Text

Annual Radiological Environmental Operating Report for 2014
	ML15132A129
Person / Time
Site:	Arkansas Nuclear
Issue date:	05/12/2015
From:	Pyle S; Entergy Operations
To:	; Document Control Desk, Office of Nuclear Reactor Regulation
References
	0CAN051502
	Download: ML15132A129 (111)
	v • d • e

Entergy Operations, Inc.

1448 S.R. 333 Russellville, AR 72802 Tel 479-858-4704 Stephenie L. Pyle Manager, Regulatory Assurance Arkansas Nuclear One 0CAN051502 May 12, 2015 U.S. Nuclear Regulatory Commission Attn: Document Control Desk Washington, DC 20555

SUBJECT:

Annual Radiological Environmental Operating Report for 2014 Arkansas Nuclear One - Units 1 and 2 Docket Nos. 50-313 and 50-368 License Nos. DPR-51 and NPF-6

REFERENCE:

Entergy letter dated April 28, 2015, Annual Radioactive Effluent Release Report for 2014 (0CAN041504)

Dear Sir or Madam:

In accordance with Arkansas Nuclear One (ANO), Unit 1 Technical Specification (TS) 5.6.2 and Unit 2 TS 6.6.2, the submittal of an annual radiological environmental operating report for the previous year is required by May 15 of each year. The subject ANO report for the calendar year 2014 is enclosed.

This report fulfills the reporting requirements of the TSs referenced above.

The radionuclides detected by the radiological environmental monitoring program during 2014 were significantly below the regulatory limits. The operation of the ANO station during 2014 had no harmful radiological effects nor resulted in any irreversible damage to the local environment.

Based on ANOs review, no environmental samples from the monitoring program equaled or exceeded the reporting levels for radioactivity concentration due to ANO effluents when averaged over any calendar quarter. A map of all sampling locations and a corresponding table providing the respective distances and directions from the reactor building is included in the Offsite Dose Calculation Manual (ODCM) submitted as part of the referenced Annual Radioactive Effluent Release Report.

0CAN051502 Page 2 of 2 This letter contains no new commitments.

If you have any questions or require additional information, please contact me.

Sincerely, ORIGINAL SIGNED BY STEPHENIE L. PYLE SLP/rwc

Enclosure:

Annual Radiological Environmental Operating Report for 2014 cc: Mr. Marc L. Dapas Regional Administrator U. S. Nuclear Regulatory Commission Region IV 1600 East Lamar Boulevard Arlington, TX 76011-4511 NRC Senior Resident Inspector Arkansas Nuclear One P. O. Box 310 London, AR 72847 U. S. Nuclear Regulatory Commission Attn: Ms. Andrea E. George MS O-8B1 One White Flint North 11555 Rockville Pike Rockville, MD 20852 Mr. Bernard R. Bevill Arkansas Department of Health Radiation Control Section 4815 West Markham Street Slot #30 Little Rock, AR 72205

Enclosure to 0CAN051502 Annual Radiological Environmental Operating Report for 2014

Enclosure to 0CAN051502 Page 1 of 108 Table of Contents Summary.................................................................................................................................. 2 1.0 Introduction .................................................................................................................... 7 1.1 Radiological Environmental Monitoring Program ................................................ 7 1.2 Pathways Monitored ............................................................................................ 7 1.3 Land Use Census ................................................................................................ 7 2.0 Interpretation and Trends of Results ............................................................................. 18 2.1 Air Particulate and Radioiodine Sample Results ................................................. 18 2.2 Thermoluminescent Dosimetry (TLD) Sample Results ....................................... 18 2.3 Water Sample Results ........................................................................................ 18 2.4 Sediment Sample Results ................................................................................... 20 2.5 Milk Sample Results ............................................................................................ 21 2.6 Fish Sample Results ........................................................................................... 21 2.7 Food Product Sample Results............................................................................. 21 2.8 Interlaboratory Comparison Results .................................................................... 21 2.9 Land Use Census Results ................................................................................... 21 3.0 Radiological Environmental Monitoring Program Summary .......................................... 22 3.1 2014 Program Results Summary ........................................................................ 22 Tables Table 1.1 Radiological Environmental Sampling Program ............................................... 9 Table 2.1 2013 Land Use Census .................................................................................... 22 Table 3.1 Radiological Environmental Monitoring Program Summary ............................. 23 Figures Figure 1-1 Sample Collection Sites - NEAR FIELD .......................................................... 15 Figure 1-2 Sample Collection Sites - FAR FIELD ............................................................. 16 Figure 1-3 Sample Collection Sites - SITE MAP ............................................................... 17 Attachments Summary of Monitoring Results ................................................................... 27 Interlaboratory Comparison Program ........................................................... 40 Sediment Dose Calculations ........................................................................ 107

Enclosure to 0CAN051502 Page 2 of 108 Summary The Annual Radiological Environmental Operating Report (AREOR) presents data obtained through analyses of environmental samples collected for Arkansas Nuclear One's (ANOs)

Radiological Environmental Monitoring Program (REMP) for the period January 1, 2014, through December 31, 2014. This report fulfills the requirements of ANO Unit 1 Technical Specification (TS) 5.6.2 and Unit 2 TS 6.6.2.

During 2014, as in previous years, ANO detected tritium attributable to plant operations at the discharge location (Station 8) where previously monitored liquid radioactive effluent from the plant is periodically discharged in accordance with the regulatory criteria established in the Offsite Dose Calculation Manual (ODCM). ANO personnel routinely monitor results from this area in order to note any trends. The review of results from this area indicates tritium levels in the surface water media continue to be below regulatory reporting limits and are consistent with concentrations that would typically be seen at this location as discussed in Section 2.3 of this AREOR.

Gross beta concentrations at the Station 14 (City of Russellville) indicator drinking water location continue to remain consistent with previous operational measurements and similar to the levels detected at the Station 57 (City of Danville) control drinking water location.

Radiological Environmental Monitoring Program ANO established the REMP prior to the station becoming operational (1974) to provide data on background radiation and radioactivity normally present in the area. ANO has continued to monitor the environment by sampling air, water, sediment, fish and food products, as well as measuring radiation directly. ANO also samples milk if milk-producing animals are present commercially within five miles of the plant.

The REMP includes sampling indicator and control locations within an approximate 20-mile radius of the plant. The REMP utilizes indicator locations near the site to show any increases or buildup of radioactivity that might occur due to station operation, and control locations farther away from the site to indicate the presence of only naturally occurring radioactivity. ANO personnel compare indicator results with control and preoperational results to assess any impact ANO operation might have had on the surrounding environment.

In 2014, ANO personnel collected environmental samples for radiological analysis. Personnel compared results of indicator locations with control locations and previous studies and concluded that overall no significant relationship exists between ANO operation and effect on the plant environs. The review of 2014 data, in most cases, showed undetectable radiation levels in the environment and in all instances, no definable trends related to significant pathways associated with ANO.

Harmful Effects or Irreversible Damage The REMP monitoring did not detect any harmful effects or evidence of irreversible damage in 2014. Therefore, no analysis or planned course of action to alleviate problems was necessary.

Enclosure to 0CAN051502 Page 3 of 108 Reporting Levels ANO's review indicates that no samples equaled or exceeded reporting levels for radioactivity concentration in environmental samples due to ANO effluents, as outlined in ODCM Table 2.5-2, when averaged over any calendar quarter. Therefore, 2014 results did not trigger any Radiological Monitoring Program special reports.

Radioactivity Not Attributable to ANO The ANO REMP has detected radioactivity attributable to other sources. These include the 25th Chinese nuclear test explosion in 1980 and the radioactivity plume release due to reactor core degradation at the Chernobyl Nuclear Power Plant in 1986. Prior to 1981, the ANO REMP detected radioactivity resulting from nuclear weapons testing, with Cesium-137 continuing to be periodically detected. In 2011, ANO detected I-131 radioactivity attributed to the Fukushima Daiichi Nuclear Power Plant accident (March 11, 2011).

Comparison to Federal and State Programs ANO personnel compared REMP data to state monitoring programs as results became available. Historically, the programs used for comparison have included the U.S. Nuclear Regulatory Commission (NRC) Thermoluminescent Dosimeter (TLD) Direct Radiation Monitoring Network and the Arkansas Department of Health (ADH).

The NRC TLD Network Program was discontinued in 1998. Historically these results have compared to those from the ANO REMP. ANO TLD results continue to remain similar to the historical average and continue to verify that plant operation is not affecting the ambient radiation levels in the environment.

The ADH and the ANO REMP entail similar radiological environmental monitoring program requirements. These programs include collecting air samples and splitting or sharing sample media such as water, sediment and fish. Both programs have obtained similar results over previous years.

Sample Deviations Milk The REMP did not include milk sampling within five miles of ANO in 2014 due to unavailability. The ODCM requires collection of milk samples, if available commercially within 5 miles of the plant. ANO personnel collected vegetation samples to monitor the ingestion pathway, as specified in the ODCM, because of milk unavailability.

Lower Levels of Detection (LLDs) during this reporting period were within the acceptable limits required by Table 2.5-1 of the ODCM.

Enclosure to 0CAN051502 Page 4 of 108 Air Samples Listed below are air sampler deviations that occurred during 2014 due to electrical power outages and equipment failure. These deviations did not result in exceeding LLD values specified in the ODCM. As described in ODCM, B 2.5.1, Actions A.1 and A.2, deviations are permitted from the required sampling schedule due to malfunction of sampling equipment and other legitimate reasons.

Station Sampling Period Comment As documented on 02/26/2014, totalizer run time for the listed sampling period was 21 hours2.430556e-4 days <br />0.00583 hours <br />3.472222e-5 weeks <br />7.9905e-6 months <br /> less than calculated run time. It 56 02/11/2014 - 02/25/2014 could not be established if the lost time was due to a power outage or if the totalizer malfunctioned. The totalizer was verified to advance. (CR-ANO-C-2014-00497)

As documented on 04/08/2014, totalizer run time for the listed sampling period was less 56 03/25/2014 - 04/08/2014 than expected and totalizer was not advancing. Totalizer was replaced.

(CR-ANO-C-2014-00930)

As documented on 05/06/2014, power was lost on 4/24/14 during the listed sampling 06 04/22/2014 - 05/06/2014 period. Reset the ground fault circuit interrupter (GFCI) and power was restored on 5/6/14. (CR-ANO-C-2014-01231)

As documented on 03/25/2014, the sample pump was not operating, thus no quantitative 01 03/11/2014 - 03/25/2014 results were obtained for the listed sampling period. Pump was replaced.

(CR-ANO-C-2014-00785)

As documented on 02/15/2014, Station #56 experienced a brief loss of power. Power was 56 02/11/2014 - 02/25/2014 restored before the end of the work shift.

(CR-ANO-C-2014-00369)

As documented on 03/12/2014, electrical power was lost to Station #56 on 3/12/2014.

56 03/11/2014 - 03/25/2014 Estimated that power restoration would occur before the end of work shift.

(CR-ANO-C-2014-00675)

Enclosure to 0CAN051502 Page 5 of 108 Missed Samples First quarter environmental TLD Station #150 missing (CR-ANO-C-2014-00946)

First quarter environmental TLD Station # 127 missing (CR-ANO-C-2014-00966).

Second quarter environmental TLD Station # 4 missing (CR-ANO-C-2014-01890).

Third quarter environmental TLD Station #150 missing (CR-ANO-C-2014-02353)

Unavailable Results No results on air volume sampled for the period 3/11/14 - 3/25/14 at Station #1 are available due to pump failure.

Program Modifications The following revisions were made to OP-1608.005, Radiological Environmental Monitoring Program (REMP) in 2014. Collectively, these changes were made through two revisions to the procedure, Revisions 40 and 41.

Applied cosmetic changes throughout the procedure to improve place-keeping and clarity without changing the process or intent.

Modified wording throughout OP-1608.005 to improve clarity and consistency. This includes removing the word procedure and replacing with OP-. The modifications made do not change the process or intent of OP-1608.005.

Added CR-ANO-C-2013-02585 in the References section. Added step to incorporate this condition report (CR) which requires chemists to ensure particulate filter is centered (off-center could allow flow to bypass the filter). A Note was also added above this step in reference to the CR.

Numerous steps were identified as having more than one action per step. These steps were modified to indicate single actions in separate steps. The intent of this change was to facilitate place-keeping so that steps are not missed.

Updated ODCM reference requirement to L.2.5.1 in applicable tables to most recent ODCM revision.

Added reference to CR-ANO-C-2014-01380 to align air station numbering with the ODCM.

Updated air samples header in Attachment 1 to OP-1608.005 to reflect the required amount of air stations from four to five. Previously, OP-1608.005 indicated that only four were required per ODCM L.2.5.1. With revision 025 of the ODCM, this is required to be five air stations. Though the requirement only stated that four stations were performed, there were five air stations already listed. The change provided consistent numbering throughout OP-1608.005 as well as the ODCM.

Enclosure to 0CAN051502 Page 6 of 108 Attachments contains results of air, TLD, water, sediment, fish, and food product samples collected in 2014. TLDs were analyzed by a vendor (Environmental Dosimetry Company -

EDC). All remaining samples were analyzed GEL Laboratories, LLC (GEL), except for the air samples covering December 30-31, 2014, which were analyzed by Teledyne Brown Engineering (TBE). TBE is the ANO vendor for 2015 samples; TBEs first air samples for 2015 also included the closing two days of 2014. contains GELs participation in the inter-laboratory comparison program during 2014. No documentation for TBEs participation is included in this report, but will be included in ANOs report for 2015 REMP activities. contains dose calculations performed for sediment using a generalized equation from Regulatory Guide 1.109, Calculation of Annual Doses to Man from Routine Releases of Reactor Effluents for the Purpose of Evaluating Compliance with 10 CFR Part 50, Appendix I, Revision 1.

Enclosure to 0CAN051502 Page 7 of 108 1.0 Introduction 1.1 Radiological Environmental Monitoring Program ANO established the REMP to ensure that plant operating controls properly function to minimize any associated radiation endangerment to human health or the environment. The REMP is designed for:

Analyzing applicable pathways for anticipated types and quantities of radionuclides released into the environment.

Considering the possibility of a buildup of long-lived radionuclides in the environment and identifying physical and biological accumulations that may contribute to human exposures.

Considering the potential radiation exposure to plant and animal life in the environment surrounding ANO.

Correlating levels of radiation and radioactivity in the environment with radioactive releases from station operation.

1.2 Pathways Monitored The airborne, direct radiation, waterborne and ingestion pathways are monitored as required by the ODCM. A description of the ANO REMP used to monitor the exposure pathways is described in Table 1.1 and shown in Figures 1-1, 1-2 and 1-3.

Section 2.0 of this report provides a discussion of 2014 sampling results and Section 3.0 provides a summary of results for the monitored exposure pathways.

1.3 Land Use Census ANO personnel conduct the land use census every 24 months as required by ODCM Surveillance (S) 2.5.2.1. The land use census was last conducted in 2013. This census serves to identify changes in land use within five miles of ANO that would require modifications to the REMP or ODCM. The most important concerns during this census are to determine location in each sector of the nearest:

1) Residence

2) Animal milked for human consumption

3) Garden of greater than 500 square feet producing fresh leafy (broadleaf) vegetables*

ANO personnel did not perform a garden census since an ODCM Limitation (L) 2.5.2 Note allows the routine sampling of broadleaf vegetation in the highest D/Q sector near the site boundary in lieu of the garden census.

Enclosure to 0CAN051502 Page 8 of 108 The method used by ANO personnel for conducting the land use census was as follows:

ANO personnel conducted door-to-door (drive by) field surveys in order to locate the nearest resident in each meteorological sector.

Consultation with local agricultural authorities was used to identify commercial milk providers within five-miles of the Unit 1 reactor building.

As a result of these surveys, the following information was obtained in each meteorological sector:

1) Nearest permanent residence

2) Nearest milking animal ANO personnel identify locations on the map, measure distances to ANO (or use a GPS system) and record results.

Locations, if any, are identified which yield a calculated dose or dose commitments greater than those currently calculated in the ODCM.

ANO personnel compare results to previous census.

Enclosure to 0CAN051502 Page 9 of 108 TABLE 1.1 RADIOLOGICAL ENVIRONMENT SAMPLING PROGRAM Exposure Sample Point Description, Sampling and Collection Requirement Type and Frequency Of Analyses Pathway Distance and Direction Frequency Radioiodine and Particulates Station 2 (243° - 0.5 miles) - South of the sewage treatment plant.

3 samples close to the Site Boundary, in (or near) different sectors with the Station 56 (264° - 0.4 miles) - West highest calculated annual average end of the sewage treatment plant.

ground level D/Q.

Station 1 (88° - 0.5 miles) - Near the meteorology tower.

Radioiodine Canister - Analyze at Continuous operation of least once per 14 days for I-131.

Radioiodine and Particulates sampler with sample collection Airborne Station 6 (111° - 6.8 miles) - as required by dust loading but Particulate Sampler - Analyze for 1 sample from the vicinity of a at least once per 14 days. gross beta radioactivity following Entergy local office in Russellville community having the highest calculated filter change.

(305 South Knoxville Avenue).

annual average ground level D/Q.

Radioiodine and Particulates Station 7 (210° - 19.0 miles) -

1 sample from a control location Entergy Supply Yard on Highway 10 15 - 30 km (10 - 20 miles) distance. in Danville.

Thermoluminescent dosimetry (TLDs) Station 1 (88° - 0.5 miles) - On a pole near the meteorology tower.

16 inner ring stations with two or more dosimeters in each meteorological sector Station 2 (243° - 0.5 miles) - South in the general area of the site boundary. of the sewage treatment plant.

Direct Station 3 (5 - 0.7 miles) - West of Once per 92 days. Gamma Dose - Once per 92 days.

Radiation ANO Gate #2 on Highway 333 (approximately 0.35 miles)

Station 4 (181° - 0.5 miles) - West of May Cemetery entrance on south side of the road.

Enclosure to 0CAN051502 Page 10 of 108 TABLE 1.1 (continued)

RADIOLOGICAL ENVIRONMENT SAMPLING PROGRAM Exposure Sample Point Description, Sampling and Collection Requirement Type and Frequency Of Analyses Pathway Distance and Direction Frequency TLDs Station 56 (264° - 0.4 miles) - West end of the sewage treatment plant.

16 inner ring stations with two or more dosimeters in each meteorological sector Station 108 (306° - 0.9 miles) -

in the general area of the site boundary South on Flatwood Road on a utility pole.

Station 109 (291° - 0.6 miles) -

Utility pole across from the junction of Flatwood Road and Round Mountain Road.

Station 110 (138° - 0.8 miles) -

Bunker Hill Lane on the first utility pole on the left.

Direct Radiation Station 145 (28° - 0.6 miles) - Near Once per 92 days. Gamma Dose - Once per 92 days.

west entrance to the RERTC on a utility pole.

Station 146 (45° - 0.6 miles) -

South end of east parking lot at RERTC on a utility pole.

Station 147 (61° - 0.6 miles) - West side of Bunker Hill Road, approximately 100 yards from intersection with State Highway 333.

Station 148 (122° - 0.6 miles) -

Intersection of Bunker Hill Road with Scott Lane on county road sign post.

Enclosure to 0CAN051502 Page 11 of 108 TABLE 1.1 (continued)

RADIOLOGICAL ENVIRONMENT SAMPLING PROGRAM Exposure Sample Point Description, Sampling and Collection Requirement Type and Frequency Of Analyses Pathway Distance and Direction Frequency TLDs Station 149 (156° - 0.5 miles) - On a utility pole on the south side of 16 inner ring stations with two or more May Road.

dosimeters in each meteorological sector in the general area of the Site Boundary. Station 150 (205° - 0.6 miles) -

North side of May Road on a utility pole past the McCurley Place turn.

Station 151 (225° - 0.4 miles) -

West side of sewage treatment plant near the lake on a metal post.

Station 152 (338° - 0.8 miles) -

South side of State Highway 333 on a road sign post.

Direct Radiation TLDs Station 6 (111° - 6.8 miles) - Once per 92 days. Gamma Dose - Once per 92 days.

Entergy local office in Russellville 8 stations with two or more dosimeters in (305 South Knoxville Avenue).

special interest areas such as population centers, nearby residences, schools, and Station 7 (210° - 19.0 miles) -

in 1 - 2 areas to serve as control Entergy Supply Yard on Highway 10 locations. in Danville.

Station 111 (120° - 2.0 miles) -

Marina Road on a utility pole on the left just prior to curve.

Station 116 (318° - 1.8 miles) -

Highway 333 and Highway 64 in London on a utility pole north of the railroad tracks.

Enclosure to 0CAN051502 Page 12 of 108 TABLE 1.1 (continued)

RADIOLOGICAL ENVIRONMENT SAMPLING PROGRAM Exposure Sample Point Description, Sampling and Collection Requirement Type and Frequency Of Analyses Pathway Distance and Direction Frequency TLDs Station 125 (46° - 8.7 miles) -

College Street on a utility pole at the 8 stations with two or more dosimeters in southeast corner of the red brick special interest areas such as population school building.

centers, nearby residences, schools, and in 1 - 2 areas to serve as control Station 127 (100° - 5.2 miles) -

locations. Arkansas Tech Campus on a utility pole across from Paine Hall.

Direct Radiation Station 137 (151° - 8.2 miles) - On Once per 92 days. Gamma Dose - Once per 92 days.

a speed limit sign on the right in front of the Morris R. Moore Arkansas National Guard Armory.

Station 153 (304° - 9.2 miles) -

Knoxville Elementary School near the school entrance gate on a utility pole.

Surface Water Station 8 (166° - 0.2 miles) - Plant 1 indicator location (influenced by plant discharge canal.

discharge) Gamma isotopic and tritium Once per 92 days.

analyses once per 92 days.

Station 10 (95° - 0.5 miles) - Plant 1 control location (uninfluenced by plant intake canal.

discharge)

Waterborne Drinking Water Station 14 (70° - 5.1 miles) -

Russellville city water system from 1 indicator location (influenced by plant the Illinois Bayou. I-131, gross beta, gamma isotopic discharge) Once per 92 days. and tritium analyses once per 92 Station 57 (208° - 19.5 miles) - days.

1 control location (uninfluenced by plant Danville public water supply discharge) treatment on Fifth Street.

Enclosure to 0CAN051502 Page 13 of 108 TABLE 1.1 (continued)

RADIOLOGICAL ENVIRONMENT SAMPLING PROGRAM Exposure Sample Point Description, Sampling and Collection Requirement Type and Frequency Of Analyses Pathway Distance and Direction Frequency Sediment Station 8 (243° - 0.9 miles) - Plant discharge canal.

1 indicator location (influenced by plant Waterborne discharge) Gamma isotopic analysis once per Station 16 (287° - 5.5 miles) - Once per 365 days.

365 days.

Panther Bay on south side of 1 control location (uninfluenced by plant Arkansas River across from mouth discharge) of Piney Creek.

Milk 1 indicator sample location within five-mile distance if commercially available. Currently, no available milking Gamma isotopic and I-131 Once per 92 days.

animals within 5 miles of ANO. analyses once per 92 days.

1 control sample location at a distance of

>five-miles when an indicator exists.

Fish Station 8 (212° - 0.5 miles) - Plant 1 sample of commercially and/or discharge canal.

recreationally important species in Gamma isotopic on edible portions vicinity of plant discharge. Station 16 (287° - 5.5 miles) - Once per 365 days.

once per 365 days.

Panther Bay on south side of Ingestion 1 sample of same species in area not Arkansas River across from mouth influenced by plant discharge. of Piney Creek.

Food Products 1 sample of broadleaf (edible or non-edible) near the site boundary from one Station 13 (273° - 0.5 miles) - West of the highest anticipated annual average from ANO toward Gate 4 onto ground level D/Q sectors, if milk Flatwood Road. Gamma. isotopic and I-131 sampling is not performed. Three per 365 days.

analyses three times per 365 days Station 55 (208° - 16.5 miles) -

1 sample location of broadleaf vegetation Intersection of Highway 27 and 154.

(edible or non-edible) from a control location 15 - 30 km (10 - 20 miles) distant, if milk sampling is not performed.

Enclosure to 0CAN051502 Page 14 of 108 TABLE 1.1 (continued)

RADIOLOGICAL ENVIRONMENT SAMPLING PROGRAM Exposure Sample Point Description, Distance and Sampling and Collection Type and Frequency Of Requirement Pathway Direction Frequency Analyses 2 sample locations of Groundwater from Station 58 (GWM-1, 22° - 0.3 miles) - Once per 92 days Control, Tritium, Gross Beta a control location up gradient from the North of Protected Area on Owner Control and Gamma Isotopic, once per protected area Area (OCA). West of Security North Check 92 days.

Point, east side of access road.

Station 62 (GWM-101, 34° - 0.5 miles) -

North of Protected Area on OCA. East of Once per 92 days Control, Tritium, Gross Beta outside receiving building. and Gamma Isotopic, once per Ground 92 days.

water Station 63 (GWM-103, 206° - 0.1 miles) -

2 sample locations of Groundwater from South of Protected area on OCA. North- Once per 92 days Indicator, Tritium, Gross Beta indicator locations down gradient from east of Stator Rewind Bldg. near wood line. and Gamma Isotopic, once per the protected area. 92 days.

Station 64 (GWM-13, 112° - 0.1 miles) -

South of Oily Water Separator facility, Once per 92 days Indicator, Tritium, Gross Beta northwest corner of U-2 Intake Structure. and Gamma Isotopic, once per Inside Protected area. 92 days.

Enclosure to 0CAN051502 Page 15 of 108 FIGURE 1-1 SAMPLE COLLECTION SITES - NEAR FIELD SR 333 152 3 108 Training 145 Center 146 147 109 13 1 West Access Rd. 10 56 2 8C 36 Scott Ln.

151 148 8S May Rd. Bunker Cemetery Bunker Hill Ln.

Hill Rd.

149 150 4 110 Arkansas Nuclear One REMP Sample Locations (Near Field)

Lake Dardanelle Revised 24May05

Enclosure to 0CAN051502 Page 16 of 108 FIGURE 1-2 SAMPLE COLLECTION SITES - FAR FIELD 1

2 0° 16 340° 20° US HWY 7 TO HARRISON 15 320° 40° INTERSTATE 40 3 TO FORT SMITH SR 5 PINEY BAY USE AREA Dover 125 SR 333 300° 60° 164 EAST TO 153 U.S.

MORELAND HWY 14 64 4

14 SR 24 TO MORELAND 280° ARKANSAS RIVER 116 INTERSTATE 40 80° 16 LONDON US 13 J I H G F E D C B HWY 64 5

DELAWARE STATE PARK 127 260° DARDANELLE STATE PARK 111 ARKANSAS TECH UNIVERSITY 100° U.S. HWY 22 HWY 524 LAKE DARDANELLE DARDANELLE STATE PARK RUSSELLVILLE 6

12 DARDANELLE LOCK AND DAM HWY 22 DAM SITE EAST PARK HWY 7T 6 240° 120° HWY 155 HWY 7 SR 247 TO POTTSVILLE MT. NEBO HWY 27 137 STATE PARK DARDANELLE 11 220° HWY 28 140° 7

HWY 7 200° 160° 10 180° 8

HWY 7 TO HOT SPRINGS HWY 27 TO DANVILLE INSET DANVILLE (SEE INSET) 9 N W E HWY 154 S

HWY 27 55 HWY 10 Entergy Substation 7

Petit Jean River 57 HWY 10 Cowger Lake City of Danville Arkansas Nuclear One HWY 80 HWY 27 REMP Sample Locations (Far Field)

Enclosure to 0CAN051502 Page 17 of 108 FIGURE 1-3 SAMPLE COLLECTION SITES - SITE MAP 62 58 STR-3 Switch STR-2 Yard STR-4 STR-6 West Access Road 64 STR-5 63 STR-1 N

Lake Dardanelle W E S

Arkansas Nuclear One REMP Sample Locations Site Map

Enclosure to 0CAN051502 Page 18 of 108 2.0 Interpretation and Trends of Results 2.1 Air Particulate and Radioiodine Sample Results The REMP has detected radioactivity in the airborne pathway attributable to other sources.

These include the 25th Chinese nuclear test explosion in 1980, the radioactive plume release due to reactor core degradation at Chernobyl Nuclear Power Plant in 1986 and the Fukushima Daiichi Nuclear Power Plant accident (Mach 11, 2011).

As in past years, there were no other detections of I-131. Indicator gross beta air particulate results for 2014 were higher compared to results obtained from 2000-2012 of the operational REMP, but less than 2013 when the annual average was 0.043. Also, the 2014 annual average was less than the average for preoperational levels. Results are reported as annual average picocuries per cubic meter (pCi/m3).

Monitoring Period Result 2000 - 2012 (Minimum Value) 0.020 2014 Value 0.035 2000 - 2012 (Maximum Value) 0.032 Preoperational 0.050 In the absence of plant-related gamma radionuclides, gross beta activity is attributed to naturally occurring radionuclides. Table 3.1, which includes gross beta concentrations and provides a comparison of the indicator and control means and ranges, emphasizes the consistent trends seen in this pathway to support the presence of naturally occurring activity. Therefore, it can be concluded that the airborne pathway continues to be unaffected by ANO operations.

2.2 Thermoluminescent Dosimetry (TLD) Sample Results ANO reports measured dose as net exposure (field reading less transit reading) normalized to 92 days and relies on comparison of the indicator locations to the control as a measure of plant impact. ANOs comparison of the inner ring and special interest area TLD results to the control, as seen in Table 3.1, identified no noticeable trend that would indicate that the ambient radiation levels are being affected by plant operations. In addition, the inner ring value of 7.83 millirem (mrem) shown in Table 3.1 for 2014 is within the historical bounds of 2000 - 2013 annual average results, which have ranged from 6.6 to 8.9 mrem. Overall, ANO concluded that the ambient radiation levels are not being affected by plant operations.

2.3 Water Sample Results Analytical results for 2014 drinking water and ground water samples were similar to those reported in previous years. Gamma radionuclides analytical results for 2014 surface water samples were similar to those reported in previous years. Tritium detection in ANO surface water indicator samples continues but at levels below those experienced in 2013 and below the ODCM-required LLD. These results are further explained below.

Enclosure to 0CAN051502 Page 19 of 108 Surface water samples were collected and analyzed for gamma radionuclides and tritium.

Gamma radionuclides were below detectable limits which is consistent with results seen in previous operational years. Tritium continues to be detected at the indicator location (Station 8) where previously monitored liquid radioactive effluent from the plant is periodically discharged in accordance with the regulatory criteria established in the ODCM and, for 2014, at levels considerably lower than the ODCM-required LLD of 3000 picocuries per liter. Furthermore, unlike the elevated tritium levels observed in 2013 attributable to particular plant events, no elevated levels attributable to particular events were observed in 2014. Results are reported as annual average picocuries per liter (pCi/l).

Monitoring Period Result 2000 - 2013 (Minimum Value) 277.1 2014 Value 554.5 2000 - 2013 (Maximum Value) 1003.5 Preoperational 200.0 ANO personnel have noted no definable increasing trends associated with the tritium levels at the discharge location. Levels detected during 2014 and previous operational years have been well below regulatory reporting limits. Therefore, the operation of ANO had no definable impact on this waterborne pathway during 2014 and levels of radionuclides remain similar to those obtained in previous operational years.

Drinking water samples were collected from two locations (indicator and control). Although ANO personnel utilize Station 14 (City of Russellville) as an indicator location due to the potential for the drinking water pathway to exist, the City of Russellville has not withdrawn water from Lake Dardanelle in the past several years.

Drinking water samples were analyzed for gross beta radionuclides, I-131, gamma radionuclides and tritium. Gamma radionuclides, gross beta radionuclides, I-131 and tritium concentrations were below the LLD limits at the indicator and control locations, which is consistent with 2013 and comparable to the 2000 - 2012 preoperational and operational years as shown below. Results from 2014 are summarized in Table 3.1. Results are reported as annual average pCi/l.

Radionuclide 2014 2013 2000 - 2012 Preoperational Gross Beta <LLD < LLD 2.59 2.0 Iodine-131 <LLD < LLD < LLD < LLD Gamma <LLD < LLD < LLD < LLD Tritium <LLD < LLD < LLD 200.0 ANO personnel have noted no definable trends associated with drinking water results at the indicator location. Therefore, the operation of ANO had no definable impact on this waterborne pathway during 2014 and levels of radionuclides remain similar to those obtained in previous operational years.

Enclosure to 0CAN051502 Page 20 of 108 Groundwater samples were collected from four REMP locations (2 control, and 2 indicator locations). During 2011, ANO incorporated sixteen additional groundwater monitoring wells into the Groundwater Protection Initiative (GPI) site program. Sample data are compiled, organized and reviewed annually to:

Analyze for increasing or decreasing trends at individual sample points, wells or groups of wells.

Review the radionuclides detected to determine whether changes should be made to the analysis suites or sampling frequencies for each sampling location.

Evaluate the locations of radionuclides in ground water to determine if changes should be made to the sampling locations.

Review current investigation levels and determine if changes should be made.

Determine if any change to the ODCM is required.

Determine if a corrective actions/remediation is required.

Groundwater samples from the four REMP locations were analyzed for tritium and gamma radionuclides. Tritium and gamma concentrations were below the LLD limits at all four locations. Listed below is a comparison of 2014 indicator results to past operational years.

Results are reported as annual average pCi/l. REMP Groundwater data are captured in Tables 8.1 and 8.2. Therefore, ANO operations had no significant impact on the environment or public by this waterborne pathway.

Radionuclide 2014 2006 - 2013 Iodine-131 < LLD < LLD Gamma < LLD < LLD Tritium < LLD < LLD 2.4 Sediment Sample Results Sediment samples were collected from two locations in 2014 and analyzed for gamma radionuclides. Listed below is a comparison of 2014 indicator results to 2013 and the 2000 -

2012 operational years. Therefore, ANO operations had no significant impact on the environment or public by this waterborne pathway. Results are reported as pCi/kg.

Monitoring Period Result 2000 - 2012 (Minimum Value) 41.79 2013 Value < LLD 2014 Value < LLD 2000 - 2012 (Maximum Value) 1170.0 Since reporting levels for radionuclides in sediment have not been established, an evaluation of potential dose to the public from this media was performed as shown in Attachment 3.

Enclosure to 0CAN051502 Page 21 of 108 2.5 Milk Sample Results Milk samples were not collected during 2014 due to the unavailability of indicator locations within five-miles of ANO.

2.6 Fish Sample Results Fish samples were collected from two locations and analyzed for gamma radionuclides. In 2014, gamma radionuclides were below detectable limits which are consistent with the preoperational monitoring period and operational results since 1997. Therefore, based on these measurements, ANO operations had no significant radiological impact upon the environment or public by this ingestion pathway.

2.7 Food Product Sample Results The REMP has detected radionuclides prior to 1990 that are attributable to other sources.

These include the radioactive plume release due to reactor core degradation at Chernobyl Nuclear Power Plant in 1986 and atmospheric weapons testing.

In 2014, food product samples were collected when available from two locations and analyzed for Iodine-131 and gamma radionuclides. The 2014 levels remained undetectable, as has been the case in previous years. Therefore, based on these measurements, ANO operations had no significant radiological impact upon the environment or public by this ingestion pathway.

2.8 Interlaboratory Comparison Results GEL Laboratories analyzed interlaboratory comparison samples to fulfill the requirements of ODCM Section 2.5.3. Attachment 2 contains these results.

2.9 Land Use Census Results The latest land use census (performed in 2013) did not identify any new locations that yielded a calculated dose or dose commitment greater than those currently calculated (see Table 2.1).

Also, the land use census identified no milk-producing animals within a five-mile radius of the plant site. ANO personnel chose not to perform a garden census in 2013, which is allowed by ODCM Section L 2.5.2, in lieu of broadleaf vegetation sampling in the meteorological sector (Sector 13) with the highest D/Q.

Enclosure to 0CAN051502 Page 22 of 108 TABLE 2.1 2013 LAND USE CENSUS Nearest Residence Within Five Miles Direction Sector Distance (miles)

N 1 0.9 NNE 2 1.3 NE 3 0.9 ENE 4 0.8 E 5 0.8 ESE 6 0.8 SE 7 0.8 SSE 8 0.8 S 9 0.8 SSW 10 0.7 SW 11 2.8 WSW 12 0.7 W 13 0.8 WNW 14 0.8 NW 15 1.0 NNW 16 0.9 3.0 Radiological Environmental Monitoring Program Summary 3.1 2014 Program Results Summary Table 3.1 summarizes the 2014 REMP results.

Enclosure to 0CAN051502 Page 23 of 108 TABLE 3.1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

Name of Facility: ANO - Units 1 and 2 Docket No: 50-313 and 50-368.

Location of Facility: Pope County, Arkansas Reporting Period: January - December 2014 Type / Indicator Location with Highest Annual Mean Control Number of Sample Type Number of LLDb Locations Mean Locations Mean Non-Routine (Units) Locationd Mean (°F)c [Range]

Analysesa (°F)c [Range] (°F)c [Range] Resultse Air Particulates 0.0355 (84 / 84) Station 2 0.0363 (28 / 28) 0.034 (56 / 56)

GB / 140 0.01 0 (pCi/m3) [0.015 - 0.072] (243°, 0.5 mi) [0.020 - 0.070] [0.019 - 0.079]

Airborne Iodine I-131 / 140 0.07 < LLD N/A N/A < LLD 0 (pCi/ m3)

(f)

Inner Ring TLDs Gamma / 61 7.83 (61 / 64) Station 56 9.2 (4 / 4) N/A 0 (mR/Qtr) [4.9 - 10.1] (264°, 0.4 mi) [8.1 - 9.7]

Special Interest Gamma / 27 (f) 6.91 (27 / 28) Station 137 8.3 (4 / 4) N/A 0 TLDs (mR/Qtr) [4.3 - 9.0] (151°, 8.2 mi) [7.7 - 9.0]

Control TLD Gamma / 4 (f)

N/A N/A N/A 6.1 (4 / 4) 0 (mR/Qtr) [5.6 - 6.6]

Enclosure to 0CAN051502 Page 24 of 108 TABLE 3.1 (continued)

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

Type / Indicator Location with Highest Annual Mean Control Number of Sample Type b Number of LLD Locations Mean Locations Mean Non-Routine (Units) Locationd Mean (°F)c [Range]

Analysesa (°F)c [Range] (°F)c [Range] Resultse H-3 / 8 3000 555 (4* / 4) Station 8 555 (4* / 4) < LLD 0

[344 - 745] (166°, 0.2 mi) [344 - 745]

GS / 24 Mn-54 15 < LLD N/A N/A < LLD 0 Fe-59 30 < LLD N/A N/A < LLD 0 Co-58 15 < LLD N/A N/A < LLD 0 Co-60 15 < LLD N/A N/A < LLD 0 Surface Water Zn-65 30 < LLD N/A N/A < LLD 0 (pCi/l)

Zr-95 30 < LLD N/A N/A < LLD 0 Nb-95 15 < LLD N/A N/A < LLD 0 I-131 15 < LLD N/A N/A < LLD 0 Cs-134 15 < LLD N/A N/A < LLD 0 Cs-137 18 < LLD N/A N/A < LLD 0 Ba-140 60 < LLD N/A N/A < LLD 0 La-140 15 < LLD N/A N/A < LLD 0

Positive tritium results

Enclosure to 0CAN051502 Page 25 of 108 TABLE 3.1 (continued)

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

Type / Indicator Location with Highest Annual Mean Control Number of Sample Type b Number of LLD Locations Mean Locations Mean Non-Routine (Units) Locationd Mean (°F)c [Range]

Analysesa (°F)c [Range] (°F)c [Range] Resultse GB / 8 4 < LLD N/A N/A < LLD 0 I-131 / 8 1 < LLD N/A N/A < LLD 0 H-3 / 8 2000 < LLD N/A N/A < LLD 0 GS / 8 Mn-54 15 < LLD N/A N/A < LLD 0 Drinking Water Fe-59 30 < LLD N/A N/A < LLD 0 (pCi/1) Co-58 15 < LLD N/A N/A < LLD 0 Co-60 15 < LLD N/A N/A < LLD 0 Zn-65 30 < LLD N/A N/A < LLD 0 Zr-95 30 < LLD N/A N/A < LLD 0 Nb-95 15 < LLD N/A N/A < LLD 0 Cs-134 15 < LLD N/A N/A < LLD 0 Cs-137 18 < LLD N/A N/A < LLD 0 Ba-140 60 < LLD N/A N/A < LLD 0 La-140 15 < LLD N/A N/A < LLD 0 Bottom GS / 2 Sediment Cs-134 150 < LLD N/A < LLD < LLD 0 (pCi/kg) Cs-137 180 < LLD N/A < LLD < LLD 0

Positive GB results.

Enclosure to 0CAN051502 Page 26 of 108 TABLE 3.1 (continued)

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

SUMMARY

Type / Indicator Location with Highest Annual Mean Control Number of Sample Type b Number of LLD Locations Mean Locations Mean Non-Routine (Units) Locationd Mean (°F)c [Range]

Analysesa (°F)c [Range] (°F)c [Range] Resultse GS / 2 Mn-54 130 < LLD N/A N/A < LLD 0 Fe-59 260 < LLD N/A N/A < LLD 0 Co-58 130 < LLD N/A N/A < LLD 0 Fish (pCi/kg)

Co-60 130 < LLD N/A N/A < LLD 0 Zn-65 260 < LLD N/A N/A < LLD 0 Cs-134 130 < LLD N/A N/A < LLD 0 Cs-137 150 < LLD N/A N/A < LLD 0 I-131 / 6 60 < LLD N/A N/A N/A 0 Food Products GS / 6 (pCi/kg)

Cs-134 60 < LLD N/A N/A N/A 0 Cs-137 80 < LLD N/A N/A N/A 0 a

GB = Gross beta; I-131 = Iodine-131; H-3 = Tritium; GS = Gamma scan.

b LLD = Required lower limit of detection based on ANO Units 1 and 2 ODCM Table 2.5-1.

c Mean and range based upon detectable measurements only. Fraction of detectable measurements at specified locations is indicated in parenthesis (F).

d Locations are specified (1) by name and (2) degrees relative to reactor site.

e Non-routine results are those which exceed ten times the control station value. If no control station value is available, the result is considered non-routine if it exceeds ten times the preoperational value for the location.

f LLD is not defined in ANO Units 1 and 2 ODCM Table 2.5-1.

Enclosure to 0CAN051502 Page 27 of 108 ATTACHMENT 1

SUMMARY

OF MONITORING RESULTS

Enclosure to 0CAN051502 Page 28 of 108 Table of Contents Table 1.1 Air Particulate ................................................................................................... 29 Table 1.2 Radioiodine Cartridge ....................................................................................... 30 Table 2.1 Thermoluminescent Dosimeters (Inner Ring) ................................................... 31 Table 2.2 Thermoluminescent Dosimeters (Special Interest Areas) ................................ 32 Table 3.1 Surface Water (Gamma Isotopic) ..................................................................... 33 Table 3.2 Surface Water (Tritium) .................................................................................... 34 Table 4.1 Drinking Water (Gross beta, I-131 and Gamma Isotopic) ................................ 35 Table 4.2 Drinking Water (Tritium) ................................................................................... 36 Table 5.1 Sediment .......................................................................................................... 36 Table 6.1 Fish ................................................................................................................... 36 Table 7.1 Food Products .................................................................................................. 37 Table 8.1 Groundwater Data (Gross Beta and Gamma Isotopic)..................................... 38 Table 8.2 Groundwater Data (Tritium) .............................................................................. 39

Enclosure to 0CAN051502 Page 29 of 108 Table 1.1 Sample Type: Air Particulate Analysis: Gross Beta Units: pCi/m3 Station 1 Station 2 Station 56 Station 6 Station 7*

Start Date End Date (Indicator) (Indicator) (Indicator) (Control) (Control)

Required LLD 0.01 0.01 0.01 0.01 0.01 12/31/2013 01/14/2014 0.032 0.034 0.037 0.033 0.042 01/14/2014 01/28/2014 0.027 0.022 0.027 0.022 0.026 01/28/2014 02/10/2014 0.036 0.034 0.034 0.030 0.032 02/10/2014 02/20/2014 0.046 0.037 0.041 0.032 0.039 02/20/2014 02/26/2014 0.025 0.020 0.030 0.023 0.026 02/26/2014 03/11/2014 0.055 0.046 0.050 0.051 0.049 03/11/2014 03/25/2014 0.015 0.029 0.042 0.031 0.032 03/25/2014 04/08/2014 0.031 0.032 0.031 0.030 0.029 04/08/2014 04/22/2014 0.072 0.070 0.056 0.062 0.079 04/22/2014 05/06/2014 0.024 0.031 0.028 0.033 0.027 05/06/2014 05/20/2014 0.030 0.029 0.028 0.028 0.028 05/20/2014 06/03/2014 0.024 0.027 0.026 0.023 0.026 06/03/2014 06/17/2014 0.025 0.023 0.024 0.020 0.023 06/17/2014 07/01/2014 0.028 0.031 0.032 0.028 0.028 07/01/2014 07/15/2014 0.031 0.031 0.028 0.028 0.026 07/15/2014 07/29/2014 0.032 0.034 0.030 0.025 0.032 07/29/2014 08/12/2014 0.041 0.040 0.034 0.039 0.038 08/12/2014 08/26/2014 0.034 0.034 0.033 0.030 0.032 08/26/2014 09/09/2014 0.027 0.033 0.028 0.031 0.028 09/09/2014 09/23/2014 0.034 0.039 0.033 0.033 0.036 09/23/2014 10/07/2014 0.042 0.041 0.037 0.039 0.041 10/07/2014 10/21/2014 0.043 0.038 0.036 0.036 0.037 10/21/2014 11/04/2014 0.047 0.048 0.045 0.046 0.047 11/04/2014 11/18/2014 0.036 0.039 0.037 0.032 0.031 11/18/2014 12/02/2014 0.044 0.047 0.032 0.035 0.034 12/02/2014 12/16/2014 0.054 0.067 0.054 0.047 0.044 12/16/2014 12/30/2014 0.038 0.035 0.034 0.033 0.029 12/30/2014 01/12/2015 0.024 0.026 0.023 0.021 0.019

Station with highest annual mean.

Enclosure to 0CAN051502 Page 30 of 108 Table 1.2 Sample Type: Radioiodine Cartridge Analysis: Iodine-131 Units: pCi/m3 Station 1 Station 2 Station 56 Station 6 Station 7*

Start Date End Date (Indicator) (Indicator) (Indicator) (Control) (Control)

Required LLD 0.07 0.07 0.07 0.07 0.07 12/31/2013 01/14/2014 < 0.046 < 0.018 < 0.019 < 0.024 < 0.022 01/14/2014 01/28/2014 < 0.014 < 0.011 < 0.027 < 0.015 < 0.018 01/28/2014 02/10/2014 < 0.017 < 0.022 < 0.025 < 0.025 < 0.023 02/10/2014 02/20/2014 < 0.031 < 0.023 < 0.049 < 0.044 < 0.032 02/20/2014 02/26/2014 < 0.051 < 0.015 < 0.013 < 0.016 < 0.019 02/26/2014 03/11/2014 <0.023 <0.017 <0.016 <0.016 <0.021 03/11/2014 03/25/2014 < 0.008 < 0.008 < 0.015 < 0.009 < 0.009 03/25/2014 04/08/2014 < 0.027 < 0.016 < 0.033 < 0.029 < 0.023 04/08/2014 04/22/2014 < 0.023 < 0.012 < 0.016 < 0.019 < 0.013 04/22/2014 05/06/2014 < 0.009 < 0.010 < 0.010 < 0.062 < 0.007 05/06/2014 05/20/2014 < 0.019 < 0.013 < 0.020 < 0.027 < 0.016 05/20/2014 06/03/2014 < 0.026 < 0.033 < 0.013 < 0.028 < 0.021 06/03/2014 06/17/2014 < 0.015 < 0.011 < 0.024 < 0.023 < 0.012 06/17/2014 07/01/2014 < 0.012 < 0.010 < 0.015 < 0.014 < 0.013 07/01/2014 07/15/2014 < 0.038 < 0.020 < 0.021 < 0.035 < 0.029 07/15/2014 07/29/2014 < 0.019 < 0.026 < 0.026 < 0.018 < 0.016 07/29/2014 08/12/2014 < 0.021 < 0.015 < 0.022 < 0.010 < 0.013 08/12/2014 08/26/2014 < 0.025 < 0.030 < 0.035 < 0.033 < 0.033 08/26/2014 09/09/2014 < 0.029 < 0.018 < 0.021 < 0.018 < 0.026 09/09/2014 09/23/2014 < 0.011 < 0.011 < 0.012 < 0.009 < 0.012 09/23/2014 10/07/2014 < 0.018 < 0.018 < 0.019 < 0.019 < 0.027 10/07/2014 10/21/2014 < 0.0120 < 0.017 < 0.034 < 0.026 < 0.026 10/21/2014 11/04/2014 < 0.015 < 0.020 < 0.023 < 0.017 < 0.027 11/04/2014 11/18/2014 < 0.018 < 0.018 < 0.029 < 0.023 < 0.027 11/18/2014 12/02/2014 < 0.019 < 0.021 < 0.021 < 0.019 < 0.017 12/02/2014 12/16/2014 < 0.017 < 0.017 < 0.024 < 0.015 < 0.011 12/16/2014 12/30/2014 < 0.022 < 0.021 < 0.032 < 0.018 < 0.043 12/30/2014 01/12/2015 < 0.019 < 0.034 < 0.034 < 0.034 < 0.034

Station with highest annual mean.

Enclosure to 0CAN051502 Page 31 of 108 Table 2.1 Sample Type: Thermoluminescent Dosimeters Analysis: Gamma Dose Units: mrem/Qtr Inner Ring (Indicators) 1st Qtr 14 2nd Qtr 14 3rd Qtr 14 4th Qtr 14 Annual Mean 14 Station (mrem) (mrem) (mrem) (mrem) (mrem) 1 8.1 7.4 8.9 9.0 8.4 2 7.2 7.9 8.2 8.5 8.0 3 5.8 4.9 5.0 6.6 5.6 4 7.6 LOST 7.2 8.9 7.9

56 9.3 9.7 8.1 9.6 9.2 108 8.1 7.6 7.1 9.8 8.2 109 8.2 8.3 7.7 9.7 8.5 110 7.4 8.2 8.3 9.2 8.3 145 8.2 7.9 7.5 8.7 8.1 146 7.8 7.9 7.4 8.7 8.0 147 7.1 6.0 6.2 7.6 6.7 148 7.7 7.1 7.6 9.0 7.9 149 7.2 8.1 7.8 8.1 7.8 150 LOST 8.2 LOST 9.8 9.0 151 7.7 7.8 7.9 10.1 8.4 152 6.8 5.9 5.2 7.3 6.3

Station with highest annual mean.

Enclosure to 0CAN051502 Page 32 of 108 Table 2.2 Sample Type: Thermoluminescent Dosimeters Analysis: Gamma Dose Units: mrem/Qtr Special Interest Areas - (Population Centers & Schools)

Station 1st Qtr 14 2nd Qtr 14 3rd Qtr 14 4th Qtr 14 Annual Mean 14 (mrem) (mrem) (mrem) (mrem) (mrem) 6 7.2 6.6 6.4 8.0 7.1 111 5.7 5.6 5.3 6.2 5.7 116 8.2 7.6 7.2 8.3 7.8 125 4.9 4.3 4.5 5.2 4.7 127 LOST 7.0 7.0 8.3 7.4

137 7.9 7.7 8.4 9.0 8.3 153 7.3 7.5 6.5 8.9 7.6

Stations with highest annual mean.

Special Interest Areas - (Control)

Station 1st Qtr 14 2nd Qtr 14 3rd Qtr 14 4th Qtr 14 Annual Mean 14 (mrem) (mrem) (mrem) (mrem) (mrem) 7 6.4 5.6 5.7 6.6 6.1

Enclosure to 0CAN051502 Page 33 of 108 Table 3.1 Sample Type: Surface Water Analysis: Gamma Isotopic Units: pCi/l Location Start Date End Date Mn-54 Co-58 Fe-59 Co-60 Zn-65 Nb-95 Zr-95 I-131 Cs-134 Cs-137 Ba-140 La-140 Required LLD 15 15 30 15 30 15 30 15 15 18 60 15 Station 8 (Indicator) 12/31/2013 01/31/2014 <2.90 <2.20 <5.18 <3.25 <5.81 <2.74 <4.80 <4.80 <3.09 <2.49 <4.33 <4.33 Station 10 (Control) 12/31/2013 01/31/2014 <2.63 <3.22 <5.46 <2.27 <4.94 <3.04 <4.38 <5.10 <3.03 <3.75 <3.99 <3.99 Station 8 (Indicator) 01/31/2014 02/29/2014 <2.17 <2.02 <4.50 <2.60 <4.73 <2.15 <4.05 <3.50 <2.37 <2.39 <3.38 <3.38 Station 10 (Control) 01/31/2014 02/29/2014 <3.19 <3.89 <7.78 <2.92 <7.71 <4.52 <6.31 <7.78 <4.38 <3.92 <5.51 <5.51 Station 8 (Indicator) 02/28/2014 03/31/2014 <4.76 <4.25 <8.28 <5.54 <10.20 <4.20 <9.26 <5.89 <5.37 <4.79 <6.31 <6.31 Station 10 (Control) 02/28/2014 03/31/2014 <4.19 <3.41 <7.34 <4.26 <8.01 <4.31 <8.17 <5.55 <3.93 <4.74 <4.52 <4.52 Station 8 (Indicator) 03/31/2014 04/30/2014 <3.66 <3.61 <7.88 <5.29 <5.70 <3.91 <7.05 <5.96 <4.37 <4.77 <6.73 <6.73 Station 10 (Control) 03/31/2014 04/30/2014 <4.87 <4.42 <10.00 <5.42 <8.54 <4.89 <10.90 <7.65 <4.70 <4.65 <10.60 <10.60 Station 8 (Indicator) 04/30/2014 05/31/2014 <3.78 <5.74 <11.20 <5.37 <10.40 <4.71 <9.57 <8.53 <5.64 <5.00 <7.25 <7.25 Station 10 (Control) 04/30/2014 05/31/2014 <3.90 <3.62 <8.91 <4.95 <8.69 <5.03 <6.67 <9.09 <3.90 <3.87 <7.60 <7.60 Station 8 (Indicator) 05/31/2014 06/30/2014 <1.98 <2.04 <3.71 <1.67 <4.21 <2.02 <3.34 <3.75 <2.07 <2.57 <4.01 <4.01 Station 10 (Control) 05/31/2014 06/30/2014 <1.67 <1.85 <4.41 <2.06 <3.87 <2.13 <3.22 <4.00 <2.05 <1.99 <3.13 <3.13 Station 8 (Indicator) 06/30/2014 07/31/2014 <3.62 <2.93 <6.73 <2.99 <6.35 <3.16 <5.33 <5.44 <3.44 <3.53 <5.40 <5.40 Station 10 (Control) 06/30/2014 07/31/2014 <2.94 <3.09 <6.01 <3.42 <7.13 <3.54 <5.72 <5.08 <3.90 <3.36 <5.68 <5.68 Station 8 (Indicator) 07/31/2014 08/31/2014 <1.90 <1.86 <3.70 <1.90 <3.77 <1.99 <3.25 <2.89 <1.90 <1.91 <2.75 <2.75 Station 10 (Control) 07/31/2014 08/31/2014 <1.95 <1.91 <4.17 <2.16 <3.69 <2.00 <3.51 <3.04 <2.35 <1.98 <3.41 <3.41 Station 8 (Indicator) 08/31/2014 09/30/2014 <3.46 <3.55 <8.19 <4.31 <8.10 <3.40 <7.74 <4.87 <4.37 <4.41 <3.28 <3.28 Station 10 (Control) 08/31/2014 09/30/2014 <1.40 <1.38 <3.05 <1.71 <3.17 <1.46 <2.76 <2.02 <1.61 <1.85 <2.00 <2.00 Station 8 (Indicator) 09/30/2014 10/31/2014 <4.55 <4.01 <9.18 <4.28 <10.20 <5.40 <8.95 <8.66 <5.76 <5.38 <10.10 <10.10 Station 10 (Control) 09/30/2014 10/31/2014 <4.06 <4.98 <7.54 <4.64 <9.06 <5.41 <5.25 <8.88 <5.90 <5.24 <7.89 <7.89 Station 8 (Indicator) 10/31/2014 11/30/2014 <5.14 <5.08 <10.40 <5.20 <9.18 <5.13 <10.10 <10.70 <5.58 <5.60 <6.74 <6.74 Station 10 (Control) 10/31/2014 11/30/2014 <3.37 <3.95 <10.20 <4.84 <10.30 <5.16 <8.45 <8.80 <4.35 <3.81 <4.92 <4.92 Station 8 (Indicator) 11/30/2014 12/31/2014 <3.92 <3.89 <8.66 <4.48 <7.11 <4.52 <7.43 <7.24 <4.55 <4.44 <6.26 <6.26 Station 10 (Control) 11/30/2014 12/31/2014 <5.72 <5.53 <9.45 <4.88 <10.30 <6.01 <9.53 <8.05 <6.68 <5.56 <11.10 <11.10

Enclosure to 0CAN051502 Page 34 of 108 Table 3.2 Sample Type: Surface Water Analysis: Tritium Units: pCi/l Location Begin Date End Date H-3 Required LLD 3000 Station 8 (Indicator) 12/31/2013 03/31/2014 745 Station 10 (Control) 12/31/2013 03/31/2014 < 334 Station 8 (Indicator) 03/31/2014 06/30/2014 344 Station 10 (Control) 03/31/2014 06/30/2014 < 243 Station 8 (Indicator) 06/30/2014 09/30/2014 546 Station 10 (Control) 06/30/2014 09/30/2014 < 343 Station 8 (Indicator) 09/30/2014 12/31/2014 583 Station 10 (Control) 09/30/2014 12/31/2014 < 323

Enclosure to 0CAN051502 Page 35 of 108 Table 4.1 Sample Type: Drinking Water Analysis: Gross Beta, Iodine-131, Gamma Isotopic Units: pCi/l Collection Gross Location I-131 Mn-54 Co-58 Fe-59 Co-60 Zn-65 Nb-95 Zr-95 Cs-134 Cs-137 Ba-140 La-140 Date Beta Required LLD 4.0 1.0 15 15 30 15 30 15 30 15 18 60 15 Station 14 (Indicator) 03/11/2014 < 3.08 < 0.81 < 3.95 < 4.58 < 7.62 < 5.82 < 8.98 < 4.50 < 8.17 < 4.39 < 5.02 < 7.81 < 7.81 Station 57 (Control) 03/11/2014 < 3.47 < 0.804 < 4.47 < 4.27 < 9.84 < 5.50 < 6.48 < 4.33 < 6.83 < 5.54 < 5.23 < 4.32 < 4.32 Station 14 (Indicator) 06/17/2014 < 2.62 < 0.83 < 4.38 < 4.10 < 7.51 < 3.12 < 6.70 < 4.15 < 7.00 < 4.85 < 4.20 < 4.07 < 4.07 Station 57 (Control) 06/17/2014 < 2.71 < 0.876 < 3.51 < 4.10 < 8.86 < 4.56 < 9.97 < 4.24 < 7.45 < 4.64 < 4.31 < 5.68 < 5.68 Station 14 (Indicator) 08/26/2014 < 2.71 < 0.88 < 2.47 < 4.32 < 8.82 < 3.46 < 8.36 < 3.37 < 6.25 < 4.32 < 4.65 < 7.15 < 7.15 Station 57 (Control) 08/26/2014 < 2.55 < 0.826 < 4.34 < 4.04 < 11.60 < 4.59 < 9.86 < 5.16 < 8.32 < 4.10 < 5.26 < 11.40 < 11.40 Station 14 (Indicator) 11/18/2014 < 2.79 < 0.83 < 3.79 < 3.05 < 6.17 < 3.48 < 6.05 < 2.83 < 4.68 < 3.38 < 2.91 < 3.79 < 3.79 Station 57 (Control) 11/18/2014 < 3.10 < 0.792 < 2.10 < 2.50 < 5.07 < 2.66 < 6.38 < 2.47 < 4.67 < 3.22 < 3.24 < 4.06 < 4.06

Enclosure to 0CAN051502 Page 36 of 108 Table 4.2 Sample Type: Drinking Water Analysis: Tritium Units: pCi/l Location Collection Date H-3 Required LLD 2000 Station 14 (Indicator) 03/11/2014 < 300 Station 57 (Control) 03/11/2014 < 296 Station 14 (Indicator) 06/17/2014 < 317 Station 57 (Control) 06/17/2014 < 314 Station 14 (Indicator) 08/26/2014 < 295 Station 57 (Control) 08/26/2014 < 297 Station 14 (Indicator) 11/18/2014 < 330 Station 57 (Control) 11/18/2014 < 329 Table 5.1 Sample Type: Sediment Analysis: Gamma Isotopic Units: pCi/kg Location Collection Date Cs-134 Cs-137 Required LLD 150 180 Station 8 (Indicator) 10/24/2014 < 83.30 < 67.70 Station 16 (Control)* 10/24/2014 < 67.50 < 59.10 Table 6.1 Sample Type: Fish Analysis: Gamma Isotopic Units: pCi/kg Location Collection Date Mn-54 Co-58 Fe-59 Co-60 Zn-65 Cs-134 Cs-137 Required LLD 130 130 260 130 260 130 150 Station 8 (Indicator) 10/24/2014 < 8.88 < 8.64 < 23.70 < 8.81 < 19.50 < 83.30 < 67.70 Station 16 (Control) 10/24/2014 < 8.61 < 9.01 < 27.60 < 9.96 < 24.70 < 67.50 < 59.10

Enclosure to 0CAN051502 Page 37 of 108 Table 7.1 Sample Type: Food Products Analysis: Iodine-131, Gamma Isotopic Units: pCi/kg Location Collection Date I-131 Cs-134 Cs-137 Required LLD 60 60 80 Station 13 (Indicator) 06/03/2014 < 33.50 < 29.90 < 28.60 Station 55 (Control) 06/03/2014 < 37.10 < 35.40 < 38.80 Station 13 (Indicator) 07/01/2014 < 20.40 < 12.70 < 12.10 Station 55 (Control) 07/01/2014 < 23.90 < 15.20 < 14.40 Station 13 (Indicator) 08/18/2014 < 51.5 < 28.4 < 31.00 Station 55 (Control) 08/18/2014 < 47.5 < 26.3 < 25.60

Enclosure to 0CAN051502 Page 38 of 108 Table 8.1 Sample Type: Groundwater Analysis: Iodine-131, Gamma Isotopic Units: pCi/l Collection Sample # I-131 Mn-54 Co-58 Fe-59 Co-60 Zn-65 Nb-95 Zr-95 Cs-134 Cs-137 Ba-140 La-140 Date Required LLD 15 15 15 30 15 30 15 30 15 18 60 15 58* 02/18/2014 < 7.79 < 3.41 < 4.14 < 9.23 < 5.05 < 6.61 < 4.71 < 6.51 < 4.27 < 4.38 < 6.53 < 6.53 62* 02/18/2014 < 10.70 < 4.76 < 6.41 < 13.50 < 5.70 < 12.90 < 4.80 < 9.56 < 8.17 < 6.27 < 14.10 < 14.10 63 02/19/2014 < 7.58 < 4.16 < 3.56 < 6.06 < 3.80 < 9.80 < 4.10 < 7.16 < 3.31 < 4.54 < 6.19 < 6.19 64 02/18/2014 < 10.20 < 4.04 < 4.89 < 11.10 < 6.23 < 9.48 < 6.32 < 8.31 < 5.41 < 4.97 < 10.20 < 10.20 58* 04/28/2014 < 7.67 < 5.66 < 4.27 < 9.94 < 5.86 < 7.12 < 5.15 < 8.60 < 3.92 < 4.18 < 8.23 < 8.23 62* 04/28/2014 < 8.09 < 4.67 < 4.09 < 9.94 < 3.46 < 7.22 < 4.26 < 6.70 < 4.92 < 5.81 < 7.66 < 7.66 63 04/28/2014 < 9.50 < 5.00 < 4.97 < 9.24 < 6.16 < 11.00 < 5.35 < 10.20 < 5.33 < 5.26 < 8.18 < 8.18 64 04/29/2014 < 6.63 < 4.87 < 4.56 < 11.20 < 5.09 < 11.80 < 5.78 < 6.54 < 5.92 < 5.47 < 7.54 < 7.54 58* 08/26/2014 < 7.10 < 1.77 < 1.85 < 4.09 < 1.97 < 3.43 < 1.88 < 3.21 < 1.98 < 1.69 < 5.18 < 5.18 62* 08/26/2014 < 8.17 < 1.86 < 2.23 < 4.71 < 2.27 < 4.24 < 2.29 < 3.92 < 2.25 < 2.13 < 5.35 < 5.35 63 08/26/2014 < 13.80 < 3.07 < 3.55 < 7.43 < 3.23 < 6.82 < 3.86 < 5.88 < 3.65 < 3.12 < 9.16 < 9.16 64 08/25/2014 < 5.30 < 1.33 < 1.55 < 3.51 < 1.60 < 3.11 < 1.67 < 2.80 < 1.60 < 1.57 < 3.70 < 3.70 58* 10/27/2014 < 3.09 < 1.89 < 1.93 < 3.80 < 2.07 < 3.88 < 2.42 < 3.37 < 2.13 < 2.04 < 3.33 < 3.33 62* 10/27/2014 < 2.66 < 1.64 < 1.67 < 3.21 < 1.83 < 3.42 < 1.77 < 3.12 < 1.81 < 1.75 < 2.70 < 2.70 63 10/27/2014 < 2.08 < 1.42 < 1.36 < 2.88 < 1.35 < 2.99 < 1.43 < 2.60 < 1.66 < 1.89 < 2.31 < 2.31 64 10/27/2014 < 4.98 < 1.89 < 2.00 < 3.24 < 2.00 < 3.93 < 2.40 < 3.62 < 1.90 < 2.12 < 4.23 < 4.23

Identifies Control Locations

Enclosure to 0CAN051502 Page 39 of 108 Table 8.2 Sample Type: Groundwater Analysis: Tritium Units: pCi/l Location Collection Date H-3 Required LLD 3000 Station 58 (Control) 02/18/2014 < 249 Station 62 (Control) 02/18/2014 < 246 Station 63 (Indicator) 02/19/2014 < 252 Station 64 (Indicator) 02/18/2014 < 277 Station 58 (Control) 04/28/2014 < 279 Station 62 (Control) 04/28/2014 < 281 Station 63 (Indicator) 04/28/2014 < 281 Station 64 (Indicator) 04/29/2014 < 283 Station 58 (Control) 08/26/2014 < 293 Station 62 (Control) 08/26/2014 < 291 Station 63 (Indicator) 08/26/2014 < 287 Station 64 (Indicator) 08/25/2014 < 318 Station 58 (Control) 10/27/2014 < 341 Station 62 (Control) 10/27/2014 < 339 Station 63 (Indicator) 10/27/2014 < 338 Station 64 (Indicator) 10/27/2014 < 327

Enclosure to 0CAN051502 Page 40 of 108 ATTACHMENT 2 INTERLABORATORY COMPARISON PROGRAM

Enclosure to 0CAN051502 Page 41 of 108 GEL LABORATORIES LLC 2014 ANNUAL QUALITY ASSURANCE REPORT FOR THE RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (REMP)

Enclosure to 0CAN051502 Page 42 of 108 TABLE OF CONTENTS

1. Introduction ........................................................................................................................ 43

2. Quality Assurance Programs for Inter-laboratory, Intra-laboratory and Third Party Cross-Check .................................................................................................... 44

3. Quality Assurance Program for Internal and External Audits ............................................. 45

4. Performance Evaluation Acceptance Criteria for Environmental Sample Analysis............ 46

5. Performance Evaluation Samples ...................................................................................... 46

6. Quality Control Program for Environmental Sample Analysis ............................................ 46

7. Summary of Data Results .................................................................................................. 47

8. Summary of Participation in the Eckert & Ziegler Analytics Environmental Cross-Check Program ....................................................................................................... 48

9. Summary of Participation in the MAPEP Monitoring Program ........................................... 48

10. Summary of Participation in the ERA MRaD PT Program ................................................. 48

11. Summary of Participation in the ERA PT Program ............................................................ 48

12. Corrective Action Request and Report (CARR) ................................................................. 48

13. References ......................................................................................................................... 49 TABLES Table 1 2014 Radiological Proficiency Testing Results and Acceptance Criteria................. 50 Table 2 2014 Eckert & Ziegler Analytics Performance Evaluation Results ........................... 68 Table 3 2014 Department of Energy Mixed Analyte Performance Evaluation Program (MAPEP) Results................................................................. 71 Table 4 2014 ERA Program Performance Evaluation Results ............................................. 79 Table 5 2014 ERA Program (MRAD) Performance Evaluation Results ............................... 81 Table 6 REMP Intra-Laboratory Data Summary: Bias and Precision By Matrix ................... 93 Table 7 All Radiological Intra-Laboratory Data Summary: Bias and Precision By Matrix ..... 95 Table 8 2014 Corrective Action Report Summary ............................................................ 1044 FIGURES Figure 1 Cobalt-60 Performance Evaluation Results and % Bias .......................................... 88 Figure 2 Cesium-137 Performance Evaluation Results and % Bias ..................................... 88 Figure 3 Tritium Performance Evaluation Results and % Bias .............................................. 89 Figure 4 Strontium-90 Performance Evaluation Results and % Bias ..................................... 89 Figure 5 Gross Alpha Performance Evaluation Results and % Bias...................................... 90 Figure 6 Gross Beta Performance Evaluation Results and % Bias ....................................... 90 Figure 7 Iodine-131 Performance Evaluation Results and % Bias ........................................ 91 Figure 8 Americium-241 Performance Evaluation Results and % Bias ................................. 91 Figure 9 Plutonium-238 Performance Evaluation Results and % Bias .................................. 92

Enclosure to 0CAN051502 Page 43 of 108 2014 ANNUAL QUALITY ASSURANCE REPORT FOR THE RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (REMP)

1. Introduction GEL Laboratories, LLC (GEL) is a privately owned environmental laboratory dedicated to providing personalized client services of the highest quality. GEL was established as an analytical testing laboratory in 1981. Now a full service lab, our analytical divisions use state of the art equipment and methods to provide a comprehensive array of organic, inorganic, and radiochemical analyses to meet the needs of our clients.

At GEL, quality is emphasized at every level of personnel throughout the company.

Managements ongoing commitment to good professional practice and to the quality of our testing services to our customers is demonstrated by their dedication of personnel and resources to develop, implement, assess, and improve our technical and management operations.

The purpose of GELs quality assurance program is to establish policies, procedures, and processes to meet or exceed the expectations of our clients. To achieve this, all personnel that support these services to our clients are introduced to the program and policies during their initial orientation, and annually thereafter during company-wide training sessions.

GELs primary goals are to ensure that all measurement data generated are scientifically and legally defensible, of known and acceptable quality per the data quality objectives (DQOs), and thoroughly documented to provide sound support for environmental decisions. In addition, GEL continues to ensure compliance with all contractual requirements, environmental standards, and regulations established by local, state and federal authorities.

GEL administers the QA program in accordance with the Quality Assurance Plan, GL-QS-B-001.

Our Quality Systems include all quality assurance (QA) policies and quality control (QC) procedures necessary to plan, implement, and assess the work we perform. GELs QA Program establishes a quality management system (QMS) that governs all of the activities of our organization.

This report entails the quality assurance program for the proficiency testing and environmental monitoring aspects of GEL for 2014. GELs QA Program is designed to monitor the quality of analytical processing associated with environmental, radiobioassay, effluent (10 CFR Part 50),

and waste (10 CFR Part 61) sample analysis.

This report covers the category of Radiological Environmental Monitoring Program (REMP) and includes:

Intra-laboratory QC results analyzed during 2014.

Inter-laboratory QC results analyzed during 2014 where known values were available.

Enclosure to 0CAN051502 Page 44 of 108

2. Quality Assurance Programs for Inter-laboratory, Intra-laboratory and Third Party Cross-Check In addition to internal and client audits, our laboratory participates in annual performance evaluation studies conducted by independent providers. We routinely participate in the following types of performance audits:

Proficiency testing and other inter-laboratory comparisons Performance requirements necessary to retain Certifications Evaluation of recoveries of certified reference and in-house secondary reference materials using statistical process control data.

Evaluation of relative percent difference between measurements through SPC data.

We also participate in a number of proficiency testing programs for federal and state agencies and as required by contracts. It is our policy that no proficiency evaluation samples be analyzed in any special manner. Our annual performance evaluation participation generally includes a combination of studies that support the following:

US Environmental Protection Agency Discharge Monitoring Report, Quality Assurance Program (DMR-QA). Annual national program sponsored by EPA for laboratories engaged in the analysis of samples associated with the NPDES monitoring program.

Participation is mandatory for all holders of NPDES permits. The permit holder must analyze for all of the parameters listed on the discharge permit. Parameters include general chemistry, metals, BOD/COD, oil and grease, ammonia, nitrates, etc.

Department of Energy Mixed Analyte Performance Evaluation Program (MAPEP).

A semiannual program developed by DOE in support of DOE contractors performing waste analyses. Participation is required for all laboratories that perform environmental analytical measurements in support of environmental management activities. This program includes radioactive isotopes in water, soil, vegetation and air filters.

ERAs MRAD-Multimedia Radiochemistry Proficiency test program. This program is for labs seeking certification for radionuclides in wastewater and solid waste. The program is conducted in strict compliance with USEPA National Standards for Water Proficiency study.

ERAs InterLaB RadCheM Proficiency Testing Program for radiological analyses. This program completes the process of replacing the USEPA EMSL-LV Nuclear Radiation Assessment Division program discontinued in 1998. Laboratories seeking certification for radionuclide analysis in drinking water also use the study. This program is conducted in strict compliance with the USEPA National Standards for Water Proficiency Testing Studies. This program encompasses Uranium by EPA method 200.8 (for drinking water certification in Utah/Primary NELAP), gamma emitters, Gross Alpha/Beta, Iodine-131, naturally occurring radioactive isotopes, Strontium-89/90, and Tritium.

ERAs Water Pollution (WP) biannual program for waste methodologies includes parameters for both organic and inorganic analytes.

Enclosure to 0CAN051502 Page 45 of 108 ERAs Water Supply (WS) biannual program for drinking water methodologies includes parameters for organic and inorganic analytes.

Environmental Cross-Check Program administered by Eckert & Ziegler Analytics, Inc.

This program encompasses radionuclides in water, soil, milk, naturally occurring radioactive isotopes in soil and air filters.

GEL procures single-blind performance evaluation samples from Eckert & Ziegler Analytics to verify the analysis of sample matrices processed at GEL. Samples are received on a quarterly basis. GELs Third-Party Cross-Check Program provides environmental matrices encountered in a typical nuclear utility REMP. The Third-Party Cross-Check Program is intended to meet or exceed the inter-laboratory comparison program requirements discussed in NRC Regulatory Guide 4.15. Once performance evaluation samples have been prepared in accordance with the instructions provided by the PT provider, samples are managed and analyzed in the same manner as environmental samples from GELs clients.

3. Quality Assurance Program for Internal and External Audits During each annual reporting period, at least one internal assessment of each area of the laboratory is conducted in accordance with the pre-established schedule from Standard Operating Procedure for the Conduct of Quality Audits, GL-QS-E-001. The annual internal audit plan is reviewed for adequacy and includes the scheduled frequency and scope of quality control actions necessary to GELs QA program. Internal audits are conducted at least annually in accordance with a schedule approved by the Quality Systems Director. Supplier audits are contingent upon the categorization of the supplier, and may or may not be conducted prior to the use of a supplier or subcontractor. Type I suppliers and subcontractors, regardless of how they were initially qualified, are re-evaluated at least once every three years.

In addition, prospective customers audit GEL during pre-contract audits. GEL hosts several external audits each year for both our clients and other programs. These programs include environmental monitoring, waste characterization, and radiobioassay. The following list of programs may audit GEL at least annually or up to every three years depending on the program.

NELAC, National Environmental Laboratory Accreditation Program DOECAP, U.S. Department of Energy Consolidated Audit Program DOELAP, U.S. Department of Energy Laboratory Accreditation Program DOE QSAS, U.S. Department of Energy, Quality Systems for Analytical Services ISO/IEC 17025:2005 A2LA, American Association for Laboratory Accreditation DOD ELAP, US Department of Defense Environmental Accreditation Program NUPIC, Nuclear Procurement Issues Committee South Carolina Department of Heath and Environmental Control (SC DHEC)

The annual radiochemistry laboratory internal audit (13-RAD-001) was conducted in July, 2014.

One (1) finding, four (4) observations, and eight (8) recommendations resulted from this assessment. By September, 2014, the finding was closed and appropriate laboratory staff addressed each observation and recommendation.

Enclosure to 0CAN051502 Page 46 of 108

4. Performance Evaluation Acceptance Criteria for Environmental Sample Analysis GEL utilized an acceptance protocol based upon two performance models. For those inter-laboratory programs that already have established performance criteria for bias (i.e.,

MAPEP, and ERA/ELAP), GEL will utilize the criteria for the specific program. For intra-laboratory or third party quality control programs that do not have a specific acceptance criteria (i.e. the Eckert-Ziegler Analytics Environmental Cross-check Program), results will be evaluated in accordance with GELs internal acceptance criteria.

5. Performance Evaluation Samples Performance Evaluation (PE) results and internal quality control sample results are evaluated in accordance with GEL acceptance criteria. The first criterion concerns bias, which is defined as the deviation of any one result from the known value. The second criterion concerns precision, which deals with the ability of the measurement to be replicated by comparison of an individual result with the mean of all results for a given sample set.

At GEL, we also evaluate our analytical performance on a regular basis through statistical process control (SPC) acceptance criteria. Where feasible, this criterion is applied to both measures of precision and accuracy and is specific to sample matrix. We establish environmental process control limits at least annually.

For Radiochemistry analysis, quality control evaluation is based on static limits rather than those that are statistically derived. Our current process control limits are maintained in GELs AlphaLIMS. We also measure precision with matrix duplicates and/or matrix spike duplicates.

The upper and lower control limits (UCL and LCL respectively) for precision are plus or minus three times the standard deviation from the mean of a series of relative percent differences.

The static precision criteria for radiochemical analyses are 0 - 20%, for activity levels exceeding the contract required detection limit (CRDL).

6. Quality Control Program for Environmental Sample Analysis GELs internal QA Program is designed to include QC functions such as instrumentation calibration checks (to insure proper instrument response), blank samples, instrumentation backgrounds, duplicates, as well as overall staff qualification analyses and statistical process controls. Both quality control and qualification analyses samples are used to be as similar as the matrix type of those samples submitted for analysis by the various laboratory clients. These performance test samples (or performance evaluation samples) are either actual sample submitted in duplicate in order to evaluate the precision of laboratory measurements, or fortified blank samples, which have been given a known quantity of a radioisotope that is in the interest to GELs clients.

Accuracy (or Bias) is measured through laboratory control samples and/or matrix spikes, as well as surrogates and internal standards. The UCLs and LCLs for accuracy are plus or minus three times the standard deviation from the mean of a series of recoveries. The static limit for radiochemical analyses is 75 - 125%. Specific instructions for out-of-control situations are provided in the applicable analytical SOP.

Enclosure to 0CAN051502 Page 47 of 108 GELs Laboratory Control Standard (LCS) is an aliquot of reagent water or other blank matrix to which known quantities of the method analytes are added in the laboratory. The LCS is analyzed exactly like a sample, and its purpose is to determine whether the methodology is in control, and whether the laboratory is capable of making accurate and precise measurements.

Some methods may refer to these samples as Laboratory Fortified Blanks (LFB). The requirement for recovery is between 75 and 125% for radiological analyses excluding drinking water matrix.

Bias (%) = (observed concentration)

100 %

(known concentration)

Precision is a data quality indicator of the agreement between measurements of the same property, obtained under similar conditions, and how well they conform to themselves.

Precision is usually expressed as standard deviation, variance or range in either absolute or relative (percentage) terms.

GELs laboratory duplicate (DUP or LCSD) is an aliquot of a sample taken from the same container and processed in the same manner under identical laboratory conditions. The aliquot is analyzed independently from the parent sample and the results are compared to measure precision and accuracy.

If a sample duplicate is analyzed, it will be reported as Relative Percent Difference (RPD). The RPD must be 20 percent or less, if both samples are greater than 5 times the MDC. If both results are less than 5 times MDC, then the RPD must be equal to or less than 100%. If one result is above the MDC and the other is below the MDC, then the RPD can be calculated using the MDC for the result of the one below the MDC. The RPD must be 100% or less. In the situation where both results are above the MDC but one result is greater than 5 times the MDC and the other is less than 5 times the MDC, the RPD must be less than or equal to 20%. If both results are below MDC, then the limits on % RPD are not applicable.

Difference (%) = (high duplicate result - low duplicate result)

100 %

(average of results)

7. Summary of Data Results During 2013, forty-four (44) radioisotopes associated with seven (7) matrix types were analyzed under GELs Performance Evaluation program in participation with ERA, MAPEP, and Eckert &

Ziegler Analytics. Matrix types were representative of client analyses performed during 2014.

Of the four hundred forty-five (445) total results reported, 98.6% (439 of 445) were found to be acceptable. The list below contains the type of matrix evaluated by GEL.

Air Filter Cartridge Water Milk Soil Liquid Vegetation

Enclosure to 0CAN051502 Page 48 of 108 Graphs are provided in Figures 1-9 of this report to allow for the evaluation of trends or biases.

These graphs include radioisotopes Cobalt-60, Cesium-137, Tritium, Strontium-90, Gross Alpha, Gross Beta, Iodine-131, Americium-241, and Plutonium-238.

8. Summary of Participation in the Eckert & Ziegler Analytics Environmental Cross-Check Program Eckert & Ziegler Analytics provided samples for sixty-nine (69) individual environmental analyses. The accuracy of each result reported to Eckert & Ziegler Analytics, Inc. is measured by the ratio of GELs result to the known value. All results fell within GELs acceptance criteria (100%).

9. Summary of Participation in the MAPEP Monitoring Program MAPEP Series 30 and 31 were analyzed by the laboratory. Of the one hundred thirty-eight (138) analyses, 97.8% (135 out of 138) of all results fell within the PT providers acceptance criteria. Three analytical failures occurred: Uranium-234/233 and Uranium-238 in Soil and Uranium-238 in vegetation.

For the corrective actions associated with MAPEP Series 30, refer to CARR 140605-879 which is detailed in Table 8.

10. Summary of Participation in the ERA MRaD PT Program The ERA MRad program provided samples (MRAD-20 and MRAD-21) for one hundred eighty-eight (188) individual environmental analyses. One hundred eighty-seven (187) of the 188 analyses fell within the PT providers acceptance criteria (99.4%). One analytical failure occurred: Americium-241 in water.

For the corrective actions associated with MRAD-20, refer to CARR140520-874 which are detailed in Table 8.

11. Summary of Participation in the ERA PT Program The ERA program provided samples (RAD-96, RAD-98, and 011014L) for fifty (50) individual environmental analyses. Of the 50 analyses, 98% (49 out of 50) of all results fell within the PT providers acceptance criteria. One analytical failure occurred: Strontium-89 in water.

For the corrective actions associated with RAD-98 refer to corrective actions CARR140825-902 (Table 8).

12. Corrective Action Request and Report (CARR)

There are two categories of corrective action at GEL. One is corrective action implemented at the analytical and data review level in accordance with the analytical SOP. The other is formal corrective action documented by the Quality Systems Team in accordance with GL-QS-E-002.

A formal corrective action is initiated when a nonconformance reoccurs or is so significant that permanent elimination or prevention of the problem is required. Formal corrective action investigations include root cause analysis.

Enclosure to 0CAN051502 Page 49 of 108 GEL includes quality requirements in most analytical standard operating procedures to ensure that data are reported only if the quality control criteria are met or the quality control measures that did not meet the acceptance criteria are documented. A formal corrective action is implemented according to GL-QS-E-002 for Conducting Corrective/Preventive Action and Identifying Opportunities for Improvement. Recording and documentation is performed following guidelines stated in GL-QS-E-012 for Client NCR Database Operation.

Any employee at GEL can identify and report a nonconformance and request that corrective action be taken. Any GEL employee can participate on a corrective action team as requested by the QS team or Group Leaders. The steps for conducting corrective action are detailed in GL-QS-E-002. In the event that correctness or validity of the laboratorys test results in doubt, the laboratory will take corrective action. If investigations show that the results have been impacted, affected clients will be informed of the issue in writing within five (5) calendar days of the discovery.

Table 8 provides the status of CARRs for radiological performance testing during 2014. It has been determined that causes of the failures did not impact any data reported to our clients.

References

1. GEL Quality Assurance Plan, GL-QS-B-001

2. GEL Standard Operating Procedure for the Conduct of Quality Audits, GL-QS-E-001

3. GEL Standard Operating Procedure for Conducting Corrective/Preventive Action and Identifying Opportunities for Improvement, GL-QS-E-002

4. GEL Standard Operating Procedure for AlphaLIMS Documentation of Nonconformance Reporting and Dispositioning and Control of Nonconforming Items, GL-QS-E-004

5. GEL Standard Operating Procedure for Handling Proficiency Evaluation Samples, GL-QS-E-013

6. GEL Standard Operating Procedure for Quality Assurance Measurement Calculations and Processes, GL-QS-E-014

7. 40 CFR Part 136 Guidelines Establishing Test Procedures for the Analysis of Pollutants

8. ISO/IEC 17025-2005, General Requirements for the Competence of Testing and Calibration Laboratories

9. ANSI/ASQC E4-1994, Specifications and Guidelines for Quality Systems for Environmental Data Collection and Environmental Technology Programs, American National Standard

10. 2003 NELAC Standard, National Environmental Laboratory Accreditation Program

11. 2009 TNI Standard, The NELAC Institute, National Environmental Accreditation Program

12. MARLAP, Multi-Agency Radiological Laboratory Analytical Protocols

13. 10 CFR Part 21, Reporting of Defects and Noncompliance

14. 10 CFR Part 50 Appendix B, Quality Assurance Criteria for Nuclear Power Plants and Fuel Reprocessing Plants

15. 10 CFR Part 61, Licensing Requirements for Land Disposal and Radioactive Waste

16. NRC REG Guide 4.15 and NRC REG Guide 4.8

Enclosure to 0CAN051502 Page 50 of 108 TABLE 1 2014 RADIOLOGICAL PROFICIENCY TESTING RESULTS AND ACCEPTANCE CRITERIA Report PT Quarter / Sample Sample Acceptance Received Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio Date ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Barium-133 80.6 76.2 63.8-83.8 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Cesium-134 64.7 66.8 54.4-73.5 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Cesium-137 112.0 109 98.1-122 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Cobalt-60 95.0 88.7 79.8-99.9 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Zinc-65 200 185 166-218 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Gross Alpha 34.8 36.1 18.6-46.4 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Gross Beta 19.6 22.3 13.5-30.4 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Gross Alpha 34.6 36.1 18.6-46.4 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Radium-226 16.2 16.8 12.5-19.2 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Radium-228 4.62 5.04 3.01-6.67 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Uranium (Nat) 7.39 7.23 5.51-8.53 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water ug/L Uranium (Nat) mass 11.00 10.6 8.07-12.5 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Radium-226 15.10 16.8 12.5-19.2 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Radium-228 4.66 5.04 3.01-6.67 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Uranium (Nat) 7.47 7.23 5.51-8.53 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water ug/L Uranium (Nat) mass 11.4 10.6 8.07-12.5 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Tritium 3320 3580 3030-3950 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Strontium-89 44.1 44.4 34.4-51.6 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Strontium-90 34.2 30.3 22.1-35.2 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Strontium-89 38.9 44.4 34.4-51.6 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Strontium-90 27.1 30.3 22.1-35.2 Acceptable ERA 1st / 2014 02/06/14 011014L Water pCi/L Strontium-89 42.3 38.7 29.3-45.7 Acceptable ERA 1st / 2014 02/06/14 011014L Water pCi/L Strontium-89 42.2 38.7 29.3-45.7 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Iodine-131 25.2 24.4 20.2-28.9 Acceptable ERA 1st / 2014 02/24/14 RAD - 96 Water pCi/L Iodine-131 22.4 24.4 20.2-28.9 Acceptable EZA 1st / 2014 05/16/14 E10846 Cartridge pCi Iodine-131 7.83E+01 7.50E+03 1.04 Acceptable EZA 1st / 2014 05/16/14 E10847 Milk pCi/L Strontium-89 9.14E+01 9.17E+01 1 Acceptable

Enclosure to 0CAN051502 Page 51 of 108 Report PT Quarter / Sample Sample Acceptance Received Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio Date EZA 1st/2014 05/16/14 E10847 Milk pCi/L Strontium-90 1.27E+01 1.51E+01 0.84 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Iodine-131 9.84E+01 9.85E+01 1 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Cerium-141 1.21E+02 1.19E+02 1.02 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Cr-51 5.19E+02 4.91E+02 1.06 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Cesium-134 1.79E+02 2.10E+02 0.85 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Cesium-137 2.55E+02 2.53E+02 1.01 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Cobalt-58 2.58E+02 2.68E+02 0.96 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Mn-54 3.01E+02 2.97E+02 1.01 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Iron-59 2.24E+02 2.19E+02 1.02 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Zinc-65 3.45E+02 3.23E+02 1.07 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Cobalt-60 3.39E+02 3.37E+02 1.00 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Iodine-131 9.24E+01 8.99E+01 1.03 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Cerium-141 8.19E+01 7.71E+01 1.06 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Cr-51 3.32E+02 3.19E+02 1.04 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Cesium-134 1.27E+02 1.36E+02 0.93 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Cesium-137 1.69E+02 1.64E+02 1.03 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Cobalt-58 1.75E+02 1.74E+02 1.01 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Mn-54 2.08E+02 1.93E+02 1.08 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Iron-59 1.68E+02 1.42E+02 1.18 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Zinc-65 2.25E+02 2.10E+02 1.07 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Cobalt-60 2.31E+02 2.19E+02 1.02 Acceptable MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Filter Gross Alpha 1.980 1.77 0.53-3.01 Acceptable GrF30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Filter Gross Beta 0.823 0.77 0.39-1.16 Acceptable GrF30 sample MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Americium-241 65 68 47.6-88.4 Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Cesium-134 5.44 0 False Pos Test Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Cesium-137 1270 1238 867-1609 Acceptable MaS30

Enclosure to 0CAN051502 Page 52 of 108 Report PT Quarter / Sample Sample Acceptance Received Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio Date MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Cobalt-57 947 966 676-1256 Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Cobalt-60 0.581 1.220 Sens. Eval. Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Iron-55 580 643 444-824 Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Manganese-54 1470 1430 1001-1859 Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Nickel-63 6.95 0 False Pos Test Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Plutonium-238 89.7 96.0 67-125 Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Plutonium-239/240 69.80 76.8 53.8-99.8 Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Potassium-40 703 622 435-809 Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Strontium-90 1.48 0 False Pos Test Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Technetium-99 37.1 0 False Pos Test Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg U-234/233 30.5 81.0 57-105 Not Accept.

MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Uranium-238 35 83 58-108 Not Accept.

MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Zinc-65 766 695 487-904 Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Americium-241 0.759 0.720 0.504-0.936 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Cesium-134 21.4 23.1 16.2-30.0 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Cesium-137 29.70 28.9 20.2-37.6 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Cobalt-57 28.0 27.5 19.3-35.8 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Cobalt-60 16.6 16.0 11.2-20.8 Acceptable MaW30

Enclosure to 0CAN051502 Page 53 of 108 Report PT Quarter / Sample Sample Acceptance Received Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio Date MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Hydrogen-3 308 321 225-417 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Iron-55 0.3 0.0 False Pos Test Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Manganese-54 14.4 13.9 9.7-18.1 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Nickel-63 31.4 34.0 23.8-44.2 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Plutonium-238 0.764 0.828 0.580-1.076 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Pu-239/240 0.6590 0.6760 0.473-0.879 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Potassium-40 0.460 0 False Pos Test Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Strontium-90 8.32 8.51 5.96-11.06 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Technetium-99 9.5 10.3 7.2-13.4 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L U-234/233 0.210 0.225 0.158-0.293 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Uranium-238 1.41 1.45 1.02-1.89 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Zinc-65 -0.126 0.0 False Pos Test Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Gross Alpha 0.96 0.85 0.255-1.443 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Gross Beta 4.7 4.2 2.10-6.29 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Iodine-129 0.0227 0.00 False Pos Test Acceptable MaW30 MAPEP ug/

MAPEP 2nd/2014 06/05/14 Filter Uranium-235 0.018 0.020 0.014-0.026 Acceptable RdF30 sample MAPEP ug/

MAPEP 2nd/2014 06/05/14 Filter Uranium-238 8.77 10.4 7.3-13.5 Acceptable RdF30 sample MAPEP ug/

MAPEP 2nd/2014 06/05/14 Filter Uranium-Total 8.80 10.4 7.3-13.5 Acceptable RdF30 sample

Enclosure to 0CAN051502 Page 54 of 108 Report PT Quarter / Sample Sample Acceptance Received Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio Date MAPEP ug/

MAPEP 2nd/2014 06/05/14 Filter Americium-241 0.086 0.090 0.063-0.117 Acceptable RdF30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Filter Cesium-134 1.85 1.91 1.34-2.48 Acceptable RdF30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Filter Cesium-137 1.81 1.76 1.23-2.29 Acceptable RdF30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Filter Cobalt-57 0.0757 0.00 False Pos Test Acceptable RdF30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Filter Cobalt-60 1.490 1.39 0.97-1.81 Acceptable RdF30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Filter Manganese-54 0.0138 0.00 False Pos Test Acceptable RdF30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Filter Plutonium-238 0.000819 0.00090 Sens. Eval. Acceptable RdF30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Filter Pu-239/240 0.071 0.7720 0.054-0.1004 Acceptable RdF30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Filter Strontium-90 1.19 1.18 0.83-1.53 Acceptable RdF30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Filter U-234/233 0.0159 0.0195 0.0137-0.0254 Acceptable RdF30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Filter Uranium-238 0.118 0.129 0.090-0.168 Acceptable RdF30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Filter Zinc-65 0.246 0.00 False Pos Test Acceptable RdF30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Filter Gross Alpha 0.656 1.20 0.36-2.04 Acceptable RdF30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Filter Gross Beta 0.95 0.85 0.43-1.28 Acceptable RdF30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Filter Americium-241 0.106 0.104 0.073-0.135 Acceptable RdF30 sample MAPEP ug/

MAPEP 2nd/2014 06/05/14 Vegetation Uranium-235 0.261 0.0268 0.0188-0.0348 Not Accept.

RdV30 sample MAPEP ug/

MAPEP 2nd/2014 06/05/14 Vegetation Uranium-238 12.7 13.3 9.3-17.3 Acceptable RdV30 sample MAPEP ug/

MAPEP 2nd/2014 06/05/14 Vegetation Uranium-Total 12.7 13.3 9.3-17.3 Acceptable RdV30 sample

Enclosure to 0CAN051502 Page 55 of 108 Report PT Quarter / Sample Sample Acceptance Received Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio Date MAPEP ug/

MAPEP 2nd/2014 06/05/14 Vegetation Americium-241 0.1100 0.108 0.076-0.140 Acceptable RdV30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Vegetation Cesium-134 5.65 6.04 4.23-7.85 Acceptable RdV30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Vegetation Cesium-137 4.98 4.74 3.32-6.16 Acceptable RdV30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Vegetation Cobalt-57 11.1 10.1 7.1-13.1 Acceptable RdV30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Vegetation Cobalt-60 7.21 6.93 4.85-9.01 Acceptable RdV30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Vegetation Manganese-54 9.24 8.62 6.03-11.21 Acceptable RdV30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Vegetation Plutonium-238 0.116 0.121 0.085-0.157 Acceptable RdV30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Vegetation Pu-239/240 0.134 0.154 0.108-0.0200 Acceptable RdV30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Vegetation Strontium-90 1.580 1.46 1.02-1.90 Acceptable RdV30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Vegetation U-234/233 0.2640 0.2530 0.0177-0.0329 Acceptable RdV30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Vegetation Uranium-238 0.174 0.165 0.116-0.215 Acceptable RdV30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Vegetation Zinc-65 8.87 7.00 4.38-8.13 Acceptable RdV30 sample ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Actinium-228 1140 1240 795-1720 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Americium-241 418 399 233-518 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Bismuth-212 976 1240 330-1820 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Bismuth-214 2290 1960 1180-2820 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Cesium-134 3080 3390 2220-4070 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Cesium-137 8310 8490 6510-10900 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Cobalt-60 6570 6830 4620-9400 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Lead-212 1330 1240 812-1730 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Lead-214 2800 2070 1210-3090 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Manganese-54 <44.3 <1000 0-1000 Acceptable

Enclosure to 0CAN051502 Page 56 of 108 Report PT Quarter / Sample Sample Acceptance Received Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio Date ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Plutonium-238 579 578 348-797 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Plutonium-239 488 471.00 308-651 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Potassium-40 10500 10500 7660-14100 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Strontium-90 2500 2780 1060-4390 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Thorium-234 3420 3360 1060-6320 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Zinc-65 5700 5400 4300-7180 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Strontium-90 6730 8530 3250-13500 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Uranium-234 2602 3390 2070-4350 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Uranium-238 2425 3360 2080-4260 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Uranium-Total 5027 6910 3750-9120 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil ug/kg Uranium-Total(mass) 7110 10100 5570-12700 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Uranium-234 3440 3390 2070-4350 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Uranium-238 3680 3360 2080-4260 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Uranium-Total 7310 6910 3750-9120 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil ug/kg Uranium-Total (mass) 11000 10100 5570-12700 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Uranium-234 3740 3390 2070-4350 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Uranium-238 3780 3360 2080-4260 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil pCi/kg Uranium-Total 7683 6910 3750-9120 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil ug/kg Uranium-Total (mass) 11300 10100 5570-12700 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Soil ug/kg Uranium-Total (mass) 11200 10100 5570-12700 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Vegetation pCi/kg Americium-241 1670 1490 911-1980 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Vegetation pCi/kg Cesium-134 657 646 415-839 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Vegetation pCi/kg Cesium-137 861 880 638-1220 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Vegetation pCi/kg Cobalt-60 997 926 639-1290 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Vegetation pCi/kg Curium-244 514 516 253-804 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Vegetation pCi/kg Manganese-54 <62.2 <300 0.00-300 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Vegetation pCi/kg Plutonium-238 2230 2110 1260-2890 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Vegetation pCi/kg Plutonium-239 3810 3740 2300-5150 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Vegetation pCi/kg Potassium-40 30800 31900 23000-44800 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Vegetation pCi/kg Strontium-90 2330 2580 1470-3420 Acceptable

Enclosure to 0CAN051502 Page 57 of 108 Report PT Quarter / Sample Sample Acceptance Received Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio Date ERA 2nd/2014 05/16/14 MRAD-20 Vegetation pCi/kg Uranium-234 1920 1760 1160-2260 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Vegetation pCi/kg Uranium-238 1970 1750 1170-2220 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Vegetation pCi/kg Uranium-Total 4025 3580 2430-4460 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Vegetation ug/kg Uranium-Total (mass) 5920 5240 3510-6650 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Vegetation pCi/kg Zinc-65 1030 919 663-1290 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Vegetation pCi/kg Uranium-234 1730 1760 1160-2260 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Vegetation pCi/kg Uranium-238 2000 1750 1170-2220 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Vegetation pCi/kg Uranium-Total 3817 3580 2430-4460 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Vegetation ug/kg Uranium-Total (mass) 5990 5240 3510-6650 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Vegetation ug/kg Uranium-Total (mass) 5620 5240 3510-6650 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter pCi/Filter Americium-241 60.2 59.7 36.8-80.8 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter pCi/Filter Cesium-134 920 1010 643-1250 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter pCi/Filter Cesium-137 816 828 622-1090 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter pCi/Filter Cobalt-60 1130 1120 867-1400 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter pCi/Filter Iron-55 254 240 74.4-469 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter pCi/Filter Manganese-54 <6.64 <50.0 0-50.0 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter pCi/Filter Plutonium-238 51.3 56.3 38.6-74.0 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter pCi/Filter Plutonium-239 47.5 48.6 35.2-63.5 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter pCi/Filter Strontium-90 76.7 78.9 38.6-118 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter pCi/Filter Uranium-234 33.8 36.4 22.6-54 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter pCi/Filter Uranium-238 34.5 36.1 23.3-49.9 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter pCi/Filter Uranium-Total 70.3 74.3 41.1-113 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter ug/Filter Uranium-Total (mass) 104 108 69.1-152 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter pCi/Filter Zinc-65 737 667 478-921 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter pCi/Filter Uranium-234 35.5 36.4 22.6-54 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter pCi/Filter Uranium-238 35.3 36.1 23.3-49.9 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter pCi/Filter Uranium-Total 72.4 74.3 41.1-113 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter ug/Filter Uranium-Total (mass) 105 108 69.1-152 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter ug/Filter Uranium-Total (mass) 100 108 69.1-152 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Filter pCi/Filter Gross Alpha 60.9 46 15.4-71.4 Acceptable

Enclosure to 0CAN051502 Page 58 of 108 Report PT Quarter / Sample Sample Acceptance Received Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio Date ERA 2nd/2014 05/16/14 MRAD-20 Filter pCi/Filter Gross Beta 58.9 53.8 34.0-78.4 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Americium-241 186 114 76.8-153 Not Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Cesium-134 1540 1660 1220-1910 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Cesium-137 2760 2690 2280-3220 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Cobalt-60 1320 1270 1100-1490 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Iron-55 1230 1200 716-1630 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Manganese-54 <7.54 <100 0.00-100 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Plutonium-238 37 44 32.6-54.9 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Plutonium-239 124 160 124-202 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Strontium-90 95 890 580-1180 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Uranium-234 77.8 82.4 61.9-106 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Uranium-238 50.8 48.4 36.9-59.4 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Uranium-Total 156 168 123-217 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water ug/L Uranium-Total (mass) 233 245 195-296 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Zinc-65 2030 1800 1500-2270 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Uranium-234 82.1 82.4 61.9-106 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Uranium-238 84.6 48.4 36.9-59.4 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Uranium-Total 170 168 123-217 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water ug/L Uranium-Total (mass) 253 245 195-296 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Uranium-234 80.5 82.4 61.9-106 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Uranium-238 90.0 48.4 36.9-59.4 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Uranium-Total 175 168 123-217 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water ug/L Uranium-Total (mass) 269 245 195-296 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Uranium-234 77.8 82.4 61.9-106 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Uranium-238 78.3 48.4 36.9-59.4 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Uranium-Total 156 168 123-217 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water ug/L Uranium-Total (mass) 233 245 195-296 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water ug/L Uranium-Total (mass) 232 245 195-296 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Gross Alpha 141.0 133 47.2-206 Acceptable ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Gross Beta 172 174.0 99.6-258 Acceptable

Enclosure to 0CAN051502 Page 59 of 108 Report PT Quarter / Sample Sample Acceptance Received Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio Date ERA 2nd/2014 05/16/14 MRAD-20 Water pCi/L Tritium 5280 5580 3740-7960 Acceptable EZA 2nd/2014 08/08/14 E10897 Cartridge pCi Iodine-131 8.73E+01 8.54E+01 1.02 Acceptable EZA 2nd/2014 08/08/14 E10898 Milk pCi/L Strontium-89 9.84E+01 9.13E+01 1.08 Acceptable EZA 2nd/2014 08/08/14 E10898 Milk pCi/L Strontium-90 1.44E+01 1.45E+01 0.99 Acceptable EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Iodine-131 9.89E+01 9.09E+01 1.09 Acceptable EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Cerium-141 1.38E+02 1.24E+02 1.12 Acceptable EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Chromium-51 2.68E+02 2.53E+02 1.06 Acceptable EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Cesium-134 1.58E+02 1.62E+02 0.97 Acceptable EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Cesium-137 1.27E+02 1.20E+02 1.06 Acceptable EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Cobalt-58 1.20E+02 1.12E+02 1.07 Acceptable EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Manganese-54 1.67E+02 1.56E+02 1.07 Acceptable EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Iron-59 1.02E+02 1.02E+02 1.00 Acceptable EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Zinc-65 2.68E+02 2.52E+02 1.06 Acceptable EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Cobalt-60 2.42E+02 2.24E+02 1.08 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Iodine-131 1.13E+02 9.83E+01 1.15 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Cerium-141 1.52E+02 1.43E+02 1.06 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Chromium-51 3.62E+02 2.94E+02 1.23 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Cesium-134 1.69E+02 1.88E+02 0.90 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Cesium-137 1.48E+02 1.39E+02 1.06 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Cobalt-58 1.34E+02 1.30E+02 1.03 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Manganese-54 1.88E+02 1.80E+02 1.04 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Iron-59 1.29E+02 1.19E+02 1.09 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Zinc-65 3.29E+02 2.93E+02 1.12 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Cobalt-60 2.74E+02 2.60E+02 1.05 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Barium-133 67.8 68.7 57.3-75.6 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Cesium-134 71 72.3 59.0-79.5 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Cesium-137 161 163 147-181 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Cobalt-60 76.7 75.5 68.0-85.5 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Zinc-65 92 82 73.8-98.5 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Gross Alpha 45.3 45.4 23.6-57.4 Acceptable

Enclosure to 0CAN051502 Page 60 of 108 Report PT Quarter / Sample Sample Acceptance Received Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio Date ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Gross Beta 32.3 33.4 21.7-41.1 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Gross Alpha 48.6 45.4 23.6-57.4 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Radium-226 8.26 9.06 6.80-10.6 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Radium-226 8.54 9.06 6.80-10.6 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Radium-226 9.7 9.06 6.80-10.6 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Radium-228 5.07 5.07 3.03-6.79 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Radium-228 5.74 5.07 3.03-6.79 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Uranium (Nat) 13.9 13.5 10.7-15.4 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water ug/L Uranium (Nat) mass 22.25 19.8 15.6-22.6 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Uranium (Nat) 13 13.5 10.7-15.4 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water ug/L Uranium (Nat) mass 20.7 19.8 15.6-22.6 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Tritium 10200 11200 9750-12300 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Tritium 10400 11200 9750-12300 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Strontium-89 56.3 42.7 32.9-49.8 Not Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Strontium-90 28.2 31.7 23.1-36.7 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Strontium-89 56.5 42.7 32.9-49.8 Not Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Strontium-90 26 31.7 23.1-36.7 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Iodine-131 28.6 26.1 21.7-30.8 Acceptable ERA 3rd / 2013 08/25/14 RAD - 98 Water pCi/L Iodine-131 22.3 26.1 21.7-30.8 Acceptable EZA 3rd/2014 11/22/14 E10993 Cartridge pCi Iodine-131 9.47E+01 8.99E+01 1.05 Acceptable EZA 3rd/2014 11/22/14 E10994 Milk pCi/L Strontium-89 9.73E+01 9.69E+01 1.00 Acceptable EZA 3rd/2014 11/22/14 E10994 Milk pCi/L Strontium-90 1.31E+01 1.64E+00 0.80 Acceptable EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Iodine-131 1.04E+02 9.76E+01 1.07 Acceptable EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Cerium-141 1.28E+02 1.26E+02 1.01 Acceptable EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Chromium-51 3.12E+02 2.88E+02 1.08 Acceptable EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Cesium-134 1.51E+02 1.58E+02 0.96 Acceptable EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Cesium-137 2.03E+02 1.93E+02 1.05 Acceptable EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Cobalt-58 1.44E+02 1.43E+02 1.01 Acceptable EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Manganese-54 1.49E+02 1.42E+02 1.05 Acceptable EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Iron-59 1.82E+02 1.58E+02 1.15 Acceptable

Enclosure to 0CAN051502 Page 61 of 108 Report PT Quarter / Sample Sample Acceptance Received Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio Date EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Zinc-65 7.41E+01 7.30E+01 1.01 Acceptable EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Cobalt-60 3.14E+02 2.94E+02 1.06 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Iodine-131 1.02E+02 9.88E+01 103 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Cerium-141 1.30E+02 1.25E+02 104 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Chromium-51 2.75E+02 2.86E+02 0.96 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Cesium-134 1.45E+02 1.56E+02 0.93 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Cesium-137 1.94E+02 1.92E+02 1.01 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Cobalt-58 1.43E+02 1.42E+02 1.01 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Manganese-54 1.46E+02 1.41E+02 1.04 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Iron-59 1.66E+02 1.57E+02 1.06 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Zinc-65 7.55E+01 7.24E+01 1.04 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Cobalt-60 3.09E+02 2.95E+02 1.05 Acceptable MAPEP Bq/

MAPEP 4th /2014 01/09/15 Filter Gross Alpha 0.433 0.530 0.16-0.09 Acceptable GrF31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Filter Gross Beta 1.060 1.060 0.53-1.59 Acceptable GrF31 sample MAPEP MAPEP 4th /2014 01/09/15 Soil Bq/Kg Americium-241 88.4 85.5 59.9-111.2 Acceptable MaS31 MAPEP MAPEP 4th /2014 01/09/15 Soil Bq/Kg Cesium-134 588 622 435-809 Acceptable MaS31 MAPEP MAPEP 4th /2014 01/09/15 Soil Bq/Kg Cesium-137 1.67 False Pos Test Acceptable MaS31 MAPEP MAPEP 4th /2014 01/09/15 Soil Bq/Kg Cobalt-57 1160 1116 781-1451 Acceptable MaS31 MAPEP MAPEP 4th /2014 01/09/15 Soil Bq/Kg Cobalt-60 821 779 545-1013 Acceptable MaS31 MAPEP MAPEP 4th /2014 01/09/15 Soil Bq/Kg Iron-55 796 680 476-884 Acceptable MaS31 MAPEP MAPEP 4th /2014 01/09/15 Soil Bq/Kg Manganese-54 1060 1009 706-1312 Acceptable MaS31 MAPEP MAPEP 4th /2014 01/09/15 Soil Bq/Kg Nickel-63 924 980 686-1274 Acceptable MaS31 MAPEP MAPEP 4th /2014 01/09/15 Soil Bq/Kg Plutonium-238 0.92 0.48 Sens. Eval. Acceptable MaS31

Enclosure to 0CAN051502 Page 62 of 108 Report PT Quarter / Sample Sample Acceptance Received Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio Date MAPEP MAPEP 4th /2014 01/09/15 Soil Bq/Kg Plutonium-239/240 61.5 58.6 41.0-76.2 Acceptable MaS31 MAPEP MAPEP 4th /2014 01/09/15 Soil Bq/Kg Potassium-40 879 824 577-1071 Acceptable MaS31 MAPEP MAPEP 4th /2014 01/09/15 Soil Bq/Kg Strontium-90 891 858 601-1115 Acceptable MaS31 MAPEP MAPEP 4th /2014 01/09/15 Soil Bq/Kg Technetium-99 466 589 412-766 Acceptable MaS31 MAPEP MAPEP 4th /2014 01/09/15 Soil Bq/Kg U-234/233 905 89 62-116 Acceptable MaS31 MAPEP MAPEP 4th /2014 01/09/15 Soil Bq/Kg Uranium-238 257 259 181-337 Acceptable MaS31 MAPEP MAPEP 4th /2014 01/09/15 Soil Bq/Kg Zinc-65 605.0 541 379-703 Acceptable MaS31 MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Americium-241 0.915 0.880 0.62-1.14 Acceptable MaW31 MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Cesium-134 -0.06 False Pos Test Acceptable MaW31 MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Cesium-137 18.4 18.4 12.9-23.9 Acceptable MaW31 MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Cobalt-57 25 24.7 17.3-32.1 Acceptable MaW31 MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Cobalt-60 12.5 12.4 8.7-16.1 Acceptable MaW31 MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Hydrogen-3 216 208 146-270 Acceptable MaW31 MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Iron-55 34.0 31.5 22.1-41.0 Acceptable MaW31 MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Manganese-54 14.2 14.0 9.8-18.2 Acceptable MaW31 MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Nickel-63 23.6 24.6 17.2-32.0 Acceptable MaW31 MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Plutonium-238 0.547 0.618 0.433-0.803 Acceptable MaW31 MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Plutonium-239/240 0.015 0.005 Sens. Eval. Acceptable MaW31

Enclosure to 0CAN051502 Page 63 of 108 Report PT Quarter / Sample Sample Acceptance Received Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio Date MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Potassium-40 174 161 113-209 Acceptable MaW31 MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Strontium-90 0.03 False Pos Test Acceptable MaW31 MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Technetium-99 6.92 6.99 4.89-9.09 Acceptable MaW31 MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Uranium-234/233 0.206 0.205 0.144-0.267 Acceptable MaW31 MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Uranium-238 1.280 1.420 0.99-1.85 Acceptable MaW31 MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Zinc-65 11.900 10.90 7.6-14.2 Acceptable MaW31 MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Gross Alpha 0.793 0.701 0.201-1.192 Acceptable MaW31 MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Gross Beta 6.220 5.94 2.97-8.91 Acceptable MaW31 MAPEP ug/

MAPEP 4th /2014 01/09/15 Filter Uranium-235 0.040 0.040 0.0278-0.0516 Acceptable RdF31 sample MAPEP ug/

MAPEP 4th /2014 01/09/15 Filter Uranium-238 19.3 20.3 14.2-26.4 Acceptable RdF31 sample MAPEP ug/

MAPEP 4th /2014 01/09/15 Filter Uranium-Total 19.00 20.4 14.3-26.5 Acceptable RdF31 sample MAPEP ug/

MAPEP 4th /2014 01/09/15 Filter Americium-241 0.0561 0.067 0.0472-0.0876 Acceptable RdF31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Filter Cesium-134 0.8640 0.96 0.67-1.25 Acceptable RdF31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Filter Cesium-137 1.190 1.20 0.84-1.56 Acceptable RdF31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Filter Cobalt-57 1.540 1.43 1.00-1.86 Acceptable RdF31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Filter Cobalt-60 1.200 1.10 0.77-1.43 Acceptable RdF31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Filter Manganese-54 0.808 0.75 0.53-0.98 Acceptable RdF31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Filter Plutonium-238 0.155 0.107 0.075-0.139 Acceptable RdF31 sample

Enclosure to 0CAN051502 Page 64 of 108 Report PT Quarter / Sample Sample Acceptance Received Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio Date MAPEP Bq/

MAPEP 4th /2014 01/09/15 Filter Plutonium-239/240 0.048 0.0468 0.0328-0.0608 Acceptable RdF31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Filter Strontium-90 0.762 0.70 0.492-0.914 Acceptable RdF31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Filter Uranium-234/233 0.037 0.0358 0.0251-0.0465 Acceptable RdF31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Filter Uranium-238 0.227 0.253 0.177-0.329 Acceptable RdF31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Filter Zinc-65 0.779 0.76 0.53-0.99 Acceptable RdF31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Vegetation Americium-241 0.226 0.19 0.135-0.251 Acceptable RdV31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Vegetation Cesium-134 4.750 5.20 3.64-6.67 Acceptable RdV31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Vegetation Cesium-137 6.910 6.60 4.62-8.58 Acceptable RdV31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Vegetation Cobalt-57 -0.002 0.00 False Pos Test Acceptable RdV31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Vegetation Cobalt-60 0.008 0.00 False Pos Test Acceptable RdV31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Vegetation Manganese-54 7.980 7.88 5.52-10.24 Acceptable RdV31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Vegetation Plutonium-238 0.001 0.001 Sens. Eval. Acceptable RdV31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Vegetation Plutonium-239/240 0.1510 0.171 0.120-0.222 Acceptable RdV31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Vegetation Strontium-90 2.330 2.32 1.62-3.02 Acceptable RdV31 sample MAPEP Bq MAPEP 4th /2014 01/09/15 Vegetation Uranium-234/233 0.046 0.047 0.0326-0.0606 Acceptable RdV31 /sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Vegetation Uranium-238 0.332 0.324 0.227-0.421 Acceptable RdV31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Vegetation Zinc-65 2.850 2.63 1.84-3.42 Acceptable RdV31 sample MAPEP Bq/

MAPEP 4th /2014 01/09/15 Filter Strontium-89 3.62 3.79 2.65-4.93 Acceptable SrF-31 sample

Enclosure to 0CAN051502 Page 65 of 108 Report PT Quarter / Sample Sample Acceptance Received Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio Date MAPEP Bq/

MAPEP 4th /2014 01/09/15 Filter Strontium-90 3.62 3.79 2.65-4.93 Acceptable SrF-31 sample MAPEP MAPEP 4th /2014 01/09/15 Water Bq/L Iodine-129 4.56 4.55 3.19-5.92 Acceptable XaW-31 ERA 3rd / 2014 11/25/14 MRAD-21 Soil pCi/kg Actinium-228 1280 1240 795-1720 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Soil pCi/kg Americium-241 825 763 431-956 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Soil pCi/kg Bismuth-212 1620 1240 330-1820 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Soil pCi/kg Bismuth-214 2900 2810 1690-4040 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Soil pCi/kg Cesium-134 1960 2140 1400-2570 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Soil pCi/kg Cesium-137 6760 6550 5020-8430 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Soil pCi/kg Cobalt-60 4480 4260 2880-5860 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Soil pCi/kg Lead-212 1260 1240 812-1730 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Soil pCi/kg Lead-214 3480 2750 1610-4100 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Soil pCi/kg Manganese-54 <30.0 <1000 0-1000 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Soil pCi/kg Plutonium-238 732 739 444-1020 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Soil pCi/kg Plutonium-239 281 309 202-427 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Soil pCi/kg Potassium-40 11500 10700 7810-14400 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Soil pCi/kg Strontium-90 8790 8420 3210-13300 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Soil pCi/kg Thorium-234 2000 2350 743-4420 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Soil pCi/kg Zinc-65 3910 3270 2600-4350 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Soil pCi/kg Uranium-234 2280 2370 1450-3040 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Soil pCi/kg Uranium-238 2340 2350 1450-2980 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Soil pCi/kg Uranium-Total 4762 4540 2360-6390 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Soil ug/kg Uranium-Total(mass) 7020 7050 3890-8870 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation pCi/kg Americium-241 2260 2290 1400-3505 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation pCi/kg Cesium-134 837 849 545-1100 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation pCi/kg Cesium-137 729 644 467-896 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation pCi/kg Cobalt-60 818 784 541-1100 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation pCi/kg Curium-244 361 367 180-572 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation pCi/kg Manganese-54 <25.3 <300 0-300 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation pCi/kg Plutonium-238 886 862 514-1180 Acceptable

Enclosure to 0CAN051502 Page 66 of 108 Report PT Quarter / Sample Sample Acceptance Received Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio Date ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation pCi/kg Plutonium-239 675 701 430-965 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation pCi/kg Potassium-40 35300 30900 22300-43400 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation pCi/kg Strontium-90 1230 1710 975-2270 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation pCi/kg Uranium-234 1980 1780 1170-2290 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation pCi/kg Uranium-238 1970 1760 1170-2240 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation pCi/kg Uranium-Total 4038 3620 2450-4510 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation ug/kg Uranium-Total(mass) 5910 5280 3540-6710 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation pCi/kg Uranium-234 1670 1780 1170-2290 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation pCi/kg Uranium-238 1800 1760 1170-2240 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation pCi/kg Uranium-Total 3556 3620 2450-4510 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation ug/kg Uranium-Total(mass) 5390 5280 3540-6710 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation ug/kg Uranium-Total(mass) 5860 5280 3540-6710 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Vegetation pCi/kg Zinc-65 1930 1570 1130-2200 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter pCi/Filter Americium-241 41.4 38.6 23.8-52.2 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter pCi/Filter Cesium-134 742 765.0 487-949 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter pCi/Filter Cesium-137 677 647 486-850 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter pCi/Filter Cobalt-60 543 523 405-653 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter pCi/Filter Iron-55 117 120.0 37.2-234 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter pCi/Filter Manganese-54 <5.87 <50 0.00-50.0 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter ug/Filter Plutonium-238 32.9 35.7 24.5-46.9 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter pCi/Filter Plutonium-239 26.8 29.1 21.1-38.0 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter pCi/Filter Strontium-90 187 168 82.1-252 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter pCi/Filter Uranium-234 26 28 27.8-41.9 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter pCi/Filter Uranium-238 28 27.60 17.8-38.2 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter pCi/Filter Uranium-Total 56 57 31.4-86.3 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter ug/Filter Uranium-Total (mass) 82.6 82.7 52.9-116 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter pCi/Filter Zinc-65 629 547 392-755 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter pCi/Filter Uranium-234 28 28 27.8-41.9 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter pCi/Filter Uranium-238 25 27.60 17.8-38.2 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter pCi/Filter Uranium-Total 55 57 31.4-86.3 Acceptable

Enclosure to 0CAN051502 Page 67 of 108 Report PT Quarter / Sample Sample Acceptance Received Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio Date ERA 3rd / 2014 11/25/14 MRAD-21 Filter ug/Filter Uranium-Total (mass) 75.1 82.7 52.9-116 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter ug/Filter Uranium-Total (mass) 90.7 82.7 52.9-116 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter pCi/Filter Gross Alpha 47.4 36.9 12.4-57.3 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Filter pCi/Filter Gross Beta 27.2 21.1 13.3-30.8 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Americium-241 72.4 68.6 46.2-92.0 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Cesium-134 816.0 850 624-977 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Cesium-137 1310 1240 1060-1490 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Cobalt-60 1130 1070 930-1250 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Iron-55 130 134 79.9-182 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Manganese-54 <6.34 <100 0.00-100 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Plutonium-238 35 33 24.6-41.4 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Plutonium-239 46.4 51 39.7-64.4 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Strontium-90 300 254 165-336 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Uranium-234 42 44 32.9-56.5 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Uranium-238 50 43.50 33.2-53.4 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Uranium-Total 92 89 65.5-115 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water ug/L Uranium-Total (mass) 137 130 104-157 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Zinc-65 1070 921 768-1160 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Uranium-234 43 44 32.9-56.5 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Uranium-238 45 43.50 33.2-53.4 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Uranium-Total 90 89 65.5-115 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water ug/L Uranium-Total (mass) 134 130 104-157 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Uranium-234 49 44 32.9-56.5 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Uranium-238 42 43.50 33.2-53.4 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Uranium-Total 93 89 65.5-115 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water ug/L Uranium-Total (mass) 126 130 104-157 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water ug/L Uranium-Total (mass) 144 130 104-157 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Gross Alpha 96.2 98 34.8-152 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Gross Beta 86.1 77.5 44.4-115 Acceptable ERA 3rd / 2014 11/25/14 MRAD-21 Water pCi/L Tritium 5490 5500 3680-7840 Acceptable

Enclosure to 0CAN051502 Page 68 of 108 TABLE 2 2014 ECKERT & ZIEGLER ANALYTICS PERFORMANCE EVALUATION RESULTS PT Quarter / Sample Sample Acceptance Report Date Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio EZA 1st/2014 05/16/14 E10846 Cartridge pCi Iodine-131 7.83E+01 7.52E+01 1.04 Acceptable EZA 1st/2014 05/16/14 E10847 Milk pCi/L Strontium-89 9.14E+01 9.17E+01 1 Acceptable EZA 1st/2014 05/16/14 E10847 Milk pCi/L Strontium-90 1.27E+01 1.51E+01 0.84 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Iodine-131 9.84E+01 9.85E+01 1 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Cerium-141 1.21E+02 1.19E+02 1.02 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Cr-51 5.19E+02 4.91E+02 1.06 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Cesium-134 1.79E+02 2.10E+02 0.85 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Cesium-137 2.55E+02 2.53E+02 1.01 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Cobalt-58 2.58E+02 2.68E+02 0.96 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Mn-54 3.01E+02 2.97E+02 1.01 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Iron-59 2.24E+02 2.19E+02 1.02 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Zinc-65 3.45E+02 3.23E+02 1.07 Acceptable EZA 1st/2014 05/16/14 E10848 Milk pCi/L Cobalt-60 3.39E+02 3.37E+02 1.00 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Iodine-131 9.24E+01 8.99E+01 1.03 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Cerium-141 8.19E+01 7.71E+01 1.06 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Cr-51 3.32E+02 3.19E+02 1.04 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Cesium-134 1.27E+02 1.36E+02 0.93 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Cesium-137 1.69E+02 1.64E+02 1.03 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Cobalt-58 1.75E+02 1.74E+02 1.01 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Mn-54 2.08E+02 1.93E+02 1.08 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Iron-59 1.68E+02 1.42E+02 1.18 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Zinc-65 2.25E+02 2.10E+02 1.07 Acceptable EZA 1st/2014 05/16/14 E10849 Water pCi/L Cobalt-60 2.31E+02 2.19E+02 1.02 Acceptable EZA 2nd/2014 08/08/14 E10897 Cartridge pCi Iodine-131 8.73E+01 8.54E+01 1.02 Acceptable EZA 2nd/2014 08/08/14 E10898 Milk pCi/L Strontium-89 9.84E+01 9.13E+01 1.08 Acceptable EZA 2nd/2014 08/08/14 E10898 Milk pCi/L Strontium-90 1.44E+01 1.45E+01 0.99 Acceptable EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Iodine-131 9.89E+01 9.09E+01 1.09 Acceptable

Enclosure to 0CAN051502 Page 69 of 108 PT Quarter / Sample Sample Acceptance Report Date Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Cerium-141 1.38E+02 1.24E+02 1.12 Acceptable EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Chromium-51 2.68E+02 2.53E+02 1.06 Acceptable EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Cesium-134 1.58E+02 1.62E+02 0.97 Acceptable EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Cesium-137 1.27E+02 1.20E+02 1.06 Acceptable EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Cobalt-58 1.20E+02 1.12E+02 1.07 Acceptable EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Manganese-54 1.67E+02 1.56E+02 1.07 Acceptable EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Iron-59 1.02E+02 1.02E+02 1.00 Acceptable EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Zinc-65 2.68E+02 2.52E+02 1.06 Acceptable EZA 2nd/2014 08/08/14 E10899 Milk pCi/L Cobalt-60 2.42E+02 2.24E+02 1.08 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Iodine-131 1.13E+02 9.83E+01 1.15 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Cerium-141 1.52E+02 1.43E+02 1.06 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Chromium-51 3.62E+02 2.94E+02 1.23 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Cesium-134 1.69E+02 1.88E+02 0.90 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Cesium-137 1.48E+02 1.39E+02 1.06 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Cobalt-58 1.34E+02 1.30E+02 1.03 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Manganese-54 1.88E+02 1.80E+02 1.04 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Iron-59 1.29E+02 1.19E+02 1.09 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Zinc-65 3.29E+02 2.93E+02 1.12 Acceptable EZA 2nd/2014 08/08/14 E10900 Water pCi/L Cobalt-60 2.74E+02 2.60E+02 1.05 Acceptable EZA 3rd/2014 11/22/14 E10993 Cartridge pCi Iodine-131 9.47E+01 8.99E+01 1.05 Acceptable EZA 3rd/2014 11/22/14 E10994 Milk pCi/L Strontium-89 9.73E+01 9.69E+01 1.00 Acceptable EZA 3rd/2014 11/22/14 E10994 Milk pCi/L Strontium-90 1.31E+01 1.64E+01 0.80 Acceptable EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Iodine-131 1.04E+02 9.76E+01 1.07 Acceptable EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Cerium-141 1.28E+02 1.26E+02 1.01 Acceptable EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Chromium-51 3.12E+02 2.88E+02 1.08 Acceptable EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Cesium-134 1.51E+02 1.58E+02 0.96 Acceptable EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Cesium-137 2.03E+02 1.93E+02 1.05 Acceptable EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Cobalt-58 1.44E+02 1.43E+02 1.01 Acceptable EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Manganese-54 1.49E+02 1.42E+02 1.05 Acceptable EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Iron-59 1.82E+02 1.58E+02 1.15 Acceptable EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Zinc-65 7.41E+01 7.30E+01 1.01 Acceptable

Enclosure to 0CAN051502 Page 70 of 108 PT Quarter / Sample Sample Acceptance Report Date Unit Analyte / Nuclide GEL Value Known value Evaluation Provider Year Number Media Range / Ratio EZA 3rd/2014 11/22/14 E10995 Milk pCi/L Cobalt-60 3.14E+02 2.94E+02 1.06 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Iodine-131 1.02E+02 9.88E+01 103 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Cerium-141 1.30E+02 1.25E+02 104 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Chromium-51 2.75E+02 2.86E+02 0.96 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Cesium-134 1.45E+02 1.56E+02 0.93 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Cesium-137 1.94E+02 1.92E+02 1.01 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Cobalt-58 1.43E+02 1.42E+02 1.01 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Manganese-54 1.46E+02 1.41E+02 1.04 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Iron-59 1.66E+02 1.57E+02 1.06 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Zinc-65 7.55E+01 7.24E+01 1.04 Acceptable EZA 3rd/2014 11/22/14 E10996 Water pCi/L Cobalt-60 3.09E+02 2.95E+02 1.05 Acceptable

Enclosure to 0CAN051502 Page 71 of 108 TABLE 3 2014 DEPARTMENT OF ENERGY MIXED ANALYTE PERFORMANCE EVALUATION PROGRAM (MAPEP) RESULTS PT Quarter / Report Sample Sample Known Acceptance Unit Analyte / Nuclide GEL Value Evaluation Provider Year Date Number Media value Range / Ratio MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Filter Gross Alpha 1.980 1.77 0.53-3.01 Acceptable GrF30 sample MAPEP Bq/

MAPEP 2nd/2014 06/05/14 Filter Gross Beta 0.823 0.77 0.39-1.16 Acceptable GrF30 sample MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Americium-241 65 68 47.6-88.4 Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Cesium-134 5.44 0 False Pos Test Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Cesium-137 1270 1238 867-1609 Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Cobalt-57 947 966 676-1256 Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Cobalt-60 0.581 1.220 Sens. Eval. Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Iron-55 580 643 444-824 Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Manganese-54 1470 1430 1001-1859 Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Nickel-63 6.95 0 False Pos Test Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Plutonium-238 89.7 96.0 67-125 Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Plutonium-239/240 69.80 76.8 53.8-99.8 Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Potassium-40 703 622 435-809 Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Strontium-90 1.48 0 False Pos Test Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Technetium-99 37.1 0 False Pos Test Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg U-234/233 30.5 81.0 57-105 Not Accept.

MaS30

Enclosure to 0CAN051502 Page 72 of 108 PT Quarter / Report Sample Sample Known Acceptance Unit Analyte / Nuclide GEL Value Evaluation Provider Year Date Number Media value Range / Ratio MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Uranium-238 35 83 58-108 Not Accept.

MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Soil Bq/kg Zinc-65 766 695 487-904 Acceptable MaS30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Am-241 0.759 0.720 0.504-0.936 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Cesium-134 21.4 23.1 16.2-30.0 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Cesium-137 29.70 28.9 20.2-37.6 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Cobalt-57 28.0 27.5 19.3-35.8 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Cobalt-60 16.6 16.0 11.2-20.8 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Hydrogen-3 308 321 225-417 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Iron-55 0.3 0.0 False Pos Test Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Manganese-54 14.4 13.9 9.7-18.1 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Nickel-63 31.4 34.0 23.8-44.2 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Plutonium-238 0.764 0.828 0.580-1.076 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Pu-239/240 0.6590 0.6760 0.473-0.879 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Potassium-40 0.460 0 False Pos Test Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Strontium-90 8.32 8.51 5.96-11.06 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Technetium-99 9.5 10.3 7.2-13.4 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L U-234/233 0.210 0.225 0.158-0.293 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Uranium-238 1.41 1.45 1.02-1.89 Acceptable MaW30

Enclosure to 0CAN051502 Page 73 of 108 PT Quarter / Report Sample Sample Known Acceptance Unit Analyte / Nuclide GEL Value Evaluation Provider Year Date Number Media value Range / Ratio MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Zinc-65 -0.126 0.0 False Pos Test Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Gross Alpha 0.96 0.85 0.255-1.443 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Gross Beta 4.7 4.2 2.10-6.29 Acceptable MaW30 MAPEP MAPEP 2nd/2014 06/05/14 Water Bq/L Iodine-129 0.0227 0.00 False Pos Test Acceptable MaW30 MAPEP ug/

MAPEP 2nd/2014 06/05/14 Filter Uranium-235 0.018 0.020 0.014-0.026 Acceptable RdF30 sample MAPEP ug/

MAPEP 2nd/2014 06/05/14 Filter Uranium-238 8.77 10.4 7.3-13.5 Acceptable RdF30 sample MAPEP ug/

MAPEP 2nd/2014 06/05/14 Filter Uranium-Total 8.80 10.4 7.3-13.5 Acceptable RdF30 sample MAPEP ug/