247, & 50-286 Page 11 of 63 TABLE 1A INDIAN POINT 3 RADIOACTIVE EFFLUENT REPORT (Jan -

Dec 2013)

GASEOUS EFFLUENTS -

SUMMATION OF ALL RELEASES

A. Fission & Activation Gasesý Units Qtr I Qtr 2 Year Qtr 3 Qtr 4 2013 Est. Total

% Error

1. Total Release Ci 2.99E-01 2.11E-02 1.70E-02 1.45E-02 3.52E-01

+ 25

2. Average release rate uCi/sec 3.85E-02 2.68E-03 2.14E-03 1.82E-03 1.11E-02

'B. lodines

1. Total Iodine-131 Ci 0.OOE+00

+ 25

2. Average release rate uCi/sec 0.00E+00 C. Particulates

1. Total Release, with Ci 00E+00

+/- 25 half-life > 8 days

2. Amarage release rate uCi/sec 0.OOE+00

3. Gross Alpha Ci 0.OOE+00

+/- 25 iD. Tritium

1. Total release Ci 3.55E+00 3.29E+00 3.28E+00 3.15E+00 1.33E+01

2. Average release rate uCi/sec 4.57E-01 4.18E-01 4.13E-01 3.96E-01 4.21E-01 iE. Carbon-14

1. Total release Ci 2.50E+00 2.50E+00 2.50E+00 2.50E+00 1.OOE+01

2. Average release rate uCi/sec 3.22E-01 3.18E-01 3.15E-01 3.15E-01 3.17E-01

- Indicates < MDA Qtrl1 Qtr 2 Qtr 3 Qtr 4 2013

Docket No. 50-3, 50-247, & 50-286 Page 12 of 63 TABLE IC INDIAN POINT 3 -

CONTINUOUS GASEOUS EFFLUENTS RADIOACTIVE EFFLUENT REPORT (Jan -

Dec 2013)

.....{............... 1.......

......d..........

Released........

1) Fission Gases A r-41 Qtr 2 Qtr 3 Qtr I Year 2013 Units Qtr 4 Ci 0.OOE+00 tXe-1 33 j

Ci O.OOE+00 Ae-1 35 Ci 0.OOE+00 F -

To a

fo Pe io

________.__1E

_0 Totl-orPe5 o

Ci 0.O+00OE0

.O+00OE0

.OOE+00 r Total for Period Ci 0.OOE+00 0.OOE+00 0.OOE+O00 0.E+00 0.OOE+00 4.

3, Particulates Total for Period II J-indicates < MDA

.~

C,i O.OOE+00 I o.OOE+00 I o.OOE+00 I o.OOE+00 I o.ooE+oo I...........

Docket No. 50-3, 50-247, & 50-286 Page 13 of 63 TABLE IC INDIAN POINT 3 BATCH GASEOUS EFFLUENTS RADIOACTIVE EFFLUENT REPORT (Jan -

Dec 2013)

Nuclides R

1) Fissio eleased V*2 r n Gases Units Qtr I Qtr 2 Qtr3 Qtr4 2013 Ar-41 Ci 1.12E-01 1.11E-02 1.34E-02 1.19E-02 1.48E-01 Kr-85 Ci O.OOE+00 Kr-85m Ci O.OOE+00 Kr-87 Ci 0.OOE+00 Kr-88 Ci 0.OOE+00 Xe-131m Ci 1.16E-04 1.16E-04 Xe-133 Ci 1.85E-01 8.95E-03 3.56E-03 2.56E-03 2.OOE-01 Xe-133m Ci 9.83E-04 9.83E-04 Xe-135 Ci 1.12E-03 9.90E-04 2.11E-03 Xi--13 5m Ci 0.00O Total for Period Ci 2.99E-01 2.10E-02 1.70E-02 1.45E-02 3.52

2) Iodines Not Applicable for Batch Release

.. T.

1I

3) Particulates Not Applicable for Batch Release

ýS Indicates< MDA E+00 E-01

Docket No. 50-3, 50-247, & 50-286 Page 14 of 63 Indian Point Energy Center (Units 1, 2, and 3)

RADIOACTIVE EFFLUENT REPORT C. LIQUID EFFLUENTS 2013

Docket No. 50-3, 50-247, & 50-286 Page 15 of 63 TABLE 2A INDIAN POINT 1 and 2 RADIOACTIVE EFFLUENT REPORT (Jan -

Dec 2013)

LIQUID EFFLUENTS -

SUMMATION OF ALL RELEASES

ýA. Fission & Activation ProductsYa st oa A.Fission&Actiation Produc Units Qtr I Qtr 2 Qtr 3 Qtr 4 2013

% Error

1. Total Release (not including Ci 2.15E-03 8.35E-03 9.57E-03 3.20E-02 5.21 E-02

+ 25 Tritium, Gr Alpha, & Gases)_

2. Average Diluted Conc uCi/mI 4.611E-12 1.133E-11 1.11E-11 4.311E-11 1.85E-11 B. Tritium

1. Total Release Ci 3.25E+02 1.13E+02 3.63E+02 5.10E+02 1.31E+03

+/-25

2. Average Diluted Conc uCi/ml 6.97E-07 1.53E-07 4.19E-07 6.86E-07 4.66E-07

ýC. Dissolved & Entrained Gasesý

1. Total Release Ci 0.OOE+00 J 25

2. AverageDiluted Conc uCi/ml 0.OOE+00

.......~~~ ~~...............~.

,...,.,...~

.D. Gross Alpha

1. Total Release Ci I

.E+00

,E. Volume of Waste Released

1. Processed Waste (LW&NCD) liters 2.27E+06 2.42E+06 1.66E+06 4.72E+06 1.11E+07

+/-10

2. Unprocessed (SGBD, SFDS, UlFD) liters 4.21E+07 4.44E+07 7.34E+07 7.43E+07 2.34E+08

+/- 10 F. Volume of Dilution Water

]liters I4.66E+1117.37E+11 8.66E+11 7.43E+11 12.81E+121

+/-10 Indicates < MDA

Docket No. 50-3, 50-247, & 50-286 Page 16 of 63 TABLE 2B INDIAN POINT 1 and 2 LIQUID RADIOACTIVE EFFLUENT REPORT (Jan -

Dec 2013)

CONTINUOUS RADIOACTIVE EFFLUENT Nuclides Released Year Qtr 4 2013 Units Qtr I Qtr 2 Qtr 3 Cs-1 37 Ci 1.12E-03 4.83E-03 4.41E-03 2.03E-02 3.07E-02 M i-63 Ci 0.OOE+00 Sr-89 Ci 0.OOE+00 Sr-90 Ci 1.70E-04 1.46E-04 7.47E-05 1.18E-04 5.09E-04 Total for Period Ci 1.29E-03 4.98E-03 4.48E-03 2.04E-02 3.12E-02 H-3.(onl.)...22-113E0 j -3nony*

I Ci 1.22E-01 [1.31E-01 7.32E-02

.41-01 4.67E-01I Indicates < MDA r

J -...

I-

.. i...

TABLE 2B INDIAN POINT 1 and 2 LIQUID RADIOACTIVE EFFLUENT REPORT (Jan -

Dec 2013)

Docket No. 50-3, 50-247, & 50-286 Page 17 of 63 BATCH RADIOACTIVE EFFLUENT Nuclides Released Year 2013 Units Qtr 1 Qtr 2 Qtr 3 Qtr 4

- IAg-110m Ci 9.90E-04 4.79E-04 3.52E-04 1.82E-03 Co-58 Ci 2.OOE-05 6.03E-04 4.64E-04 1.09E-03 Co-60 Ci 1.71E-05 3.35E-04 6.77E-05 1.21E-04 5.411E-04 Fe-55 Ci 5.28E-04 3.42E-04 8.70E-04 Ni-63 Ci 1.18E-03 8.94E-03 1.01E-02 Sb-125 Ci 8.43E-04 1.40E-03 2.42E-03 1.74E-03 6.40E-03 I Total for Period

._[

Ci 8.60E-04 3.27E-03 5.09E-03 1.16E-02 j2.08E-02 Dissolved & Entrained Gas Kr-85 Ci O.0OE+00

( To-t133 Ci O 0.00E+00

_Tjotal for Period Ci 0.00E+00 0.00E÷00 0.00E+00 0.00E+00 0.00E+00 Indicates < MDA J.....

1~.

Docket No. 50-3, 50-247, & 50-286 Page 18 of 63 TABLE 2A INDIAN POINT 3 RADIOACTIVE EFFLUENT REPORT (Jan -

Dec 2013)

LIQUID EFFLUENTS -

SUMMATION OF ALL RELEASES

,A, Fission & Activation Products&

1. Total Release (not including Tritium, Gr Alpha, & Gases)

2. Average Diluted Conc Units Qtrl Qtr2 Qtr3 Ci 1.07E-02 7.88E-03 3.07E-03 uCi/ml 2.30E-11 1.07E-11 3.55E-12 Qtr 4 2.48E-03 3.34E-1 2 Year 2013 2.41 E-02 8.58E-1 2 Est. Total

% Error 1 25

'1. Tritium

1. Total Release Ci 5.20E+02 5.09E+01 7.95E+00 1.56E+02 7.35E+02 1 25

2. Average Diluted Conc uCi/ml 1.12E-06 6.91E-08 9.18E-09 2.1OE-07 2.61E-07

.. ~ ~ ~ ~ ~

~

'C. Dissolved & Entrained Gases,

1. Total Release Ci 2.66E-03 2.40E-05 3.69E-05 2.72E-03

+/- 25

2. AverageDiluted Conc uCi/ml 5.71E-12 3.26E-14 0.OOE+00 4.97E-14 9.68E-13

'D. Gross Alpha

11. TotalRelease Ci [

2

]

[0"00 0

E. Volume of Waste Released

1. Processed Fluids (Mbn Tanks) liters 1.57E+06 9.12E+05 2.03E+05 4.89E+05 3.17E+06

+/- 10

2. Unprocessed Fluids (SGs) liters 4.80E+06 6.86E+06 2.36E+06 1.64E+06 1.57E+07

+/- 10

[. Volume of Dilution Water liters 4.66E+11]7.37E+11 (8.66E+11 7.43E+11 2.81E+12J 0 10 I

indicates < MDA

Docket No. 50-3, 50-247, & 50-286 Page 19 of 63 TABLE 2B INDIAN POINT 3 LIQUID RADIOACTIVE EFFLUENT REPORT (Jan -

Dec 2013)

BATCH and CONTINUOUS RADIOACTIVE LIQUID EFFLUENT Batch Fission/Activation Products Units Qtr I Qtr 2 Qtr 3 Qtr 4 2013 Co-58 Ci 6.58E-04 4.08E-03 9.1OE-04 3.59E-04 6.01E-03 Co-60 Ci 1.70E-03 2.58E-04 7.85E-05 8.87E-05 2.13E-03 Cr-51 Ci 1.54E-05 1.15E-04 1.30E-04 Cs-137 Ci 1.76E-04 1.87E-06 9.48E-06 1.87E-04 Fe-55 Ci 6.68E-04 6.68E-04 Mn-54 Ci 4.97E-06 7.70E-06 1.27E-05 Ni-63 Ci 3.45E-03 1.12E-03 1.69E-03 1.80E-03 8.06E-03 Sb-124 Ci 2.17E-04 2.51E-04 2.05E-05 4.89E-04 Sb-125 Ci 3.05E-03 8.88E-04 3.75E-04 2.OOE-04 4.51 E-03 Te-123m Ci 8.64E-05 1.56E-04 2.68E-05 2.69E-04 Te-125m Ci 6.16E-04 9.95E-04 1.61E-03 Zn-65 Ci 6.81 E-06 6.81 E-06 Total for Period Ci 1.06E-02_7.88E-03 3.07E-03 2.48E-03 2.41 E-02 Dissolved and Entrained Gas (Batch).

Xe-133 Ci 2.66E-03 2.40E-05 3.69E-05 2.72E-03 AXe-135 Ci 2.37E-06 2.37E-06 0.OOE+00 I

Total for Period Ci 2.66E-03 2.40E-05 0.OOE+00 3.69E-05 2.72E-03 S...............

Continuous Releases (SG H-3 (only)

BloL'dow)

°,T I

Ci

<.4mda4I4.2E-3.21 E-78E-03

-indicates <mda

Docket No. 50-3, 50-247, & 50-286 Page 20 of 63 Indian Point Energy Center (Units 1, 2, and 3)

RADIOACTIVE EFFLUENT REPORT D. SOLID WASTE 2013

Docket No. 50-3, 50-247, & 50-286 Page 21 of 63 Units I and 2 Solid Waste Shipped Offsite for Disposal and Estimates of Major Nuclides by Waste Class and Stream 01/01/2013 to 12131/2013 Percent Cutoff: 0 (all identified isotopes are included)

Waste Stream : Resins, Filters, and Evap Bottoms LWS Resin Plant Resin 8-120 2011 Filters WMG Rx Cavity/SFP Demin Waste Volume Curies

% Error (Ci)

Class ft3 m 3 Shipped A

1.77E+02 5.01 E+00 5.52E+00

+/-25%

B 0.OOE+00 0.OOE+00 0.OOE+00

+/- 25%

C 1.38E+02 3.91 E+00 6.88E+01

+/- 25%

All 3.15E+02 8.92E+00 7.43E+01

+/-25%

Waste Stream

Dry Active Waste Soil / Bebris Intermodal Scrap Metal 20' Sea Land DAW/Dirt; B-25 Box DAW 20' Sea Land Waste Volume Curies

% Error (Ci)

Class ft3 m 3 Shipped A

1.98E+04 5.60E+02 5.36E-02

+/-25%

B 0.OOE+00 0.OOE+00 0.OOE+00

+/-25%

C 0.OOE+00 0.OOE+00 0.OOE+00

+/-25%

All 1.98E+04 5.60E+02 5.36E-02

+/-25%

Waste Stream

Irradiated Components Waste Volume Curies

% Error (Ci)

Class ft3 m 3 Shipped A

0.OOE+00 0.OOE+00 0.OOE+00

+1-25%

B 0.OOE+00 0.OOE+00 0.OOE+00

+/-25%

C 0.OOE+00 0.OOE+00 0.OOE+00

+1-25%

All 0.OOE+00 0.OOE+00 0.OOE+00

+1-25%

Waste Stream: Other Waste Waste Volume Curies

% Error (Ci)

Class ft3 m 3 Shipped A

0.OOE+00 0.OOE+00 0.OOE+00

+/-25%

B 0.OOE+00 0.00E+00 0.OOE+00

+1-25%

C O.OOE+00 0.OOE+00 0.OOE+00

+/-25%

All 0.OOE+00 0.00E+00 0.OOE+00

+/-25%

Waste Stream: Sum of All 4 Categories LWS Resin DAW / Dirt; B-25 Box DAW 20' Sea Land Soil / Debris - Intermodal Waste Volume Curies

% Error (Ci)

Class ft3 m 3 Shipped A

2.OOE+04 5.65E+02 5.57E+00

+1-25%

B 0.OOE+00 0.OOE+00 0.OOE+00

+/-25%

C 1.38E+02 3.91 E+00 6.88E+01

+/-25%

All 2.01 E+04 5.69E+02 7.44E+01

+/-25%

Combined Waste Type Shipment, Major Volume Waste Type Shown

Docket No. 50-3, 50-247, & 50-286 Page 22 of 63 Units 1 and 2 Solid Waste Shipped Offsite for Disposal and Estimates of Major Nuclides by Waste Class and Stream 01/01/2013 to 12/31/2013 Percent Cutoff: 0 Number of Shipments Mode of Transportation Destination 1

4 Hittman Transport Hittman Transport R & R Trucking Inc.

Hittman Transport Barnwell Processing Facility Energy Solutions - Bear Creek Studsvik Processing - Memphis Studsvik Processing Facility 50 1

Resins, Filters, and Evaporator Bottoms Waste Class A Nuclide Name H-3 C-14 Mn-54 Fe-55 Fe-59 Co-57 Co-58 Co-60 Ni-63 Zn-65 Zr-95 Ag-110m Sb-125 Cs-134 Cs-1 37

% Abundance 13.39%

12.81%

0.16%

9.45%

0.01%

0.14%

1.62%

8.43%

23.40%

0.04%

0.01%

0.07%

3.86%

0.70%

25.92%

Curies 7.38E-01 7.06E-01 8.78E-03 5.21 E-01 5.73E-04 7.52E-03 8.95E-02 4.65E-01 1.29E+00 2.17E-03 5.25E-04 3.81 E-03 2.13E-01 3.88E-02 1.43E+00

Docket No. 50-3, 50-247, & 50-286 Page 23 of 63 Units I and 2 Solid Waste Shipped Offsite for Disposal and Estimates of Major Nuclides by Waste Class and Stream 01/01/2013 to 12/31/2013 Percent Cutoff: 0 Resins, Filters, and Evaporator Bottoms Waste Class C Nuclide Name C-14 Mn-54 Fe-55 Co-57 Co-58 Co-60 Ni-63 Sr-90 Nb-94 Ag-110m Sb-125 Cs-134 Cs-137

% Abundance 3.54%

0.31%

19.68%

0.15%

4.02%

13.64%

51.53%

0.10%

0.03%

1.82%

3.39%

0.12%

1.69%

Curies 2.44E+00 2.10E-01 1.35E+01 1.04E-01 2.77E+00 9.39E+00 3.55E+01 6.75E-02 1.92E-02 1.25E+00 2.33E+00 8.10E-02 1.17E+00

Docket No. 50-3, 50-247, & 50-286 Page 24 of 63 Units I and 2 Solid Waste Shipped Offsite for Disposal and Estimates of Major Nuclides by Waste Class and Stream 01/01/2013 to 12/31/2013 Percent Cutoff: 0 Resins, Filters, and Evaporator Bottoms Waste Class All Nuclide Name H-3 C-14 Mn-54 Fe-55 Fe-59 Co-57 Co-58 Co-60 Ni-63 Zn-65 Sr-90 Zr-95 Nb-94 Ag-110m Sb-125 Cs-134 Cs-1 37

% Abundance 0.99%

4.23%

0.29%

18.92%

0.00%

0.15%

3.84%

13.25%

49.44%

0.00%

0.09%

0.00%

0.03%

1.69%

3.42%

0.16%

3.49%

Curies 7.38E-01 3.14E+00 2.19E-01 1.41E+01 5.73E-04 1.12E-01 2.86E+00 9.85E+00 3.68E+01 2.17E-03 6.75E-02 5.25E-04 1.92E-02 1.25E+00 2.54E+00 1.20E-01 2.59E+00

Docket No. 50-3, 50-247, & 50-286 Page 25 of 63 Units I and 2 Solid Waste Shipped Offsite for Disposal and Estimates of Major Nuclides by Waste Class and Stream 01/0112013 to 12/31/2013 Percent Cutoff: 0 Dry Active Waste Waste Class A Nuclide Name C-14 Mn-54 Fe-55 Co-57 Co-60 Ni-63 Sb-125 Cs-1 34 Cs-1 37 Dry Active Waste Waste Class All Nuclide Name C-14 Mn-54 Fe-55 Co-57 Co-60 Ni-63 Sb-125 Cs-134 Cs-137 Percent Abundance 1.11%

2.08%

15.66%

0.10%

54.92%

10.73%

1.00%

0.27%

14.13%

Percent Abundance 1.11%

2.08%

15.66%

0.10%

54.92%

10.73%

1.00%

0.27%

14.13%

Curies 5.96E-04 1.11 E-03 8.39E-03 5.20E-05 2.94E-02 5.75E-03 5.37E-04 1.45E-04 7.57E-03 Curies 5.96E-04 1.11E-03 8.39E-03 5.20E-05 2.94E-02 5.75E-03 5.37E-04 1.45E-04 7.57E-03

Docket No. 50-3, 50-247, & 50-286 Page 26 of 63 Units 1 and 2 Solid Waste Shipped Offsite for Disposal and Estimates of Major Nuclides by Waste Class and Stream 01/0112013 to 12/31/2013 Percent Cutoff: 0 Sum of All 4 Categories Waste Class A Nuclide Name H-3 C-14 Mn-54 Fe-55 Fe-59 Co-57 Co-58 Co-60 Ni-63 Zn-65 Zr-95 Ag-11im Sb-125 Cs-134 Cs-137 Percent Abundance 13.26%

12.70%

0.18%

9.51%

0.01%

0.14%

1.61%

8.88%

23.28%

0.04%

0.01%

0.07%

3.83%

0.70%

25.80%

Curies 7.38E-01 7.07E-01 9.89E-03 5.29E-01 5.73E-04 7.57E-03 8.95E-02 4.95E-01 1.30E+00 2.17E-03 5.25E-04 3.81 E-03 2.13E-01 3.90E-02 1.44E+00

Docket No. 50-3, 50-247, & 50-286 Page 27 of 63 Units I and 2 Solid Waste Shipped Offsite for Disposal and Estimates of Major Nuclides by Waste Class and Stream 01/01/2013 to 12/31/2013 Percent Cutoff: 0 Sum of All 4 Categories Waste Class C Nuclide Name C-14 Mn-54 Fe-55 Co-57 Co-58 Co-60 Ni-63 Sr-90 Nb-94 Ag-110m Sb-125 Cs-134 Cs-137 Percent Abundance 3.54%

0.31%

19.68%

0.15%

4.02%

13.64%

51.53%

0.10%

0.03%

1.82%

3.39%

0.12%

1.69%

Curies 2.44E+00 2.10E-01 1.35E+01 1.04E-01 2.77E+00 9.39E+00 3.55E+01 6.75E-02 1.92E-02 1.25E+00 2.33E+00 8.1OE-02 1.17E+00

Docket No. 50-3, 50-247, & 50-286 Page 28 of 63 Units I and 2 Solid Waste Shipped Offsite for Disposal and Estimates of Major Nuclides by Waste Class and Stream 01/01/2013 to 12/31/2013 Percent Cutoff: 0 Sum of All 4 Categories Waste Class All Nuclide Name H-3 C-14 Mn-54 Fe-55 Fe-59 Co-57 Co-58 Co-60 Ni-63 Zn-65 Sr-90 Zr-95 Nb-94 Ag-110m Sb-125 Cs-134 Cs-1 37 Percent Abundance 0.99%

4.23%

0.30%

18.92%

0.00%

0.15%

3.84%

13.28%

49.41%

0.00%

0.09%

0.00%

0.03%

1.69%

3.42%

0.16%

3.50%

Curies 7.38E-01 3.14E+00 2.20E-01 1.41E+01 5.73E-04 1.12E-01 2.86E+00 9.88E+00 3.68E+01 2.17E-03 6.75E-02 5.25E-04 1.92E-02 1.25E+00 2.54E+00 1.20E-01 2.60E+00

Docket No. 50-3, 50-247, & 50-286 Page 29 of 63 Unit 3 Solid Waste Shipped Offsite for Disposal and Estimates of Major Nuclides by Waste Class and Stream 01/01/2013 to 12/31/2013 Percent Cutoff: 0 (all identified isotopes are included)

Waste Stream: Resins, Filters, and Evaporator Bottoms LWS Resin 14-215 Waste Volume Curies

% Error (Ci)

Class ft3 m 3 Shipped A

1.48E+02 4.19E+00 1.64E+00

+/- 25%

B 0.QOE+00 Q.OOE+00 O.QOE+00

+/- 25%

C O.OOE+O0 O.OOE+O0 O.OOE+00

+/- 25%

All 1.48E+02 4.19E+00 1.64E+00

+/-25%

Waste Stream : Dry Active Waste Unit 3 DAW-20' Sealand U3 DAW B-25 20' Intermodal Soil Waste Volume Curies

% Error (Ci)

Class ft3 m 3 Shipped A

2.04E+04 5.77E+02 9.20E-01

+/-25%

B 0.OOE+00 Q.OOE+00 0.OOE+00

+/-25%

C O.OOE+00 0.OOE+00 O.OOE+00

+/-25%

All 2.04E+04 5.77E+02 9.20E-01

+/-25%

Waste Stream : Irradiated Components Waste Volume Curies

% Error (Ci)

Class ft3 m 3 Shipped A

0.OOE+00 O.OOE+00 0.OOE+00

+/-25%

B 0.OOE+00 0.OOE+00 Q.OOE+00

+/-25%

C 0.OOE+00 0.OOE+00 O.OOE+00

+/-25%

All O.OOE+00 0.OOE+00 0.O0E+00

+/-25%

Waste Stream : Other Waste Waste Volume Curies

% Error (Ci)

Class ft3 m 3 Shipped A

0.OOE+00 0.OOE+00 0.OOE+00

+/-25%

B O.OOE+00 0.OOE+00 Q.OOE+00

+/-25%

C 0.00E+00 0.O0E+00 0.OOE+00

+/-25%

All 0.OOE+00 0.QOE+00 0.OOE+00

+/-25%

Waste Stream : Sum of All 4 Categories LWS Resin 14-215 Unit 3 DAW-20' Sealand U3 DAW B-25 20' Intermodal Soil Waste Volume Curies

% Error (Ci)

Class ft3 m 3 Shipped A

2.05E+04 5.81E+02 2.56E+00

+/-25%

B 0.OOE+00 O.OOE+00 Q.OOE+00

+/-25%

C 0.OOE+0Q 0.O0E+00 O.OOE+00

+/-25%

All 2.05E+04 5.81 E+02 2.56E+00

+/-25%

Combined Waste Type Shipment, Major Volume Waste Type Shown

Docket No. 50-3, 50-247, & 50-286 Page 30 of 63 Unit 3 Solid Waste Shipped Offsite for Disposal and Estimates of Major Nuclides by Waste Class and Stream 01/01/2013 to 12/31/2013 Percent Cutoff: 0 Number of Shipments Mode of Transportation Destination 1

9 9

Hittman Transport Hittman Transport R & R Trucking Barnwell Processing Facility Energy Solutions Bear Creek Studsvik Processing - Memphis Resins, Filters, and Evaporator Bottoms Waste Class A Nuclide Name Percent Abundance Curies C-14 Mn-54 Fe-55 Co-57 Co-58 Co-60 Ni-59 Ni-63 Sr-90 Sb-125 Cs-1 37 Ce-144 Pu-241 Am-241 Cm-243 1.50%

0.22%

11.10%

0.05%

0.09%

9.11%

0.47%

50.58%

0.01%

22.45%

4.22%

0.12%

0.07%

0.00%

2.47E-02 3.58E-03 1.82E-01 8.71E-04 1.50E-03 1.50E-01 7.75E-03 8.30E-01 2.17E-04 3.68E-01 6.92E-02 2.04E-03 1.07E-03 5.10E-06 2.57E-06

Docket No. 50-3, 50-247, & 50-286 Page 31 of 63 Unit 3 Solid Waste Shipped Offsite for Disposal and Estimates of Major Nuclides by Waste Class and Stream 0110112013 to 12/31/2013 Percent Cutoff: 0 Resins, Filters, and Evaporator Bottoms Waste Class All Nuclide Name Percent Abundance Curies C-14 Mn-54 Fe-55 Co-57 Co-58 Co-60 Ni-59 Ni-63 Sr-90 Sb-125 Cs-1 37 Ce-144 Pu-241 Am-241 Cm-243 1.50%

0.22%

11.10%

0.05%

0.09%

9.11%

0.47%

50.58%

0.01%

22.45%

4.22%

0.12%

0.07%

0.00%

2.47E-02 3.58E-03 1.82E-01 8.71 E-04 1.50E-03 1.50E-01 7.75E-03 8.30E-01 2.17E-04 3.68E-01 6.92E-02 2.04E-03 1.07E-03 5.10E-06 2.57E-06

Docket No. 50-3, 50-247, & 50-286 Page 32 of 63 Unit 3 Solid Waste Shipped Offsite for Disposal and Estimates of Major Nuclides by Waste Class and Stream 01101/2013 to 12/31/2013 Percent Cutoff: 0 Dry Active Waste Waste Class A Nuclide Name C-14 Cr-51 Mn-54 Fe-55 Co-57 Co-58 Co-60 Ni-63 Sr-90 Zr-95 Nb-95 Sn-113 Sb-125 Cs-1 34 Cs-137 Dry Active Waste Waste Class All Nuclide Name C-14 Cr-51 Mn-54 Fe-55 Co-57 Co-58 Co-60 Ni-63 Sr-90 Zr-95 Nb-95 Sn-113 Sb-125 Cs-134 Cs-1 37 Percent Abundance 2.73%

0.15%

0.19%

5.09%

0.01%

2.29%

20.40%

59.88%

0.23%

0.61%

1.12%

0.03%

0.11%

0.43%

6.73%

Percent Abundance 2.73%

0.15%

0.19%

5.09%

0.01%

2.29%

20.40%

59.88%

0.23%

0.61%

1.12%

0.03%

0.11%

0.43%

6.73%

Curies 2.51 E-02 1.33E-03 1.72E-03 4.68E-02 1.08E-04 2.11 E-02 1.88E-01 5.51 E-01 2.12E-03 5.63E-03 1.03E-02 2.27E-04 1.03E-03 3.93E-03 6.19E-02 Curies 2.51 E-02 1.33E-03 1.72E-03 4.68E-02 1.08E-04 2.11 E-02 1.88E-01 5.51 E-01 2.12E-03 5.63E-03 1.03E-02 2.27E-04 1.03E-03 3.93E-03 6.19E-02

Docket No. 50-3, 50-247, & 50-286 Page 33 of 63 Unit 3 Solid Waste Shipped Offsite for Disposal and Estimates of Major Nuclides by Waste Class and Stream 0110112013 to 12/31/2013 Percent Cutoff: 0 Sum of All 4 Categories Waste Class A Nuclide Name C-14 Cr-51 Mn-54 Fe-55 Co-57 Co-58 Co-60 Ni-59 Ni-63 Sr-90 Zr-95 Nb-95 Sn-113 Sb-125 Cs-1 34 Cs-1 37 Ce-144 Pu-241 Am-241 Cm-243 Percent Abundance 1.94%

0.05%

0.21%

8.94%

0.04%

0.88%

13.17%

0.30%

53.92%

0.09%

0.22%

0.40%

0.01%

14.43%

0.15%

5.12%

0.08%

0.04%

0.00%

Curies 4.98E-02 1.33E-03 5.30E-03 2.29E-01 9.78E-04 2.26E-02 3.37E-01 7.75E-03 1.38E+00 2.33E-03 5.63E-03 1.03E-02 2.27E-04 3.70E-01 3.93E-03 1.31E-01 2.04E-03 1.07E-03 5.1OE-06 2.57E-06

Docket No. 50-3, 50-247, & 50-286 Page 34 of 63 Unit 3 Solid Waste Shipped Offsite for Disposal and Estimates of Major Nuclides by Waste Class and Stream 01/01/2013 to 12/31/2013 Percent Cutoff: 0 Sum of All 4 Categories Waste Class All Nuclide Name C-14 Cr-51 Mn-54 Fe-55 Co-57 Co-58 Co-60 Ni-59 Ni-63 Sr-90 Zr-95 Nb-95 Sn-113 Sb-1 25 Cs-134 Cs-1 37 Ce-144 Pu-241 Am-241 Cm-243 Percent Abundance 1.94%

0.05%

0.21%

8.94%

0.04%

0.88%

13.17%

0.30%

53.92%

0.09%

0.22%

0.40%

0.01%

14.43%

0.15%

5.12%

0.08%

0.04%

0.00%

Curies 4.98E-02 1.33E-03 5.30E-03 2.29E-01 9.78E-04 2.26E-02 3.37E-01 7.75E-03 1.38E+00 2.33E-03 5.63E-03 1.03E-02 2.27E-04 3.70E-01 3.93E-03 1.31E-01 2.04E-03 1.07E-03 5.10E-06 2.57E-06

Docket No. 50-3, 50-247, & 50-286 Page 35 of 63 Indian Point Energy Center (Units 1, 2, and 3)

RADIOACTIVE EFFLUENT REPORT E.

RADIOLOGICAL IMPACT ON MAN Jan 1, 2013 -

Dec 31, 2013

Docket No. 50-3, 50-247, & 50-286 Page 36 of 63 RADIOLOGICAL IMPACT ON MAN Routine Effluent Dose Calculations:

The Radiological Impact on Man due to radioactive effluent from the site is determined from NRC approved modeling, per Reg Guide 1.109 and NUREG 0133. Calculations are divided into 3 categories: Noble Gases, Particulates and Iodine, and Liquid Releases (fish and invertebrate consumption). This modeling involves conservative dose calculations to Adult, Teen, Child, and Infant age groups. Furthermore, dose modeling is performed for six separate organs as well as the total body dose. This well-established industry model provides doses (as a result of plant effluent) to a hypothetical maximally exposed individual offsite. While ALL age groups and organs are considered, it is this maximum value that is provided in the tables that follow.

An approved computer code is used to perform liquid and gaseous dose calculations according to the models and parameters presented in the Indian Point Offsite Dose Calculation Manual (ODCM).

This information is stored in a database on site to enhance dose tracking and information management.

Site airborne effluent dose calculations include annual average dispersion and deposition factors, averaged from data collected over approximately ten year periods. When new data is averaged (approximately every ten years) the modeling is updated and used in subsequent airborne effluent calculations.

Liquid offsite dose calculations involve fish and invertebrate consumption pathways only, as determined appropriate in the ODCM.

While the ODCM identified some site-specific dose factors, the bulk of this information is obtained directly from Regulatory Guide 1.109 and NUREG 0133. Details of the calculations, site-specific data, and their bases are presented in the ODCM.

Carbon-14 (C-14):

Concentrations and offsite dose from C-14 were determined from sampling at Indian Point #3 from August 1980 to June 1982, during a study conducted by the NY State Department of Health (C. Kunz, later published and incorporated into NCRP 81). The annual C-14 curies released, as determined from this study, were consistent with NUREG 0017, Rev. 1. Data was then normalized to a maximum expected annual total, based on rated electrical capacity, (approximately 1000 MW(e) maintained for the entire.year). Once the curies released were established, dose calculations were performed per the station ODCM, which uses all C-14 released to determine inhalation doses, and 26% of the total (determined to be Carbon Dioxide form), to determine the ingestion doses, in accordance with Reg Guide 1.109.

In 2010, IPEC and other facilities combined historical data with the application of an EPRI model designed to estimate C-14 releases, given some key site-specific plant parameters (mass of the primary coolant, average thermal neutron cross section, rated MW, etc). The estimates from this model, for IPEC, closely match the measured observations of 1982.

The maximum annual C-14 release information is as follows:

Maximum (Bounding) Annual C-14 releases from IPEC Unit 2 Unit 3 Liquid Effluent C14 Released Curies 0.07 0.07 Total Airborne C14 Released Curies 11.19 11.05 Airborne C14 as CO 2 Curies 2.91 2.87 Airborne Effluent Child TB Dose, C14 mrem 0.0690 0.0675 Airborne Effluent Child Bone Dose, C14 mrem 0.346 0.338 Liquid Effluent Child TB Dose, C14 mrem 0.00117 0.00116 Liquid Effluent Child Bone Dose, C14 mrem 0.00583 0.00577

Docket No. 50-3, 50-247, & 50-286 Page 37 of 63 The bounding values were then normalized with actual effective full power days (EFFD) to yield more accurate year to year annual airborne curies and mrem for each unit. A small liquid effluent component is maintained at IPEC as a result of data accumulated in the 1983 study (Kunz).

Tables 1A (shown earlier) include the airborne curie data for the current year. The following section (Radiological Impact on Man) includes the dose information.

C-14 doses are grouped with "Iodine and Particulate" and reported in Table D in the following Radiological Impact on Man tables, for each unit. Table "C" provides doses from this category excluding C-14, to facilitate historical comparisons.

However, since C-14 is grouped as a particulate, the total dose for this isotope needs to be added to all other lodines and Particulates, for comparison of the singular dose limit for this category.

Therefore, table "D" includes dose from all categories of this group (Iodine, Particulate, Tritium, and Carbon-14), for appropriate comparison of the dose limits.

C-14 doses (alone) for the current year are provided (for information) in the following table:

Calculated Annual C-14 releases from IPEC, 2013 1

I Airborne Effluent Child TB Dose, C14 mrem Airborne Effluent Child Bone Dose, Cý mrem unit,a 0.0611 0.306 The airborne effluent dose from C-14 is distributed evenly over the year and applied to a total Iodine and Particulate dose in Table "D" following this section.

Members of the Public:

Members of the public visiting the site receive minimal dose as a result of onsite releases because of the relatively insignificant total amount of time they are on site, as well as the immeasurably low levels of dose at the critical receptors. Their doses can be calculated from standard ODCM methodology, with typical occupancy factors employed. These factors are determined by comparing a conservative assumption for their expected hours on site, to 8760 hours0.101 days 2.433 hours 0.0145 weeks 0.00333 months (the number of hours in a year, used in calculations in the ODCM).

example 1:

Several students visit the site for an 8-hour guided tour.

Their occupancy factor is:

8/ 8760 or 0.0009.

example 2:

A man drives his wife to work and drops her off at the security gate each morning, with a total stay-time on site for 2 minutes per day. His occupancy factor is calculated as follows:

2 min/60 min/hr =0.0333 hr; 0.0333 / 8760 = 3.8E-6.

While onsite meteorological factors (dispersion and deposition) may be as high as a factor of ten higher than those used by the ODCM for routine effluents, these occupancy factors, when multiplied by doses calculated per the ODCM, demonstrate that dose to MEMBERS OF THE PUBLIC within the site boundary is negligible.

Docket No. 50-3, 50-247, & 50-286 Page 38 of 63 Groundwater:

Curies and dose contribution from activity discovered in onsite groundwater and storm drain pathways during the year are discussed in more detail in Section H. The offsite dose calculation involves multiple source term measurements, as well as computations for release and dilution flow.

A summary of the quantification methodology, and the resulting calculated doses, is provided at the end of Section H. The Total Dose table below provides a means to compare ground water doses with those of other components making up the total offsite dose.

Total Dose:

Unit and pathway-specific dose data can be found on the Radiological Impact on Man tables following this discussion.

For simplicity and to demonstrate compliance with 40CFR190, the following table indicates the maximum hypothetical Total Dose to an individual from operation of the facility, including any measured direct shine component from the site property:

Year: 2013 I.

Total Body Max Organ 40 CFR 190 limit==

IPEC 25 mrem 75 mrem Routine Airborne Effluents' Units I and 2 2.26E-03 2.26E-03 Routine Liquid Effluents Units 1 and 2 1.17E-03 1.90E-03 Liquid Releases of C14 Units 1 and 2 1.17E-03 5.83E-03 Airborne Releases of C14 Units 1 and 2 6.76E-02 3.39E-01 Routine Airborne Effluents' Unit 3 2.25E-03 2.25E-03 Routine Liquid Effluents Unit 3 2.05E-04 4.45E-04 Liquid Releases of C14 Unit 3 1.1 7E-03 5.83E-03 Airborne Releases of C14 Unit 3 6.11 E-02 3.06E-01 Ground Water & Storm Drain Totals IPEC 2 7.78E-05 3.15E-04 Direct Shine from areas such as dry cask storage, radwaste storage, SG IPEC3 1.30E-01 1.30E-01 Mausoleum, etc.

Indian Point Energy Center Total Dose, per 40 CFR 190 E

1 Note 1: Routine airborne dose in this table is conservatively represented as a sum of Iodine, Particulate, and Tritium dose (excluding C-14, in mrem) with a mrem term added from noble gas gamma air energy (mrad, expressed as mrem). This 'addition' does not represent a real dose and is listed here solely to help demonstrate compliance with 40CFR1 90.

(Doses by type of release and comparison to the specific limits of 10CFR50 Appendix I are summarized on the following pages.)

Note 2: Groundwater curie and dose calculations are provided in Section H.

Note 3: 40CFR190 requires the reporting of total dose, including that of direct shine. Direct shine dose from sources other than dry cask are indistinguishable from background.

Direct shine dose is determined from TLDs near the dry cask area and site boundary, compared with REMP TLDs and historical values, and corrected with occupancy factors to determine a bounding, worst case assessment of direct shine dose to a real individual.

These doses are slightly higher than those of the previous year due to additional storage on the Independent Spent fuel Storage Installation (ISFSI). Details of each year's dose evaluation are available on site from Radiation Protection.

'Docket No. 50-3, 50-247, & 50-286 Page 39 of 63 INDIAN POINT UNITS 1 and 2 NUCLEAR POWER PLANTS RADIOLOGICAL IMPACT ON MAN JANUARY -

DECEMBER 2013 Maximum exposed individual doses in mrem or mrad A. LIQUID DOSES F

Y V

Y Qtr 1:

Qtr2 Qtr 3 Qtr 4 ANNUAL Organ Dose (mrem) 1.60E-04 2.61E-04 2.29E-04 1.26E-03 [ 1.90E-03 Applicable Limit (mrem) 5 5

5 5

10 Percent of Limit

(%)

3.20E-03 5.22E-03 4.58E-03 2.52E-02 j 1.90E-02 Age Group Adult Child Child Child Child Critical Organ Liver bone Bone Bone Bone Adult Total Body (mrem) 1.59E-04 1.70E-04 1.67E-04 6.78E-04 1.17E-03 Applicable Limit (mrem) 1.5 1.5 1.5 1.5 3.0 Percent of Limit

(%)

1.06E-02 1.13E-02 1.11E-02 4.52E-02 3.91 E-02 B. AIRBORNE NOBLE GAS DOSES Qtr 1 Qtr 2 Qtr 3 Qtr4 ANNUAL Gamma Air (mrad) 1.66E-05 1.09E-05 2.74E-05 2.58E-05 8.07E-05 Applicable Limit (mrad) 5 5

5 5

10 Percent of Limit

(%)

3.32E-04 2.18E-04 5.48E-04 5.16E-04 8.07E-04 Beta Air (mrad) 1.89E-05 7.27E-06 2.33E-05

1. 77E-05 6.72E-05 Applicable Limit (mrad) 10 10 10 10 20 :J.

Percent of Limit

(%)

1.89E-04 7.27E-05 2.33E-04 1.77E-04 3.36E-04

.C. AIRBORNE IODINE, PARTICULATE, & TRITIUM DOSES (excluding C-14, for info only):z Qtr 1 Qtr 2 Qtr 3 Qtr 4 ANNUAL Iodine/Part (mrem) 3.31 E-04 8.46E-04 5.55E-04 4.52E-04 2.18E-03 Applicable Limit (mrem) 7.5 7.5 7.5 7.5 15 Percent of Limit

(%)

4.41 E-03 1.13E-02 7.40E-03 6.03E-03 1.46E-02 Age Group Child Child Child Child Child Critical Organ Liver Liver Liver Liver Liver D. AIRBORNE IODINE, PART1CULATE, TRITlUM, and CARBON-14 DOSES Child TB Dose (mrem) 1.72E-02 1.77E-02 1.75E-02 1.74E-02 6.98E-02 Applicable Limit (mrem) 7.5 7.5 7.5 7.5 15 Percent of Limit

(%)

2.30E-01 2.37E-01 2.33E-01 2.31 E-01 4.65E-01 SQtr 1

Qtr 2 Qtr 3 Qtr 4 ANNUAL Child Bone Dose (mrem) 8.48E-02 8.48E-02 8.48E-02 8.48E-02 3.39E-01 Applicable Limit (mrem) 7.5 7.5 7.5 7.5 15 Percent of Limit

(%)

1.13E+00 1.13E+00 1.13E+00 1.13E+00 2.26E+00

Docket No. 50-3, 50-247, & 50-286 Page 40 of 63 INDIAN POINT 3 NUCLEAR POWER PLANT RADIOLOGICAL IMPACT ON MAN JANUARY DECEMBER 2013 Maximum exposed individual doses in mrem or mrad A. LIQUID DOSES I-4..4 1)

I"÷r% -,

f1%4 A

AkIkll IAI Organ Dose (mrem) 2.63E-04 5.22E-05 5.90E-05 7.38E-05 4.45E-04 Applicable Limit (mrem) 5 5

5 5

10 Percent of Limit

(%)

5.26E-03 1.04E-03 1.18E-03 1.48E-03 4.45E-03 Age Group Child Adult Child Child Child Critical Organ Bone GILLI Bone Bone Bone Adult Total Body (mrem) 1.59E-04 1.42E-05 3.26E-06 2.86E-05 2.05E-04 ]

Applicable Limit (mrem) 1.5 1.5 1.5 1.5 3.0 Percent of Limit

(%)

1.06E-02 9.47E-04 2.17E-04 1.91E-03 6.84E-03

...... j

..i B. AIRBORNE NOBLE GAS DOSES Qtr 1 Qtr 2 Qtr 3 Qtr 4 ANNUAL Gamma Air (mrad) 3.71 E-05 3.52E-06 3.89E-06 3.44E-06 4.80E-05 Applicable Limit (mrad) 5 5

5 5

10 Percent of Limit

(%)

7.42E-04 7.04E-05 7.78E-05 6.88E-05 4.80E-04 Beta Air (mrad) 8.02E-05 6.86E-06 6.78E-06 5.92E-06 9.98E-05 J Applicable Limit (mrad) 1 10 10 10 10 20 F

Percent of Limit

(%)

8.02E-04 6.86E-05 6.78E-05 5.92E-05 4.99E-04

ýC. AIRBORNE IODINE, PARTICULATE,& TRITIUM DOSES (excluding C-14, for info only).

Qtr 1 Qtr 2 Qtr 3 Qtr 4 ANNUAL Iodine/Part (mtrer) 5.87E-04 5.44E-04 5.43E-04 5.21 E-04 2.20E-03 Applicable Limit (mrem) 7.5 7.5 7.5 7.5 15 Percent of Limit

(%)

7.83E-03 7.25E-03 7.24E-03 6.95E-03 1.46E-02 Age Group Child Child Child Child Child Critical Organ Liwer Liver Liver Liver Liver D. AIRBORNE IODINE, PART1CULATE, TRIILUM, and CARBON-14 DOSES Child TB Dose (mrem) 1.59E-02 1.58E-02 1.58E-02 1.58E-02 6.33E-02 Applicable Limit (mrem) 7.5 7.5 7.5 7.5 15 Percent of Limit

(%)

2.11E-01 2.11E-01 2.11E-01 2.11E-01 4.22E-01 Qtr 1 Qtr 2 Qtr 3 Qtr 4 ANNUAL Child Bone Dose (mrem) 7.65E-02 7.65E-02 7.65E-02 7.65E-02 3.06E-01 Applicable Limit (mrem) 7.5 7.5 7.5 7.5 15 Percent of Limit

(%)

1.02E+00 1.02E+00 1.02E+00 1.02E+00 2.04E+00

Docket No. 50-3, 50-247, & 50-286 Page 41 of 63 Indian Point Energy Center (Units 1, 2, and 3)

RADIOLOGICAL EFFLUENT REPORT F.

METEOROLOGICAL DATA Jan 1, 2013 -

Dec 31, 2013 This data is stored onsite and is available in printed or electronic form.

Docket No. 50-3, 50-247, & 50-286 Page 42 of 63 Indian Point Energy Center (Units 1, 2, and 3)

RADIOACTIVE EFFLUENT REPORT G. OFFSITE DOSE CALCULATION MANUAL, REMP SAMPLING LOCATIONS, PROCESS CONTROL PROGRAM, OR LAND USE CENSUS LOCATION CHANGES 2013 There were no changes to the REMP Sampling Locations in 2013.

There were no changes in the Land Use Census in 2013.

The Process Control Program (PCP) was updated in 2013 An administrative update to this fleet procedure was performed to ensure inter-changeable position titles for the "General Plant Manager" and "Plant Superintendent" at Palisades. See the enclosed fleet procedure.

There were no changes to the IPEC ODCM in 2013

Docket No. 50-3, 50-247, & 50-286 Page 43 of 63 Indian Point Energy Center (Units 1, 2, and 3)

RADIOACTIVE EFFLUENT REPORT H. GROUNDWATER and STORM WATER REPORT ACTIVITY ON SITE and OFFSITE DOSE CALCULATION FOR THE PERIOD:

Jan 1, 2013 -

Dec 31, 2013

Docket No. 50-3, 50-247, & 50-286 Page 44 of 63 Summary of IPEC Groundwater and Storm Water Activity, 2013 The precipitation mass balance model applied in previous years was applied for offsite dose calculations in 2013, with some minor calibration updates performed by the contractor with regard to the distribution of groundwater flow through the site. Groundwater elevation readings continued to validate the model throughout the year.

As defined in the ODCM, a conservative method of source term selection is used for determining offsite dose from Groundwater and Storm Water. If a result is below MDC (whether positive or negative) it is not included in the computed average.

This computed average is therefore biased high (more conservative from a dose computation perspective) relative to an average computed using all of the data (many of which indicate no activity).

In cases where all the sampling locations assigned to a given stream tube provided results below the MDC, then an average activity value of zero was assigned to the effected portion of the stream tube. (This mathematically allows the calculation to proceed in the absence of positive detections).

Historical average precipitation at IPEC has been approximately 3 feet per year.

In 2011, precipitation was unusually high (over 6 feet). In 2013, precipitation was measured at 2.81 feet per year (or inches per month, as an average).

Doses from Groundwater/Storm water are dependent on two factors: source term and precipitation during the effected year.

Results of 2013 Groundwater and Storm water offsite dose evaluation The results of the assessment are shown on the following table. These dose values are a small portion of the annual limits (<0.005%), and were added to the Total Dose table in the opening summary of the Dose to Man section of this report (Section E).

Groundwater (GW) and storm water tritium released from IPEC in 2013 totaled approximately 0.199 curies, resulting in a total body dose of significantly less than 0.1 mrem (2.4E-7 mrem). It is evident that tritium alone, whether from ground water or routine effluents, does not arithmetically contribute to integrated offsite dose.

Sampling near the effluent points identified only trace levels of Cesium-137, Tritium and Strontium-90. These data, as part of the Monitored Natural Attenuation analyses, show a continuation of the decreasing trends established with the termination of the identified Unit 2 SFP leaks (tritium plume) and the defueling and draining of Unit 1 SFPs (strontium plume).

Strontium-90, a legacy isotope from Unit 1, contributed approximately 0.000022 curies to site effluent from the groundwater pathway.

Combined GW releases from IPEC in 2013 (all radionuclides) resulted in a calculated annual dose of less than 0.0032% of the annual limits for whole body and critical organ:

IPEC Groundwater and Storm Water Effluent Dose, 2013 0.0000778 mrem to the total body (0.00259% limit) 0.000315 mrem to the critical organ, adult bone (0.00315% limit)

The annual dose from combined groundwater and storm water pathways remains well below applicable limits. When combined with routine liquid effluents (Section E), the total dose also remains significantly below ALARA limits of 3 mrem total body, and 10 mrem to the critical organ.

Docket No. 50-3, 50-247, & 50-286 Page 45 of 63 IPEC Summary for Storm & Ground Water releases (H-3, Co-60, Ni-63, Sr-90, and Cs-137)

Nnrth~rn (*lI=*n ;7nn*

Adult Doses in mrem ISOTOPE.

BONEV*

',LIVER TOT BODY,.

THYROID KIDNEY LUNG

- GI-wLLI*:;

H-3 0.00E+00 3.69E-09 3.69E-09 1 3.69E-09 3.69E-09 3.69E-09 3.69E-09 Co-60 0.00E+00 0.OOE+00 0.00E+00 0.00E+00 0.00E+00 0.OOE+00 0.OOE+00 Ni-63 0.OOE+0O 0.00E+00 0.OOE+00 0.OOE+00 0.OOE+00.

0.OOE+00 0.00E+00 Sr-90 0.OOE+00 0.OOE+00 0.00E+00 0.OOE+00 0.00E+00 0.00E+00 0.00E+00 F

Cs-137 0.00E+00 0.OOE+00 0.00E+00 I 0.00E+00 0.00E+00 I 0.00E+00 0.00E+00 i

totals 0.00E+00 3.69E-09 3.69E-09 I 3.69E-09 3.69E-09 I 3.69E-09 3.69E-09 Unit 2 North ISOTOPE' BONE.'

LIVER TOT BODY THYROID KIDNEY:

LUNG

'GI-LLI.

H-3 0.00E+00 1.01E-08 1.01E-08 1.01E-08 1.01E-08 1.01E-08 1.01E-08 Co-60 0.00E+00 0.00E+00 0.00E+00.

0.OOE+00.

0.00E+00 0.00E+00 0.00E+00 Ni-63 O.00E+00 0.00E+00 0.0OE+00 0.0OE+00 0.O00.00E 000 0.00E+00 Sr-90 0.OOE+00 O.00E+00 0.OOE+00 0.OOE+00 0.OOE+00 0.OOE+00 0.OOE+00 Cs-137 O.OOE+00 0.00E+0 0.00E+00 O.OOE+0O 0.00E+00 0.OOE+00 0.00E+00 totals 0.OOE+00 1.01E-08 1.01E-08 1.01E-08 1.01E-08 1.01E-08 1 1.E-O8 Unit 1/2 IVISOTOPE.

BONE:-

-ý,IVER

,TOT BODY'I.

THYROID

KIDNEY, LUNG..

GI-LLIF H-3 0.0OE+00 5.23E-08 5.23E-08 5.23E-08 5.23E-08 5.23E-08 5.23E-&M Co-60 0.OOE+00 0.OOE+00 O.OOE+00 O.OOE+00 O.00E+00 0.00E+00 O.OOE+00 Ni-63 0.OOE+00 0.OOE+00 0.00E+00 0.00E+00 0.OOE+00 0.00E+00 0.OOE+00 Sr-90 1.06E-04 0.OOE+00 2.60E-05 I 0.OOE+00 O.00E+00 O.OOE+00 3.05E-06 Cs-137 5.07E-07 6.94E-07 4.55E-07 0.OOE+00 2.35E-07 7.83E-08 1.34E-08 totals I1.06E-04 7.46E-07 2.66E-05 5.23E-08 2.88E-07 1.31E-07 3.12E-06 Unit 3 North ISOTOPE.ý':

BONE LIVER TOT..BODY THYROID KIDNEY LUNG GI-LLI H-3

.00E+00

=.0-8 -7.9ME0 7.70E-08

-7.9E-8=

7.90E-08 7.90E-0 Co-60 0.OOE+00 O.OOE+00 0.00E+00 O.OOE+00 0.00E+00.

0.00E+00 O.OOE+00 Ni-63 0,00E+00 0.00E+0 O0.00E+00

.00E+00 O.OOE+00 O..000E+OO 0.OOE+00.

Sr-90 2.09E-04 0.OOE+00 5.12E05 0.00EE+00

+.00E O

0.

00E

6.01E-06 Cs-137 0.OOE+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 000E+00 totals 2.09E-04 7.90E-08 5.12E-05 7.90E-08 7.90E-08 I 7.90E-08 6.09E-06 Unit 3 South ISOTOPE BONE.',"'

LIVER.

TOT BODY, THYROID.

KIDNEY LUNG;..

GI-L,,I-.

H-3 O.OOE+00 7.85E-08.

7.85E-08 7.85E-08 7.85E-08 7.85E-08 7:85E-08 Co-60 0.00E+00 0.00E+00 0.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 O.OOE+00 Ni-63 0.00E+00 0.OOE+00 0.OOE+00 0.OOE+00 0.OOE+00 0.00E+00 0.OOE+00 Sr-90 0.OOE+00 0.OOE+00 0.OOE+00 O.OOE+0 I 0.OOE+00 O.00E+00 0.O0E+00 Cs-137 0.00E+00 0.00E+00 0.00E+00 0.OOE+00 O.OOE+00 0.00E+00 0.OOE+00 totals 0.00E+00 7.85E-08 7.85E-08 7.85E-08 I

7.85E-08 7.85E-08 7.85E-08 Southern Clean Zone

.ISOTOPE v.. BONE:

LIVER.

TOT BODY THYROID,,

" KIDNEY..,..

LUNG GI.LLI:"

H-3 M

=

7 14.46E-08 1.46E-08

.146E-0 Co-60 0.OOE+00 O.OOE+00 O.OOE+00 0.OOE+00 0.OOE+00 0.OOE+00 0.OOE+00 Ni-63 0.OOE+00 0.OOE+00 0.00E+00 0.OOE+00 0.OOE+00 O.00E+00 0.OOE+00 Sr-90 O.00E+O0

.0.OOE+00 0.00E+00 O.OOE+00 O.OOE+00 0.00E+00 O.OOE+00 Cs-137 O.OOE+00 0.OOE+00 0.OOE+00 0.OOE+00 0.00E+00

.OOE+00 0.00E+00 totals 0.00E+00 1.46E-08 i.46E-08 1.46E-08 I1.46E-08 1.46E-08

=.46E-O8 2013 3.30E+02 uCi 4.84E+I04

+/-1X.

9.65E+03, 9.13E03 19.14E+03 4.80E+04 1480E+04:

Totals:

Adult Doses, in mrem H-3 only I

O.OOE+OO I 2.38E-07 I 2.38E-07 2.38E-07 2.38E-07 I2.38E-07 I 2.38E-07 I

'Total uCi I

BONE.

"..LIVER. 1. TOT:BQDY.., I THYROID*

KIDNEY, 1::..-LUNG:

, GI-LLI

-1.

3+05 H3 all isotopes 3.15E-04 9.32E-07 I 7.78E-05 I 2.38E-07 4.74E-07 3.16E-07 I 9.31E-06

[9p9E1p0 co I Adult Doses 2.20E01sr

%AnnualUimit 0,00315 0000 1

00259 0.000 1

0.000 1

0.000 I

E01Cs

Docket No. 50-3, 50-247, & 50-286 Page 46 of 63 INDIAN POINT RADIOLOGICAL GROUNDWATER MONITORING PROGRAM 2013 Summary of Results The following pages represent the isotopic radio-analytical data for all onsite groundwater testing performed at Indian Point in 2013, as required per the ODCM and NEI 07-07.

(The units on the following pages are pCi/L)

Docket No. 50-3, 50-247, 50-286 Page 47 of 63 Sample 3a Sample Date Dt Well ID Result Error Date B-1 drain pipe into manhole checked s 30' Sample 3a Sample 3a Sample Result Error Date Result Error Date Result Error Date everal times per quarter; no water available for samples

-4.0 9.1 7/9 3.4 8.0 10/16 0.9 9.3 7/31

-1.5 9.7 11/4 4.4 8.4 7/12 1.4 10.2 10/24 B-6 1-2 MH-5 MW-107 MW-111 MW-30-69 MW-30-84 MW-31-49 MW-31-63 MW-31-85 MW-32-149 MW-32-173 MW-32-190 MW-32-59 MW-32-85 MW-33 MW-35 MW-36-24 MW-36-41 MW-36-52 MW-37-22 MW-37-32 MW-37-40 MW-37-57 MW-39-102 MW-39-124 MW-39-183 MW-39-195 MW-39-67 MW-39-84 MW-40-100 MW-40-127 1/29 1.8 6.6 4/10 2/6 1.1 7.9 4/24 1/30 4.6 8.4 4/11 5/6 4/23 2/21

-2.2 9.2 5/2 2/21 0.3 7.2 5/2 2/4

-0.8 8.4 4/22 2/4 0.2 8.0 4/22 2/4

-0.5 8.5 4/22 2/4 3.1 8.1 4/22 2/4

-1.9 9.8 4/22 2/4 2.3 9.0 4/22 2/4 6.8 9.8 4/22 2/4 6.5 10.4 4/22 4/23 4/23 2/20

-1.6 6.9 5/1 2/20

-0.1 8.1 5/1 2/20

-0.9 7.1 5/1 2/20 2.3 11.3 5/1 2/20 4.2 4.4 5/1 2/20

-0.6 4.5 5/1 2/20

-1.1 4.6 5/1 4/24 4/24 4/24 4/24 4/24 4/24 3/13 3.1 9.5 5/7 3/13

-4.0 9.4 5/7 1.8 10.3 3.9 7.0

-3.7 7.7 8/30 0.0 5.3

-3.8 8.6 8/30

-0.5 5.3 2.7 7.1 7/15

-3.9 10.1 4.3 9.8 7/15

-5.1 8.9

-1.8 9.2 7/15 2.4 9.3 2.0 7.6 7/15

-1.2 8.6 5.0 6.0 7/15

-1.7 10.7 2.1 7.8 7/15 6.7 8.3

-1.3 7.4 7/15

-2.0 6.6 3.7 9.8 7/15 0.3 7.0 1.0 6.9 0.6 8.0

-1.9 6.7 7/31 5.2 7.6 0.8 7.7 7/31

-0.1 10.6

-5.2 9.2 7/31 3.1 9.6 4.3 7.4 7/29

-4.9 9.4

-2.7 7.9 7/29

-0.2 6.8 0.3 8.0 7/29

-2.8 7.1

-4.6 7.8

7/29 1.0 8.3

-2.2 9.7 0.8 5.9 1.2 6.7

-1.9 5.3 0.5 6.6 5.4 7.6 3.3 8.6 7/26

-3.1 7.8 2.5 9.2 7/26 0.3 7.5 12/12 12/4 12/4 10/28 10/28 10/28 10/28 10/28 10/28 10/28 10/28 11/7 11/7 11/7 11/7 11/7 11/7 11/7 10/29 10/29 10/29 10/29 10/29 10/29 11/11 11/11 3cr average Result Error 1.2 9.5 0.6

-1.4 10.0

-0.2

-3.5 8.6 1.7 1.8

-1.7 6.5 1.1

-3.1 8.6

-2.2

-2.1 6.7

-1.5 2.3 6.2 0.0 2.4 5.4 0.4 1.9 6.2 0.5 0.2 7.5 1.0

-1.4 6.1 0.0 3.0 8.6 3.5

-2.1 7.7 0.4 6.4 5.8 4.2 1.0 0.6 1.1 9.3 0.7

-0.9 8.4

-0.1 2.8 6.8

-0.1

-5.2 8.1

-0.9 3.1 6.1 1.1 0.9 5.6

-0.6

-0.4 6.4

-1.3

-8.5 8.1

-5.4 4.2 3.8 2.5 2.4 7.5 1.8 1.6 5.9

-0.1 0.4 6.0 0.5 1.2 6.3 3.3

-1.8 7.5 0.4 3.6 7.0 0.6 Co-60 in Groundwater - 2013

Docket No. 50-3, 50-247, 50-286 Page 48 of 63 Sample 3a Sample 30 Sample 3a Sample 30 Sample average Well ID Date Result Error Date Result Error Date Result Error Date Result Error Date Result Error MW-40-162 MW-40-27 MW-40-46 MW-40-81 MW-41-40 MW-41-63 MW-42-49 MW-42-78 MW-43-28 MW-43-62 MW-44-102 MW-44-66 MW-45-42 MW-45-61 MW-46 MW-47-56 MW-47-80 MW-49-26 MW-49-42 MW-49-65 MW-50-42 MW-50-66 MW-51-104 MW-51-135 MW-51-163 MW-51-189 MW-51-40 MW-51-79 MW-52-11 MW-52-122 MW-52-162 MW-52-18 MW-52-181 3/13

-1.7 10.0 3/13 0.7 4.0 3/13 4.0 9.7 3/13 5.8 9.3 2/13 0.4 6.5 2/13

-0.1 5.5 2/12

-1.2 6.9 2/12 4.7 8.0 2/19 3.3 9.8 2/19 1.6 6.9 2/26 1.2 7.0 2/26

-0.2 7.8 2/13 1.5 5.6 2/13

-1.2 5.7 1/29 4.1 9.2 1/30 3.2 5.4 1/30 0.9 3.5 1/30

-1.1 5.9 2/11

-2.5 8.3 2/11

-3.4 7.8 3/15 2.6 9.2 3/15 6.2 9.7 3/15 1.1 9.7 3/15 2.8 6.2 3/15 1.1 7.4 3/15

-0.9 10.4 5/7 1.3 8.9 7/26

-4.1 9.8 5/7

-0.7 5.9 7/26 6.4 8.1 5/7

-1.8 8.0 7/26

-0.5 7.1 5/7 1.1 7.2 7/26

-7.1 7.8 4/30

-1.9 7.0 7/22

-0.8 6.7 4/30 0.5 6.8 7/22 4.2 8.3 3/11

-1.2 6.3 4/29 0.9 6.9 7/18

-3.0 6.9 3/11

-17.1 12.2 4/29 1.1 7.7 7/18 0.0 6.9 4/26 3.0 9.9 7/19

-2.5 7.9 4126

-2.4 10.3 7/24

-3.1 9.5 5/3 7.3 9.6 7/22 0.2 7.1 5/3 1.2 6.7 7/23

-6.4 8.1 4/30

-0.6 7.1 7/23 0.0 8.3 4/30

-3.6 8.0 7/22

-1.9 8.6 4/10

-0.7 8.5 7/30 3.9 9.9 4/26 1.8 6.9 4/26 0.0 8.0 4/11 0.8 7.8 7/17 3.9 8.9 4/11 2.2 10.56 7/17 0.7 7.2 4/11 0.5 7.2 7/17 6.3 7.4 4/30 6.4 9.7 7/18

-7.8 10.2 4/30 1.2 8.9 7/18

-1.2 8.3 5/6

-4.4 9.8 7/25

-3.8 7.8 5/6 1.6 7.7 7/25 0.3 9.0 5/6 0.4 10.0 7/25 0.7 6.4 5/6 1.8 8.3 7/25

-1.0 7.5 5/6 5.3 7.6 7/25

-2.6 9.9 5/6'

-1.1 7.5 7/25 4.0 7.4 4/24 3.3 6.9 4/18 2.0 10.0 4/18 5.5 7.4 4/18

-2.1 5.9 4/18

-3.3 9.1 11/11 11/111 11/11 11/11 10/31 10/31 10/30 10/30 10131 10/3 1 11/5 11/5 11/5 11/5 11/8 10/24 10/24 10/24 10/24 10/24 11/12 11/12 11/12 11/12 11/12 11/12

-0.7 7.1

-1.3

-1.8 6.6 1.2 0.3 6.9 0.5 1.7 4.2 0.4

-2.6 5.8

-1.2 1.6 8.7 1.6 0.6 7.9

-0.8

-0.9 6.2

-2.4 3.1 5.8 1.7 0.2 8.9

-0.9

-0.8 6.5 2.0

-0.2 6.2

-1.4 0.5 6.2 0.3 4.4 4.9

-0.6

-2.0 5.5 1.3 1.8 0.0 2.2 6.0 2.5 1.0 8.3 1.2 2.7 7.4 2.1

-1.3 6.8

-1.3 0.2 6.6

-0.8

-1.4 7.3

-1.7

-3.0 8.0 1.3

-2.2 7.9 0.0 1.7 6.4 1.3 2.6 9.3 1.6 2.4 9.7 1.1 3.3 2.0 5.5

-2.1

-3.3 Co-60 in Groundwater - 2013

Docket No. 50-3, 50-247, 50-286 Page 49 of 63 Sample 30 Sample 30 Sample 30 Sample 30 Sample Date Date Date Date Date Well ID Result Error Result Error Result Error Result Error MW-52-48 4/18

-5.0 7.7 MW-52-64 4/18

-2.2 8.6 MW-53-120 2/12 2.0 5.0 4/29 0.2 6.8 7/18

-2.2 9.0 10/30 MW-53-82 2/12 0.2 6.3 4/29 0.7 8.1 7/18

-2.6 8.5 10/30 MW-54-123 2/11

-7.7 11.7 4/12

-1.7 6.1 7/23

-0.1 10.7 11/1 MW-54-144 2/11 3.3 8.5 4/12 0.6 8.8 7/23

-0.9 8.3 11/1 MW-54-173 2/11 0.0 6.9 4/12

-0.5 10.2 7/23

-0.2 7.1 11/1 MW-54-190 2/11

-0.2 4.1 4/12 2.7 5.8 7/23

-0.2 8.0 11/1 MW-54-37 2/11 4.0 8.7 4/12 0.5 6.4 7/23 0.2 6.3 11/1 MW-54-58 2/11

-4.2 9.3 4/12

-0.1 7.2 7/23 1.6 6.3 11/1 MW-55-24 2/6

-1.0 7.1 4/23 1.8 8.5 7/17

-1.9 8.2 12/12 MW-55-35 2/6

-5.3 9.2 4/23 0.5 5.2 7/17 2.2 7.7 12/12 MW-55-54 2/6 0.5 6.9 4/23 2.2 5.4 7/17

-5.4 10.2 12/12 MW-56-53 3/11 1.1 3.6 4129 1.0 6.8 1114 MW-56-83 3/11 0.2 5.3 4/29

-3.9 9.2 11/4 MW-57-11 4/12 0.4 10.1 MW-57-20 4/12 2.2 8.2 MW-57-45 4/12 2.0 9.1 MW-58-26 2/14

-2.87 5.94 4/25 2.4 7.5 11/6 MW-58-65 2/14 5.54 7.23 4/25 0.1 8.8 11/6 MW-60-135 2/7

-2.0 5.6 4/19 3.7 7.8 7/12 4.2 12.4 10/25 MW-60-154 2/7

-2.9 6.8 4/19 5.7 8.5 7/12

-4.3 12.6 10/25 MW-60-176 2/7

-0.4 6.3 4/19 2.2 8.6 7/12 0.6 8.8 10/25 MW-60-35 2/7

-0.7 6.8 4/19

-3.2 8.2 7/12 1.9 9.5 10/25 MW-60-53 2/7

-0.9 5.6 4/19 1.6 8.0 7/12

-0.1 9.7 10/25 MW-60-72 2/7 2.0 3.4 4/19 1.1 7.5 7/12 2.6 8.1 10/25 MW-62-138 2/5 2.1 10.8 4/16

-2.0 8.9 7/11 2.4 8.0 10/22 MW-62-18 2/5

-2.9 7.7 4/16

-1.7 8.9 7/11

-2.2 10.0 10/22 MW-62-182 2/5 0.3 8.6 4/16

-3.5 8.3 7/11 1.7 7.7 10/22 MW-62-37 2/5 3.2 6.3 4/16 1.6 8.6 7/11 2.7 8.9 10/22 MW-62-53 2/5 1.5 9.3 4/16

-4.7 8.1 7/11 1.7 9.0 10/22 MW-62-71 2/5 2.3 6.6 4/16

-0.1 8.8 7/11 0.5 7.9 10/22 MW-62-92 2/5

-0.4 8.4 4/16 1.1 6.2 7/11 2.8 7.3 10/22 3o average Result Error

-5.0

-2.2 0.0 6.5 0.0

-4.6 8.5

-1.5 3.7 7.6

-1.4

-0.9 8.6 0.5

-1.8 7.0

-0.6 1.8 9.2 1.0

-0.5 11.0 1.1

-1.9 6.8

-1.2

-2.7 8.0

-0.9 1.9 10.6

-0.2

-0.4 8.6

-0.8

-3.3 9.3

-0.4

-3.2 8.0

-2.3 0.4 2.2 2.0 0.6 6.8 0.1

-0.5 10.0 1.7

-1.0 5.5 1.2

-1.1 5.7

-0.6 0.8 5.3 0.8 3.1 6.7 0.3

-2.4 6.1

-0.5 2.2 7.3 2.0 0.0 7.3 0.6

-2.3 7.0

-2.3

-6.0 6.9

-1.9 4.8 10.1 3.1 1.6 7.4 0.0 1.9 6.7 1.1

-0.5 8.1 0.7 Co-60 in Groundwater - 2013

Docket No. 50-3, 50-247, 50-286 Page 50 of 63 Sample 3a Sample 30 Sample 30 Sample 3a plea average Well ID Date Result Error Date Result Error Date Result Error Date Result Error Date Result Error MW-63-112 1/31 2.7 9.6 4/15

-2.1 6.8 7/10

-3.8 7.4 10/21

-0.4 8.3

-0.9 MW-63-121 1/31

-0.3 7.9 4/15 1.9 7.1 7/10 2.2 5.9 10/21

-1.3 6.7 0.6 MW-63-163 1/31

-1.7 8.3 4/15 0.4 7.2 7/10

-0.4 6.4 10/21 0.0 6.9

-0.4 MW-63-174 1/31

-3.7 8.0 4/15

-5.5 8.2 7/10 2.5 7.7 10/21

-2.7 7.9

-2.4 MW-63-18 1/31 1.2 6.6 4/15 2.7 7.6 7/10 0.0 8.7 10/21 4.5 7.6 2.1 MW-63-34 1/31

-2.5 7.0 4/15

-2.1 7.7 7/10 2.4 7.9 10/21 0.4 5.5

-0.5 MW-63-50 1/31

-4.7 10.4 4/15 0.1 5.9 7/10 7.6 7.3 10/21 3.1 7.6 1.6 MW-63-93 1/31 0.1 7.5 4/15

-0.1 8.3 7/10

-1.6 9.1 10/21 4.0 7.2 0.6 MW-66-21 2/22

-1.9 3.5 4/17 3.0 8.3 7/16 1.7 7.6 10/23 0.7 6.3 0.9 MW-66-36 2/22 1.7 9.6 4/17

-3.6 7.8 7/16 1.1 9.7 10/23 1.5 9.5 0.2 MW-67-105 3/5 3.4 7.6 4117

-1.6 11.3 7/16

-0.6 9.5 10(23 0.1 6.9 0.3 MW-67-173 3/5 0.1 7.5 4/17 1.3 9.5 7/16

-0.9 10.4 10/23 2.8 5.6 0.8 MW-67-219 3/5 3.8 7.2 4/17 2.3 8.4 7/16

-1.4 11.0 10/23 1.5 8.2 1.5 MW-67-276 3/5 0.5 7.7 4/17 0.9 7.6 7/16

-2.5 7.2 10/23

-1.0 7.3

-0.5 MW-67-323 3/5

-3.4 9.6 4/17 1.2 8.3 7/16 5.3 9.4 10/23 1.6 7.5 1.1 MW-67-340 3/5 3.9 12.1 4/17 2.0 9.1 7/16 0.3 7.1 10/23

-1.7 8.0 1.1 MW-67-39 3/5

-1.6 4.1 4/17

-1.1 7.7 7/16

-1.6 9.7 10/23

-2.8 6.4

-1.7 MW-68-103 3/4

-0.958 4.86 4/25 1.5 7.7 7/9 1.1 6.1 0.6 MW-68-132 3/4 0.887 6.18 4/25 0.1 7.6 7/9 4.7 8.3 1.9 MW-68-19 3/4 1.23 3.81 4/25

-3.5 9.6 7/9

-5.2 13.0

-2.5 MW-68-29 3/4 0.89 3.57 4/25

-3.0 6.7 7/9 0.4 8.0

-0.5 MW-68-57 3/4 0.772 7.62 4/25

-0.1 10.2 7/9

-4.2 8.1

-1.2 CSS 4/23

-4.2 8.3 11/6 1.9 7.1

-1.1 NCD 2/18 0.0 7.7 4/1 6.4 8.9 6/24 0.3 8.1 9/9 4.7 6.1 12/9 0.6 8.1 2.4 SFDS 2/20 2.9 10.6 4/3 0.1 6.4 6/26

-2.11 4.47 9/11 1.9 5.7 12/11 3.3 7.3 1.2 U3-4D 2/14

-2.0 7.6 4/26 0.9 7.4 7/19 0.846 8.34 10/16 0.0 7.6

-0.1 U3-4S 2/14

-1.2 8.4 4/26 1.2 8.7 7/19 1.5 10.4 10/16

-2.2 7.7

-0.2 U3-T1 2/19 1.9 7.0 5/8 0.7 7.6 7/19

-1.0 8.8 11/6 0.3 6.9 0.5 U3-T2 2/19 2.7 6.1 5/8 1.9 9.3 7/19

-0.6 6.8 11/6 3.8 10.1 1.9 Co-60 in Groundwater - 2013

/

Docket No. 50-3, 50-247, 50-286 Page 51 of 63 Sample 30 Sample 30 Sample 3o Sample 30 Sample 3a average Well ID Date Result Error Date Result Error Date Result Error Date Result Error Date Result Error B-1 times per quarter; no water available for samples B-6 1/29 5.3 10.1 1-2 2/6 1.5 7.8 MH-5 1/30 5.7 6.7 MW-107 MW-111 MW-30-69 2/21 0.9 9.4 MW-30-84 2/21 1.7 6.5 MW-31-49 2/4

-0.4 8.0 MW-31-63 2/4 3.2 9.2 MW-31-85 2/4 2.5 7.0 MW-32-149 2/4

-2.8 7.0 MW-32-173 2/4 2.1 10.9 MW-32-190 2/4

-2.7 8.6 MW-32-59 2/4 0.0 8.0 MW-32-85 2/4

-0.1 7.4 MW-33 MW-35 MW-36-24 2/20 2.5 7.4 MW-36-41 2/20 3.6 7.2 MW-36-52 2/20 3.9 13.1 MW-37-22 2/20 3.2 9.6 MW-37-32 2/20

-0.3 6.3 MW-37-40 2/20 1.5 4.7 MW-37-57 2/20

-0.2 4.8 MW-39-102 MW-39-124 MW-39-183 MW-39-195 MW-39-67 MW-39-84 MW-40-100 3/13 0.0 9.5 MW-40-127 3/13 7.2 10.9 MW-40-162 3/13

-2.1 11.3 4/10 4/24 4/11 5/6 4/23 5/2 5/2 4/22 4/22 4/22 4/22 4/22 4/22 4122 4/22 4/23 4/23 5/1 5/1 5/1 5/1 5/1 5/1 5/1 4/24 4/24 4/24 4/24 4/24 4/24 5/7 5/7 5/7 6.6 7.9

-0.8 9.6 4.3 7.8 0.0 30.9

-2.9 6.5 7.8 13.7 0.4 15.7 3.6 5.6 0.7 8.8

-2.2 8.4

-0.6 6.3 0.8 12.9 3.3 7.5 1.6 8.0 5.2 11.4

-1.1 6.7

-1.0 8.1 0.7 7.6 4.2 6.9 14.1 13.2

-0.9 8.8 3.7 9.9 0.1 9.2 20.7 10.8 1.2 7.4 0.7 5.7

-0.3 6.6

-0.7 5.2 6.7 13.8 3.8 8.3 3.1 7.6 5.4 14.5 0.1 9.3 7/9 3.3 8.8 10/16 2.7 10.9 7/31

-3.1 7.3 11/4

-3.1 7.5 7/12 2.9 8.3 10/24 3.7 7.9 12/12 0.2 6.8 8/30 0.9 4.9 12/4 5.0 9.5 8/30 0.0 11.0 12/4

-0.9 6.8 7/15

-2.3 9.3 10/28 0.2 5.6 7/15 0.4 7.1 10/28 1.7 8.6 7/15

-8.1 7.9 10/28 6.1 12.1 7/15

-0.6 8.6 10/28 5.0 6.3 7/15

-2.0 7.9 10/28

-2.8 10.1 7/15

-2.3 8.0 10/28 7.3 9.7 7/15

-6.6 8.9 10/28 2.2 6.9 7/15

-1.8 6.8 10/28 2.8 11.7 7/31

-2.3 7.3 11/7

-1.3 8.1 7/31

-1.1 9.2 11/7 3.2 6.8 7/31 2.3 7.5 11/7

-1.0 6.7 7/29

-1.2 8.5 11/7 0.0 14.5 7/29

-1.3 7.9 11/7 2.0 5.5 7/29

-2.6 9.8 11/7

-1.5 6.5 7/29

-1.6 7.5 11/7 0.5 8.2 10/29

-1.6 8.8 10/29

-0.8 8.3 10/29 2.7 7.2 10/29 2.1 6.1 10/29 1.5 5.7 10/29

-0.1 8.2 7/26 4.5 6.3 11/11 0.0 8.7 7/26 2.8 8.9 11/11 0.0 7.2 7/26 6.6 10.0 11/11 0.9 6.3 4.4

-1.4 4.1 0.0

-1.3 3.6 0.3 0.3 1.5

-0.4 0.2

-0.5 1.4

-0.7 1.5

-1.1

-1.0

-0.1 2.5 4.8 0.3 1.0

-0.6 4.8

-0.2 0.0 1.2 0.7 4.1 1.9 1.9 3.9 1.4 Cs-137 in Ground Water-2013

Docket No. 50-3, 50-247, 50-286 Page 52 of 63 Sample 30 Sample 3o.

Sample 30 Sample 3a Sample 3a average Well ID Date Result Error Date Result Error Date Result Error Date Result Error Date Result Error MW-40-27 3/13 1.4 4.4 MW-40-46 3/13 8.8 10.4 MW-40-81 3/13 4.9 9.4 MW-41-40 2/13 1.2 6.8 MW-41-63 2/13

-1.9 6.1 MW-42-49 2/12 291000 981 MW-42-78 2/12

-0.6 6.0 MW-43-28 2/19 2.1 7.6 MW-43-62 2/19 0.5 6.0 MW-44-102 2/26 2.0 6.5 MW-44-66 2/26

-0.9 7.8 MW.45-42 2/13 3.7 6.7 MW-45-61 2/13 1.2 5.1 MW-46 1/29 0.7 7.5 MW-47-56 MW-47-80 MW-49-26 1/30 1.2 4.9 MW-49-42 1/30

-0.7 5.3 MW-49-65 1/30 5.2 9.3 MW-50-42 2/11 1.6 8.1 MW-50-66 2/11 0.1 7.9 MW-51-104 3/15 4.2 8.2 MW-51-135 3/15

-4.1 12.3 MW-51-163 3/15 2.7 13.9 MW-51-189 3/15 5.8 14.9 MW-51-40 3/15 0.7 11.2 MW-51-79 3/15 7.9 12.3 MW-52-11 MW-52-1 22 MW-52-162 MW-52-18 MW-52-1 81 MW-52-48 MW-52-64 5/7

-2.3 7.3 5/7 2.0 7.1 5/7 2.6 7.4 4/30 0.7 6.8 4/30

-1.4 7.3 3/11 259000 528 3/11

-0.2 8.3 4/26

-5.3 9.2 4/26

-5.0 11.1 5/3

-3.2 7.1 5/3 1.3 12.9 4/30 2.8 8.0 4/30 0.9 9.3 4110 5.0 9.8 4/26 0.6 7.5 4/26 0.7 6.8 4/11

-1.7 8.0 4/11 10.0 10.6 4/11 2.3 6.3 4/30 0.1 11.5 4/30

-0.6 5.9 5/6 3.5 6.8 5/6 6.8 12.0 5/6

-0.4 9.7 5/6

-1.4 6.9 5/6

-2.1 8.3 5/6

-1.6 7.3 4/24 7.2 8.4 4/18

-4.4 10.5 4/18

-2.9 7.2 4/18

-0.9 7.5 4/18 6.0 11.0 4/18

-2.5 8.8 4118 2.4 7.5 7/26 8.5 12.0 11/11

-3.4 8.3 7/26

-1.2 9.5 11/11

-2.9 6.8 7/26

-1.6 7.1 11/11 0.3 7.7 7/22 0.4 8.3 10/31

-0.4 5.8 7/22

-3.7 8.6 10/31 0.8 17.1 4/29 141000 654 7/18 36500 381.0 10/30 53200 393 4/29

-0.9 7.5 7/18

-0.7 7.4 10/30 1.6 7.0 7/19 3.3 7.4 10/31 0.0 7.0 7/24 2.2 9.6 10/31 1.7 9.8 7/22 0.1 10.3 11/5 0.0 8.4 7/23

-2.3 7.2 11/5 5.5 7.6 7/23

-2.1 7.4 11/5

-1.1 6.1 7/22 1.2 8.3 11/5 3.7 10.1 7/30 6.3 8.5 11/8 1.4 6.0 7/17 1.8 8.3 10/24 7/17

-2.5 10.8 10/24 7/17

-1.1 6.6 10/24 7/18 2.6 12.1 10/24 7/18 1.3 9.8 10/24 7/25 3.1 8.1 11/12 7/25 1.7 8.9 11/12 7/25

-3.1 9.6 11/12 7/25

-3.6 7.5 11/12 7/25

-2.5 7.7 11/12 7/25 2.2 6.6 11/12

-6.1 2.1

-0.3 3.2 4.3 0.0 1.7 0.9 1.0 2.2

-1.2 8.0 9.6 7.4 4.9 9.8 8.8 7.4 7.0 6.3 8.1 9.3 1.0 1.7 1.6 0.5

-1.6 156140

-0.2 0.0

-0.1

-0.3 0.9 0.8 1.7 3.4 0.6 0.7

-1.2 2.2 1.5 1.9 1.3 2.7 1.5 0.0 0.5

-0.4 1.8 7.2

-4.4

-2.9

-0.9 6.0

-2.5 2.4 Cs-137 in Ground Water - 2013

Docket No. 50-3, 50-247, 50-286 Page 53 of 63 Sample 3a Sample 3U Sample 3a Sample 3a Sample 3a average Well ID Date Result Error Date Result Error Date Result Error Date Result Error Date Result Error MW-53-120 2/12 MW-53-82 2/12 MW-54-123 2/11 MW-54-144 2/11 MW-54-173 2/11 MW-54-190 2/11 MW-54-37 2/11 MW-54-58 2/11 MW-55-24 2/6 MW-55-35 2/6 MW-55-54 2/6 MW-56-53 3/11 MW-56-83 3/11 MW-57-11 MW-57-20 MW-57-45 MW-58-26 2/14 MW-58-65 2/14 MW-60-135 217 MW-60-154 217 MW-60-176 2/7 MW-60-35 217 MW-60-53 217 MW-60-72 2/7 MW-62-138 2/5 MW-62-18 2/5 MW-62-182 2/5 MW-62-37 2/5 MW-62-53 2/5 MW-62-71 2/5 MW-62-92 2/5 MW-63-112 1/31 MW-63-121 1/31 MW-63-163 1/31 0.3 5.1 4/29 5.3 6.8 4/29

-4.3 7.5 4/12 0.2 8.5 4/12

-1.2 7.3 4/12 0.0 3.6 4/12

-0.5 8.7 4/12

-3.6 9.7 4/12 5.1 9.5 4/23

-2.4 9.2 4/23 5.0 12.5 4/23

-3.5 4.8 4/29

-1.6 5.3 4/29 4/12 4/12 4/12 1.8 8.4 4/25 1.4 6.0 4/25 1.0 6.3 4/19

-0.3 7.7 4/19 2.4 5.8 4/19 3.7 4.7 4/19

-3.2 6.3 4/19 0.3 5.4 4/19 3.7 9.9 4/16 2.1 7.6 4/16 1.0 8.0 4/16

-3.1 9.2 4/16 0.2 7.0 4/16

-4.4 7.4 4/16 3.0 8.3 4/16 1.5 8.5 4/15 2.6 7.5 4/15 0.9 8.8 4/15 1.6 5.5 8.5 9.8 6.1 8.9 1.8 7.4 1.4 7.2 2.1 6.3 1.2 6.6

-4.3 8.3

-3.3 7.1 2.0 7.7 0.5 4.8

-0.6 5.9

-0.8 7.1 0.0 10.2 0.4 6.8

-0.4 7.7

-1.5 7.1

-4.4 9.8 1.3 7.5

-3.8 8.1 0.0 7.5 1.7 8.3

-4.8 9.7 6.5 10.3 5.7 11.2

-3.4 6.2 0.2 8.2 2.6 10.4

-1.1 10.6 5.3 8.3

-5.1 6.3 0.8 12.0

-0.9 6.5

-3.5 9.5 7/18

-0.9 7.6 10/30 2.9 7/18 4.1 11.2 10/30 2.2 7/23 4.2 10.7 11/1 2.0 7/23 1.6 9.4 11/1

-1.0 7/23

-2.0 11.3 11/1

-0.9 7/23 6.1 8.9 11/1 1.0 7/23

-5.9 9.7 11/1 0.0 7/23

-7.7 9.3 11/1

-2.9 7/17 2.8 8.9 12/12 4.6 7/17 0.0 7.1 12/12

-4.1 7/17 0.0 10.6 12/12

-1.2 11/4

-3.2 11/4

-9.7 11/6 0.6 11/6 1.4 7/12 0.1 7.1 10125

-1.9 7/12

-1.8 10.4 10/25

-1.2 7/12 1.7 8.4 10/25 2.9 7/12 2.8 6.8 10/25 1.7 7/12 0.1 8.1 10/25

-0.6 7/12 2.0 10.1 10/25 1.1 7/11 5.5 8.3 10/22 3.5 7/11

-2.4 10.6 10/22

-7.0 7/11 1.8 9.9 10/22 3.3 7/11 1.0 10.7 10/22

-1.8 7/11 0.5 8.2 10/22 0.8 7/11 0.4 6.7 10/22

-0.2 7/11 2.7 14.1 10/22

-1.1 7/10

-0.1 7.9 10121 3.8 7/10

-0.5 6.5 10/21 3.0 7/10 0.6 6.8 10/21

-0.3 6.6 7.8 7.7 8.0 7.1 6.8 16.9 8.8 7.6 9.2 8.6 11.1 9.9 6.3 10.3 5.7 4.8 5.1 7.5 5.0 5.7 7.2 8.3 8.6 8.0 6.6 7.8 10.7 4.4 10.6 6.0 1.0 5.0 2.0 0.7

-0.7 2.3

-1.3

-4.6 2.3

-1.1 1.1

-2.4

-4.0 0.0 0.4

-0.4 0.3

-0.6 0.1

-1.8 1.8 2.5

-2.1 2.5 4.6

-2.7 1.6

-0.3 0.1 0.3

-0.1 1.5 1.1

-0.6 Cs-137 in Ground Water - 2013

Docket No. 50-3, 50-247, 50-286 Page 54 of 63 Sample 30 Sample Well ID Date Result Error Date MW-63-174 1/31

-2.0 7.9 4/15 MW-63-18 1/31

-0.9 9.1 4/15 MW-63-34 1/31 3.1 6.8 4/15 MW-63-50 1/31 0.5 6.9 4/15 MW-63-93 1/31 1.6 7.7 4/15 MW-66-21 2/22 1.9 7.2 4/17 MW-66-36 2/22 0.7 3.3 4117 MW-67-105 3/5 6.6 9.4 4/17 MW-67-173 3/5 0.6 7.9 4/17 MW-67-219 3/5 7.7 7.9 4/17 MW-67-276 3/5

-1.7 7.6 4/17 MW-67-323 3/5

-4.2 8.2 4/17 MW-67-340 3/5

-6.1 9.5 4/17 MW-67-39 3/5 1.6 3.8 4/17 MW-68-103 3/4

-3.2 5.8 4/25 MW-68-132 3/4

-3.8 7.2 4/25 MW-68-19 3/4 0.2 3.7 4/25 MW-68-29 3/4

-2.8 3.7 4/25 MW-68-57 3/4 2.0 4.7 4/25 CSS 4/23 NCD 2/18 22000 199 4/1 SFDS 2/20 6.7 9.4 4/3 U3-4D 2/14 0.7 7.5 4/26 U3-4S 2/14 1.0 8.4 4/26 U3-T1 2/19

-0.5 5.8 5/8 U3-T2 2/19

-6.3 7.1 5/8 3a Sample 3a Sample 30 Sample 3a average Result Error Date Result Error Date Result Error Date Result Error 1.6 8.4 7/10

-0.3 7.4 10/21

-1.1 7.4

-0.4

-3.3 10.8 7/10

-1,3 9.0 10/21 1.2 7.0

-1.1 7.6 10.9 7/10

-0.6 7.9 10/21

-1.5 7.5 2.1

-0.2 7.8 7/10 3.4 12.1 10/21

-4.5 8.9

-0.2 0.4 7.3 7/10 0.1 9.5 10/21 1.3 7.4 0.8 1.2 6.9 7/16

-0,8 9.4 10/23 4.1 7.1 1.6 8.0 8.8 7/16 0.0 8.8 10/23

-4.7 8.4 1.0

-0.8 12.1 7/16

-3.2 9.1 10/23

-0.6 7.2 0.5

-0.7 8.6 7/16 2.8 8.0 10/23

-1.8 5.6 0.2 2.5 10.1 7/16

-5,2 9.1 10/23 2.9 8.9 2.0 1.9 6.8 7/16

-1.2 9.0 10/23

-0.8 8.1

-0.5 1.6 7.2 7/16

-0.2 8.8 10/23 4.1 7.3 0.3 4.7 9.9 7/16

-1.1 6.5 10/23 3.1 9.7 0.2 6.0 9.8 7/16 1.7 7.8 10/23 4.1 10.1 3.4 4.2 8.3 7/9 5.2 8.0 2.1

-5.1 9.8 7/9

-3.7 8.3

-4.2 2.4 8.2 7/9 4.2 10.8 2.3 0.7 11.6 7/9

-2.0 7.1

-1.3

-5.1 10.5 7/9

-0.3 7.1

-1.1 5.4 6.2 11/6 3.9 7.6 4.6 20900 254 6/24 13200 106 9/9 12700 150 12/9 11700 180 16100 5.5 7.5 6/26 6.4 5.5 9/11 5.8 7.0 12/11 2.3 8.4 5.3 2.2 8.3 7/19 1.6 9.0 10/16 5.1 7.1 2.4

-1.7 10.2 7/19 4.9 9.8 10/16

-0.8 6.7 0.8 1.1 7.2 7/19 0.4 7.0 11/6 1.0 6.9 0.5 0.9 9.2 7/19

-2.3 9.7 11/6 1.8 8.6

-1.5 Cs-137 in Ground Water - 2013

Docket No. 50-3, 50-247, 50-286 Page 55 of 63 Sample 3a Sample 3a Sample 30 Sample 3a Sample 3o average Well ID Date Result Error Date Result Error Date Result Error Date Result Error Date Result Error B-1 times per quarter; no water available for samples B-6 1-2 MH-5 MW-1 07 MW-111 MW-30-69 MW-30-84 MW-31-49 MW-31-63 MW-31-85 MW-32-149 MW-32-173 MW-32-190 MW-32-59 MW-32-85 MW-33 MW-35 MW-36-24 MW-36-41 MW-36-52 MW-37-22 MW-37-32 MW-37-40 MW-37-57 MW-39-102 MW-39-124 MW-39-183 MW-39-195 MW-39-67 MW-39-84 MW-40-100 MW-40-127 MW-40-162 1/29 229 369 2/6 99 351 1/30 1080 450 2/21 75500 2480 2/21 6220 786 2/4 807 426 2/4 20000 1270 2/4 4480 666 2/4 228 366 2/4 301 372 2/4 1230 462 2/4 10300 930 2/4 11100 1070 2/20 207 390 2/20 5410 735 2/20 3900 657 2/20 3150 615 2/20 3470 648 2/20 5150 747 2/20 4740 708 3/13

-55 342 3/13 44 354 3/13 18 351 4/10 4/24 4/11 5/6 4/23 5/2 5/2 4/22 4/22 4/22 4/22 4/22 4/22 4/22 4/22 4/23 4/23 5/1 5/1 5/1 5/1 5/1 5/1 5/1 4124 4/24 4/24 4/24 4/24 4/24 5/7 5/7 5/7

-42 363

-186 342 747 432 48 324 901 429 70300 2420 6200 774 18100 1340 15100 1160.

4060 675 312 375 330 375 1260 477 27800 1650 9150 984 3490 672 831 456

-56 420 4940 789 3420 684 2830 648 2320 624 4440 753 3960 717 150 351 370 387 143 375 340 384 321 390 208 384 108 357 50 348 66 348 7/9 233 321 7/31 28 288 7/12 1270 429 8/30 57000 2210 8/30 5030 756 7/15 18500 1230 7/15 11700 1010 7/15 3160 609 7/15

-123 369 7/15 33 390 7/15 808 450 7/15 35300 1680 7/15 9150 906 7/31 170 393 7/31 3780 654 7/31 4410 690 7/29 1820 528 7/29 1700 531 7/29 3260 627 7/29 3490 639 7/26 41 384 7/27 132 396 7/28 231 405 10/16 82 354 125 11/4 60 354 0

11/11 103 396 800 48 12/12 2870 594 1886 12/4 54600 2080 64350 12/4 4660 672 5528 10/28 11800 1020 12302 10/28 33200 1770 20000 10/28 2460 564 3540 10/28 230 378 162 10/28 228 384 223 10/28 1220 465 1130 10/28 20300 1310 23425 10/28 7440 828 9210 3490 831 11/7 3

354 81 11/7 4030 660 4540 11/7 4440 690 4043 11/7 1150 444 2238 11/7 1530 492 2255 11/7 3240 612 4023 11/7 3300 615 3873 10/29 73 363 112 10/29 68 360 219 10/29

-85 342 29 10/29 904 381 622 10/29 254 378 288 10/29

-144 375 32 11/11 210 321 76 11/11 106 393 83 11/11 260 324 144 H-3 in Ground Water - 2013

Sample 3a Well ID Date Result Error MW-40-27 3/13 65 363 MW-40-46 3/13 145 363 MW-40-81 3/13

-2 324 MW-41-40 2/13 452 402 MW-41-63 2/13 367 393 MW-42-49 2/12 663 423 MW-42-78 2/12 311 378 MW-43-28 2/19 164 369 MW-43-62 2119 53 354 MW-44-102 2/26 432 405 MW-44-66 2/26 181 366 MW-45-42 2/13 7270 825 MW-45-61 2/13 1670 501 MW-46 1/29 2030 516 MW-47-56 MW-47-80 MW-49-26 1/30 4080 708 MW-49-42 1/30 6320 843 MW-49-65 1/30 5660 813 MW-50-42 2/11 847 432 MW-50-66 2/11 5600 729 MW-51-104 3/15 77 333 MW-51-135 3/15 30 333 MW-51-163 3/15 83 324 MW-51-189 3/15 65 330 MW-51-40 3/15 130 339 MW-51-79 3/15 76 333 MW-52-11 MW-52-122 MW-52-162 MW-52-18 MW-52-181 MW-52-48 MW-52-64 Sample Date 5/7 5/7 5/7 4/30 4/30 3/11 3/11 4/26 4/26 5/3 5/3 4/30 4/30 4/10 4/26 4/26 4/11 4/11 4/11 4/30 4/30 5/6 5/6 5/6 5/6 5/6 5/6 4/24 4/18 4/18 4/18 4/18 4/18 4/18 Result 265 151 263 1540 566 441 297 206 235 543 372 6360 1650 2560 1200 8970 3860 5050 5210 282 5390

-8

-58

-83

-50 75

-48 363 192 439 252 276 319 85 3a Sample 3cr Sample 3cr Sample Error Date Result Error Date Result Error Date 354 7/29 33 381 11/11 339 7/30

-134 375 11/11 351 7/31 50 393 11/11 510 8/1 916 477 10/31 408 8/2 616 441 10/31 396 4/29 478 369 8/3 442 468 10/30 411 4/29 266 375 8/4 425 462 10/30 447 8/5 242 408 10/31 372 8/6 268 405 10/31 393 8/7 561 441 11/5 375 8/8 163 414 11/5 858 8/9 2600 513 11/5 570 8/10 597 366 11/5 570 8/11 2030 573 11/8 534 978 678 759 780 372 804 342 336 333 339 351 327 381 363 387 363 369 381 342 Docket No. 50-3, 50-247, 50-286 Page 56 of 63 3a average Result Error 270 327 158 301 321 116 282 333 148 1920 576 1207 612 354 540 2180 528 841 424 441 345 333 414 236 129 393 171 646 363 546 422 423 285 976 480 4302 401 345 1080 1910 471 2133 1200 8970 3120 573 3708 4210 645 5095 4300 642 5103 112 414 373 3540 681 4723

-200 390 22 99 417 101

-325 378

-5

-250 387 12

-19 408 115

-294 375

-9 363 192 439 252 276 319 85 7/17 7/17 7/17 7/18 7/18 7/25 7/25 7/25 7/25 7/25 7/25 3770 690 10/24 4800 762 10/24 5240 792 10/24 252 408 10/24 4360 729 10/24 221 405 11/12 334 420 11/12 305 429 11/12 284 411 11/12 273 411 11/12 228 399 11/12 H-3 in Ground Water - 2013

Docket No. 50-3, 50-247, 50-286 Page 57 of 63 Sample Well ID Date MW-53-120 MW-53-82 MW-54-123 MW-54-144 MW-54-173 MW-54-190 MW-54-37 MW-54-58 MW-55-24 MW-55-35 MW-55-54 MW-56-53 MW-56-83 MW-57-11 MW-57-20 MW-57-45 MW-58-26 MW-58-65 MW-60-135 MW-60-154 MW-60-176 MW-60-35 MW-60-53 MW-60-72 MW-62-138 MW-62-18 MW-62-182 MW-62-37 MW-62-53 MW-62-71 MW-62-92 MW-63-112 MW-63-121 MW-63-163 2/12 2/12 2/11 2/11 2/11 2/11 2/11 2/11 2/6 2/6 2/6 3/11 3/11 2/14 2/14 2/7 2/7 2/7 2/7 2/7 2/7 2/5 2/5 2/5 2/5 2/5 2/5 2/5 1/31 1/31 1/31 30 Sample Result Error Date 7000 807 4/29 686 417 4/29 8170 870 4/12 7250 837 4/12 5420 735 4/12 8750 912 4/12 7200 825 4/12 7530 840 4/12 1490 477 4/23 1170 438 4/23 6140 762 4/23 836 438 4/29 7570 834 4/29 4/12 4/12 4/12 928 447 4/25 1730 507 4/25 161 378 4/19 477 399 4/19 1200 474 4/19 240 378 4/19 108 366 4/19 166 372 4/19 4110 660 4/16 326 378 4/16 821 429 4/16 356 387 4/16 478 396 4/16 1340 471 4/16 1340 465 4/16 1890 546 4/15 2820 609 4/15 583 402 4/15 3a Result Error 7570 918 862 516 7340 891 5820 813 5900 771 7570 852 6160 831 7130 882 1380 510 1560 534 5100 798 2560 600 6530 879 3320 666 4740 753 5020 765 1440 501 1540 531

-76 351 500 399 1060 459 188 378

-167 345

-42 363 3790 648 207 381 921 450 426 396 569 420 1790 522 1700 504 1280 450 2430 534 642 411 Sample Date Result 30 Sample 30 Sample 30 Error Date Result Error Date Result Error 7/18 6650 867 10/30 5540 786 7/18 1040 486 10/30 2260 597 7/23 8340 951 11/1 6960 858 7/23 6250 846 11/1 5180 759 7/23 6180 840 11/1 5250 774 7/23 5980 822 11/1 4310 717 7/23 6210 840 11/1 5840 801 7/23 7860 918 11/1 7010 861 7/17 1310 516 12/12 1070 417 7/17 1240 507 12/12 1260 435 7/17 4870 768 12/12 4900 684 11/4 1160 510 11/4 3510 681 average 6690 1212 7703 6125 5688 6653 6353 7383 1313 1308 5253 1519 5870 3320 4740 5020 893 1437 203 538 1133 190 63 73 3483 220 1171 451 714 1743 1690 1490 2423 798 7/12 7/12 7/12 7/12 7/12 7/12 7/11 7/11 7/11 7/11 7/11 7/11 7/11 7/10 7/10 7/10 371 417 749 459 1080 492 324 417 251 405

-92 372 3100 573

-15 354 1290 459 406 384 823 426 1890 498 1730 486 1270 453 2460 537 1080 441 11/6 11/6 10/25 10/25 10/25 10/25 10/25 10/25 10/22 10/22 10/22 10/22 10/22 10/22 10/22 10/21 10/21 10/21 312 429 1040 504 358 384 427 387 1190 468 6

369 61 375 261 366 2930 654 362 396 1650 540 615 429 984 474 1950 561 1990 573 1520 534 1980 570 885 462 H-3 in Ground Water-2013

Docket No. 50-3, 50-247, 50-286 Page 58 of 63 Well ID MW-63-174 MW-63-18 MW-63-34 MW-63-50 MW-63-93 MW-66-21 MW-66-36 MW-67-105 MW-67-173 MW-67-219 MW-67-276 MW-67-323 MW-67-340 MW-67-39 MW-68-103 MW-68-132 MW-68-19 MW-68-29 MW-68-57 CSS NCD SFDS U3-4D U3-4S U3-T1 U3-T2 Sample Date 1/31 1/31 1/31 1/31 1/31 2/22 2/22 3/5 3/5 3/5 3/5 3/5 3/5 3/5 3/4 3/4 3/4 3/4 3/4 2/18 2/20 2/14 2/14 2/19 2/19 3o Sample Result Error Date 966 456 4/15 331 387 4/15 310 384 4/15 418 387 4/15 738 405 4/15

-16 363 4/17 2300 537 4/17 3190 603 4/17 479 363 4/17 1030 453 4/17 929 465 4/17 317 405 4/17 608 435 4/17 1540 483 4/17 1440 507 4/25 1760 519 4/25 7520 831 4/25 13100 1050 4/25 5870 771 4/25 4/23 1520 669 4/1 159 390 4/3 643 426 4/26 783 426 4/26 1890 525 5/8 4350 666 5/8 3U Sample 3a Sample 3a Sample 30 Result Error Date Result Error Date Result Error Date Result Error 912 441 7/10 1220 450 10/21 986 480 186 375 7/10 325 375 10/21 344 405 170 369 7/10 375 381 10/21 247 372 202 378 7/10 416 387 10/21 523 423 448 387 7/10 732 411 10/21 673 432 162 345 7/16 148 360 10/23 453 447 2020 528 7/16 1950 504 10/23 1160 525 2460 564 7/16 3210 573 10/23 3000 657 658 426 7/16 582 354 10/23 640 411 979 447 7/16 958 399 10/23 1140 453 766 435 7/16 965 396 10/23 860 426 261 393 7/16 557 366 10/23 428 390 470 411 7/16 515 357 10/23 408 384 1070 462 7/16 863 423 10/23 1210 495 average 1021 297 276 390 648 187 1858 2965 590 1027 880 391 500 1171 2007 2253 5657 11003 7160 3525 2386 285 1026 1196 2448 4108 1990 555 2300 597 3910 699 12300 1150 8020 939 1850 534 2660 600 6/24 1380 528

-42 360 6/26 588 351 1010 468 1060 477 2780 627 5850 828 719 2590 534 7/9 2700 543 7/9 5540 720 7/9 7610 816 7/9 7590 816 11/6 9/9 3120 645 12/9 9/11 529 456 12/11 7/19 1080 414 10/16 7/19 1140 417 10/16 7/19 2130 498 11/6 7/19 3940 621 11/6 5200 780 3250 591 190 360 1370 474 1800 510 2990 591 2290 588 H-3 in Ground Water - 2013

Docket No. 50-3, 50-247, 50-286 Page 59 of 63 Sample 30 Sample 30 Sample 30 Sample 30 Sample 3o average Well ID Date Result Error Date Result Error Date Result Error Date Result Error Date Result Error MW-42-49 2/12 MW-42-78 2/12 MW-49-26 1/30 MW-49-42 1/30 MW-49-65 1/30 MW-50-42 2/11 MW-50-66 2/11 MW-53-120 2/12 MW-53-82 2/12 MW-54-123 2/11 MW-54-144 2/11 MW-54-173 2/11 MW-54-190 2/11 MW-54-37 2/11 MW-54-58 2/11 MW-55-24 2/6 MW-55-35 2/6 MW-55-54 2/6 MW-57-11 MW-57-20 MW-57-45 MW-60-53 2/7 MW-66-21 2/22 MW-66-36 2/22 MW-67-105 3/5 MW-67-173 3/5 MW-67-219 3/5 MW-67-276 3/5 MW-67-323 3/5 MW-67-340 3/5 MW-67-39 3/5 CSS NCD 2/18 SFDS 2/20 1880 63 3/11 1330.0 51.0

-4.7 17.9 3/11 3.9 19.7 1.2 18.9 4/11 15.7 17.0 1.5 18.8 4/11 7.7 18.4 0.0 17.4 4/11 1.6 14.8

-4.5 18.2 4/30 6.8 16.4 5.2 18.8 4/30 9.1 16.8 8.9 19.9 4/29 10.1 16.8 7.4 18.8 4/29 18.7 20.8 0.5 14.9 4/12 10.5 15.0

-2.6 18.7 4/12 9.6 16.6 5.5 14.0 4/12 2.7 16.1 7.5 19.7 4/12 1.0 16.9 0.5 14.1 4/12 0.0 12.2

-3.7 13.8 4/12

-4.4 15.2

-8.6 17.0 4/23

-5.3 16.4 2.9 17.9 4/23

-1.3 15.9

-9.6 16.9 4/23 2.4 16.5 4/12 0.6 15.4 4/12

-8.0 15.2 4/12

-9.9 15.8 9.7 20.6 4/19 5.9 16.8 0.1 14.3 4/17

-8.1 15.5 4.5 17.9 4/17

-4.7 15.1

-1.9 14.3 4/17

-1.1 15.7

-3.5 14.1 4/17

-2.3 12.7 3.2 16.6 4/17 3.7 16.3 5.4 19.4 4/17 10.4 15.6 10.3 18.3 4/17

-2.1 20.3 10.5 19.1 4/17

-6.8 15.3

-1.2 12.7 4/17

-2.3 16.1 4/23 12.5 18.0 438 36 4/1 441.0 34.2 6.3 20.5 4/3

-0.3 16.3 4/29 654.0 40.8 4/29 8.6 15.1 6/24 135.0 23.9 6/26 6.8 20.6 7/18 343.0 28.2 10/30 7/18 0.0 17.5 10/30 7/17 8.9 18.8 10/24 7/17

-0.4 16.1 10/24 7/17 3.8 18.2 10/24 7/18 3.3 19.3 10/24 7/18 1.5 16.2 10/24 7/18 9.4 16.6 10/30 7/18

-2.8 16.1 10/30 7/23 7.7 17.9 11/1 7/23

-1.5 15.7 11/1 7/23 4.7 16.8 11/1 7/23 7.0 16.8 11/1 7/23 8.1 16.5 11/1 7/23

-3.2 16.4 11/1 7/17 4.0 18.3 12/12 7/17

-1.0 18.9 12/12 7/17 2.2 17.8 12/12 7/12 0.8 19.0 10/25 7/16 0.0 18.1 10/23 7/16

-3.1 17.2 10/23 7/16 8.3 17.6 10/23 7/16 6.2 15.8 10/23 7/16

-2.4 16.9 10/23 7/16 4.5 18.8 10/23 7/16

-0.8 14.0 10/23 7/16 15.0 18.5 10/23 7/16 6.3 19.8 10/23 11/6 9/9 189.0 24.2 12/9 518.0 38.4 11.1 13.8 8.8 13.2 4.5 12.9 8.6 13.1 5.8 12.8 5.4 13.1 2.3 16.5 1.3 12.9 8.0 13.8 0.0 13.4

-2.8 13.4 3.0 14.8 6.5 13.2 5.4 13.1 12.2 18.6

-2.3 18.6 4.4 18.5 8.8 18.1 1.4 20.3 1.2 13.4 1.5 13.4 0.8 14.5 7.7 16.2 3.0 15.7 12.1 15.6

-2.5 16.4

-4.1 16.8 10.0 14.8 328.0 32.7 945 4

9 3

4 3

5 8

6 7

1 3

5 4

-1 1

0 0

1

-8

-10 6

-2

-1 2

0 3

6 5

4 0

11 306 4

9/11 1.8 16.9 12/11 4.8 17.4 Ni-63 in Groundwater - 2013

Docket No. 50-3, 50-247, 50-286 Page 60 of 63 Sample

3.

Sample 3a Sample 3o Sample

3.

Sample 3o average Well ID Date Result Error Date Result Error Date Result Error Date Result Error Date Result Error B-1 times per quarter; no water available for samples B-6 1/29

-0.3 1.2 4/10

-0.9 1.2 7/9 1.4 1.9 10/16 1.1 1.8 0.3 1-2 2/6 0,9 1.5 4/24 1.9 1.8 7/31 0.3 1.7 11/4 0.8 1.8 1.0 MH-5 1/30 0.0 1.3 4/11 1.6 1.8 7/12 0.1 1.5 10/24

-0.3 1.6 0.4 MW-107 MW-111 MW-30-69 2/21 1.5 1.7 MW-30-84 2/21 1.3 1.6 MW-31-49 2/4 1.2 1.7 MW-31-63 2/4 0.6 1.7 MW-31-85 214 0.2 1.4 MW-32-149 2/4 1.0 1.5 MW-32-173 2/4 0.4 1.5 MW-32-190 2/4 0.4 1.5 MW-32-59 2/4 0.4 1.4 MW-32-85 2/4 0.4 1.5 MW-33 MW-35 MW-36-24 2/20 2.1 2.2 MW-36-41 2/20 6.2 2.0 MW-36-52 2/20 4.5 2.1 MW-37-22 2/20 8.8 2.2 MW-37-32 2/20 12.6 2.8 MW-37-40 2/20 18.8 3.1 MW-37-57 2/20 16.8 2.8 MW-39-102 MW-39-124 MW-39-183 MW-39-195 MW-39-67 MW-39-84 MW-40-100 3/13 0.2 1.7 MW-40-127 3/13 1.1 1.7 5/6 1.7 1.9 4/23 1.4 1.8 5/2 0.6 1.5 5/2 0.4 1.6 4/22 0.4 1.5 4/22

-0.7 1.2 4/22 0.4 1.6 4/22

-0.1 1.6 4/22 1.0 1.7 4/22

-0.5 1.6 4/22

-0.3 1.7 4/22

-0.8 1.5 4/23 0.1 1.5 4/23 0.7 1,3 5/1 1.0 1.8 5/1 5.6 2.3 5/1 2.6 2.0 5/1 8.5 2.9 5/1 8.3 2.8 5/1 15.7 3.7 5/1 12.8 2.6 4/24 0.3 1.5 4/24 0.7 1.6 4/24 0.9 1.5 4/24 1.7 1.8 4/24 1.2 1.8 4/24 1.1 1.4 5/7

-1.0 1.3 5/7 1.7 1.9 1.7 12/12 0.1 1.2 0.8 8/30 0.8 1.8 12/4

-0.5 1.3 0.6 8/30 0.6 1.7 12/4 1.0 1.8 0.8 7/15 0.7 1.7 10/28

-0.3 1.1 0.5 7/15

-0.4 1.2 10/28 0.1 1.0

-0.1 7/15

-0.6 1.1 10/28 0.0 1.4 0.0 7/15

-0.5 1.1 10/28

-0.5 1.0 0.0 7/15 0.3 1.5 10/28

-0.7 0.8 0.3 7/15 0.0 1.7 10/28 0.0 1.2 0.0 7/15 1.0 1.5 10/28

-1.0 1.1 0.0 7/15

-0.2 1.1 10/28 0.6 1.2 0.0 0.1 0.7 7/31 0.6 1.1 11/7 0.6 1.3 1.0 7/31 3.0 1.9 11/7 2.5 1.7 4.3 7/31 2.7 1.8 11/7 4.7 2.1 3.6 7/29 4.6 2.2 11/7 11.2 2.8 8.3 7/29 13.7 3.2 11/7 16.3 3.1 12.7 7/29 13.9 3.2 11/7 13.1 2.7 15.4 7/29 18.8 4.1 11/7 19.2 3.6 16.9 10/29 2.0 1.9 1.1 10/29

-1.0 1.3

-0.1 10/29

-1.0 1.5

-0.1 10/29 0.2 1.5 0.9 10/29 0.5 1.7 0.9 10/29 1.6 1.9 1.3 7/26 0.1 1.4 11/11

-0.1 1.0

-0.2 7/26 0.5 1.7 11/11

-1.0 1.0 0.6 Sr-90 in Ground Water - 2013

S S

Docket No. 50-3, 50-247, 50-286 Page 61 of 63 Sample 3a Sample 30 Sample 30 Sample 3c Sample 30 average Date ResultDError a

ResutErr Date Well ID Date Result Error Date Result Eesult Error Result Error AW-40-162 3/13 0.2 1.6 5/7

-1.1 1.5 7/26

-0.8 1.5 11/11

-0.4 0.7

-0.5 MW-40-27 3/13 1.2 1.8 5/7

-1.5 1.6 7/26 0.4 1.6 11/11

-0.4 1.1

-0.1 MW-40-46 3/13 0.7 1.6 5/7 1.6 1.8 7/26 0.6 1.7 11/11

-0.6 1.0 0.6 MW-40-81 3/13 0.8 1.6 5/7

-0.3 1.6 7/26

-0.3 1.4 11/11

-1.0 1.0

-0.2 MW-41-40 2/13 5.9 2.3 4/30 3.8 2.3 7/22 1.3 1.5 10/31 1.7 1.9 3.2 MW-41-63 2/13 5.8 2.3 4/30 5.5 2.4 7/22 4.4 2.0 10/31 2.5 1.5 4.6 MW-42-49 2/12 74.7 7.4 3/11 28.2 4.3 4/29 18.3 3.5 7/18 20.8 3.1 10/30 20.8 4.2 32.6 MW-42-78 2/12

-0.8 1.4 3/11 0.4 1.7 4/29 0.0 1.4 7/18

-0.5 1.1 10/30

-0.2 1.6

-0.2 MW-43-28 2/19 0.3 1.7 4/26

-0.3 1.3 7/19

-0.2 1.5 10/31

-1.0 1.4

-0.3 MW-43-62 2/19 0.6 1.2 4/26

-0.2 1.4 7/24

-0.1 1.4 10/31

-0.8 1.4

-0.1 AW-44-102 2/26

-0.1 1.6 5/3 0.0 1.6 7/22 0.3 1.4 11/5

-0.4 0.9

-0.1 MW-44-66 2/26 0.3 1.7 5/3

-1.0 1.3 7/23

-0.6 1.2 11/5 0.1 1.1

-0.3 MW-45-42 2/13 0.8 1.7 4/30 0.5 1.5 7/23 1.4 1.7 11/5 0.3 1.3 0.8 MW-45-61 2/13

-0.8 1.4 4/30 0.2 1.0 7/22 1.3 1.8 11/5

-0.4 1.0 0.1 MW-46 1/29 1.2 1.8 4/10

-0.1 1.6 7/30 1.6 1.7 11/8

-0.4 0.9 0.6 MW-47-56 4/26

-0.7 0.8

-0.7 MW-47-80 MW-49-26 1/30 14.8 3.2 MW-49-42 1/30 14.1 3.1 MW-49-65 1/30 7.4 2.9 MW-50-42 2/11 6.5 2.8 MW-50-66 2/11 14.8 3.8 MW-51-104 3/15

-0.1 1.6 MW-51-135 3/15

-0.1 1.7 MW-51-163 3/15 1.0 1.8 MW-51-189 3/15 0.1 1.7 MW-51-40 3/15

-0.5 1.3 MW-51-79 3/15 0.4 1.7 MW-52-11 MW-52-122 MW-52-162 MW-52-18 MW-52-181 4/26 1.7 1.7 4/11 12.9 3.3 4/11 10.4 2.6 4/11 7.7 2.9 4/30 5.4 2.4 4/30 18.0 3.9 5/6 1.5 1.6 5/6 0.1 1.7 5/6 0.7 1.5 5/6 0.2 1.6 5/6 0.0 1.5 5/6 1.1 1.8 4/24

-0.6 1.6 4/18 1.6 1.8 4/18 0.2 1.6 4/18 0.5 1.7 4/18

-0.7 1.3 1.7 7/17 10.9 2.7 10/24 13.4 2.2 13.0 7/17 13.0 2.9 10/24 13.9 3.1 12.9 7/17 7.2 2.4 10/24 6.4 2.3 7.2 7/18 1.1 1.7 10/24 7.8 2.8 5.2 7/18 19.2 3.2 10/24 23.8 4.0 19.0 7/25 1.0 1.6 11/12 1.4 1.8 0.9 7/25 0.7 1.2 11/12 0.6 1.3 0.3 7/25

-0.4 1.1 11/12

-0.3 0.9 0.3 7/25

-0.4 1.3 11/12 0.5 1.6 0.1 7/25

-0.3 1.4 11/12

-1.0 1.1

-0.4 7/25

-0.7 1.4 11/12 0.3 1.1 0.3

-0.6 1.6 0.2 0.5

-0.7 Sr-90 in Ground Water - 2013

Docket No. 50-3, 50-247, 50-286 Page 62 of 63 M

M M

Sample 3a Sample 3a Sample 3o Sample Well ID Date Result Error Date Result Error Date Result Error Date AW-52-48 4/18 0.5 1.7 AW-52-64 4/18 1.3 1.8 IW-53-120 2/12 34.6 4.5 4/29 28.4 5.0 7/18 AW-53-82 2/12

-1.0 1.6 4/29

-0.2 1.3 7/18 IW-54-123 2/11 2.6 2.0 4/12 0.6 1.5 7/23 IW-54-144 2/11 8.3 2.4 4/12 4.9 2.2 7/23 1W-54-173 2/11 4.8 1.9 4/12 3.8 2.1 7/23 IW-54-190 2/11 12.4 3.2 4/12 13.4 3.4 7/23 AW-54-37 2/11 3.5 1.9 4/12 3.2 1.9 7/23 AW-54-58 2/11 1.4 1.8 4/12 0.4 1.6 7/23 AW-55-24 2/6 12.9 3.2 4/23 26.0 4.7 7/17 AW-55-35 2/6 11.3 2.9 4/23 20.4 4.0 7/17 AW-55-54 2/6 11.9 3.4 4/23 15.6 3.2 7/17 AW-56-53 3/11 0.1 1.6 4/29 0.3 1.7 MW-56-83 3/11 1.2 1.8 4/29 0.5 1.7 MW-57-11 4/12 34.0 5.1 MW-57-20 4/12 1.5 1.8 3o Sample 30 average Result Error Date Result Error 0.5 MW-57-45 MW-58-26 2/14 MW-58-65 2/14 MW-60-135 2/7 MW-60-154 2/7 MW-60-176 2/7 MW-60-35 2/7 MW-60-53 2/7 MW-60-72 217 MW-62-138 2/5 MW-62-18 2/5 MW-62-182 2/5 MW-62-37 2/5 MW-62-53 2/5 MW-62-71 2/5 MW-62-92 2/5 1.4

-0.3

-0.1 0.5

-0.5 0.2

-0.6 0.1 3.0 1.1

-0.1 0.2 0.6 0.8

-0.1 1.9 1.1 1.1 1.4 1.4 1.6 1.6 1.5 2.0 1.8 1.5 1.5 1.4 1.7 1.6 4/12 4/25 4/25 4/19 4/19 4/19 4/19 4/19 4/19 4/16 4/16 4/16 4/16 4/16 4/16 4/16 1.6 0.1 0.8

-0.7 0.2

-0.9 1.5 0.8 0.5

-0.7 0.0

-0.9 1.1 1.8

-1.2 0.7 1.8 1.0 1.8 1.3 1.6 1.4 1.8 1.7 1.6 1.4 1.5 1.6 1.8 1.9 1.5 1.6 30.1 4.4 10/30 27.4 0.6 1.4 10/30 0.2 1.3 1.7 11/1 0.7 6.9 2.4 11/1 7.0 3.1 1.8 11/1 3.3 11.8 3.3 11/1 11.4 4.8 2.1 11/1 4.3

-1.7 1.3 11/1 1.0 18.1 3.6 12/12 10.5 20.3 3.8 12/12 12.6 18.8 3.7 12/12 15.3 11/4

-0.1 11/4 0.2 11/6

-0.2 11/6

-0.9 0.0 1.5 10/25

-0.1 0.3 1.3 10/25 0.0 0.6 1.3 10/25

-0.8

-0.4 0.9 10/25 0.3

-0.6 1.3 10/25 0.3 0.0 1.4 10/25 0.5 1.1 1.7 10/22 1.8 0.1 1.2 10/22 0.4 0.0 1.0 10/22 0.5 0.5 1.6 10/22

-0.1

-0.2 1.3 10/22 0.0 0.4 1.7 10/22

-0.2

-0.2 1.6 10/22

-0.9 4.1 1.6 1.8 2.8 2.1 3.3 2.3 1.5 3.6 3.3 3.7 0.8 1.3 1.2 1.2 1.0 1.5 1.3 1.1 1.6 1.7 1.9 1.3 1.3 1.4 1.5 1.5 1.4 1.3 30.1

-0.1 1.3 6.8 3.8 12.3 3.9 0.3 16.9 16.2 15.4 0.1 0.6 34.0 1.5 1.6 0.4

-0.1

-0.3 0.2

-0.4 0.4 0.0 0.3 1.3 0.4

-0.1 0.4 0.5 0.0

-0.1 7/12 7/12 7/12 7/12 7/12 7/12 7/11 7/11 7/11 7/11 7/11 7/11 7/11 Sr-90 in Ground Water - 2013

Docket No. 50-3, 50-247, 50-286 Page 63 of 63 Sample

3.

Sample 3a Sample 3a Sample 3a Sample 3a average Well ID Date Res Date Result ErrorDate Date WelI eutiElt E rror Dateror Result Error Dae Result Error Dae Result Error MW-63-112 1/31 MW-63-121 1/31 MW-63-163 1/31 MW-63-174 1/31 MW-63-18 1/31 MW-63-34 1/31 MW-63-50 1/31 MW-63-93 1/31 MW-66-21 2/22 MW-66-36 2/22 MW-67-105 3/5 MW-67-173 3/5 MW-67-219 3/5 MW-67-276 3/5 MW-67-323 3/5 MW-67-340 3/5 MW-67-39 3/5 MW-68-103 3/4 MW-68-132 3/4 MW-68-19 3/4 MW-68-29 3/4 MW-68-57 3/4 CSS NCD 2/18 SFDS 2/20 U3-4D 2/14 U3-4S 2/14 U3-T1 2/19 U3-T2 2/19 0.7 0.0 1.5 0.9

-0.8

-0.4 0.2

-0.1 0.5 10.0 1.5

-1.2 0.8 0.5

-0.9 0.6 9.3 0.7 0.6 1.9 1.2 1.9 55.6 1.9

-1.0 0,5 0.4 0.3 1.8 1.6 1.9 1.5 1.4 1.5 1.4 1.7 1.7 2.5 1.9 1.4 1.8 1.7 1.5 1.7 2.9 1.7 1.7 1.9 1.8 2.0 6.4 2.0 1.4 1.4 1.7 1.6 4/15 4/15 4/15 4/15 4/15 4/15 4/15 4/15 4/17 4/17 4/17 4/17 4/17 4/17 4/17 4/17 4/17 4/25 4/25 4/25 4/25 4/25 4/23 4/1 4/3 4/26 4/26 5/8 5/8

-0.4 1.6 7/10 0.3 1.6 10/21 0.5 1.7 0.3

-1.1 1.4 7/10 0.7 1.7 10/21

-1.2 1.3

-0.4

-1.1 1.3 7/10

-0.1 1.4 10/21

-0.4 1.1 0.0 0.6 1.5 7/10

-1.0 1.5 10/21

-0.3 1.5 0.1

-0.1 1.6 7/10 1.0 1.8 10/21

-0.2 1.4 0.0

-1.0 1.1 7/10

-1.4 1.4 10/21

-0.4 1.3

-0.8

-0.6 1.4 7/10 0.1 1.3 10/21 0.1 1.6

-0.1 0.2 1.6 7/10

-0.2 1.6 10/21 0.7 1.5 0.2 0.1 1.5 7/16 1.2 1.8 10/23 0.4 1.6 0.5 10.0 3.0 7/16 8.6 2.6 10/23 7.3 3.8 9.0 0.3 1.6 7/16 1.6 1.7 10/23 1.8 1.9 1.3 0.0 1.7 7/16 0.7 1.7 10/23

-0.2 1.2

-0.2 1.0 1.7 7/16

-0.5 1.2 10/23

-0.6 1.1 0.2 0.5 1.5 7/16

-0.5 1.6 10/23 0.1 1.2 0.1 0.1 1.6 7/16

-0.5 1.4 10/23

-0.7 0.9

-0.5 0.1 1.6 7/16 1.8 1.9 10/23 0.4 1.2 0.7 9.4 2.8 7/16 5.3 2.3 10/23 10.0 2.6 8.5 0.3 1.7 7/9

-0.5 1.5 0.2 0.7 1.7 7/9 0.6 1.8 0.6 1.6 1.9 7/9 1.3 1.8 1.6 0.1 1.7 7/9 0.2 1.5 0.5

-0.8 1.4 7/9 0.6 1.7 0.6 15.1 3.4 11/6 20.2 3.1 17.7 80.6 7.8 6/24 48.2 4.4 9/9 65.9 5.6 12/9 35.5 5.0 57.2 5.3 2.0 6/26 6.8 2.8 9/11 7.0 2.7 12/11 6.3 2.4 5.5 1.3 1.7 7/19 0.0 1.7 10/16 0.9 1.7 0.3

-0.4 1.0 7/19 1.8 1.9 10/16 0.9 1.7 0.7 1.1 1.8 7/19 0.9 1.8 11/6 0.1 1.6 0.6

-0.4 1.6 7/19 0.8 1.7 11/6 1.1 1.8 0.5 Sr-90 in Ground Water - 2013

NL-14-039, Annual Radioactive Effluent Release Report

Contents

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NL-14-039, Annual Radioactive Effluent Release Report

Text

SUBJECT:

Dear Sir or Madam:

Enclosure:

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