ML030990673
| ML030990673 | |
| Person / Time | |
|---|---|
| Site: | Fort Calhoun  |
| Issue date: | 12/31/2002 |
| From: | Omaha Public Power District |
| To: | Office of Nuclear Reactor Regulation |
| References | |
| Download: ML030990673 (121) | |
Text
9-SUPPLEMENT TO OMAHA PUBLIC POWER DISTRICT FORT CALHOUN STATION 2001 ANNUAL RADIOLOGICAL EFFLUENT RELEASE REPORT FOR TECHNICAL SPECIFICATION SECTIONS 5.9.1.b AND 5.9.4.a The supplement reflects the following corrections:
- 1.
A recalculation of the following tables due to wind direction averaging error:
- a. Tables IV-A-1 through IV-A Receptor Dose Projections
- b. Table IV-B Dose Contributions at Unrestricted Area Boundary
- c. Table IV-C ALARA Annual Integrated Dose Summary
- 2.
Typographical corrections to the following sections:
- a. Section 1, Introduction, pages 1-2 and 1-8
- b.Section V, Solid Waste, page V-3
- 3.
Inclusion of a copy of revisions made in 2001 to the Process Control Program, which consists of:
- a. The Fort Calhoun Station Process Control Program, RW-200 (Section VII, Attachment 1)
- b. Joint Frequency Distribution Wind Direction vs. Wind Speed (Section VII, Attachment 2, pages VI1-4 through VI1-17)
The Fort Calhoun Station meteorological system achieved a cumulative availability rate of 99.01 % for the joint frequency parameters required by Regulatory Guide 1.23 of wind speed, wind direction and delta temperature.
There were no abnormal releases during 2001.
During 2001 there were no changes to the ODCM and one change to the PCP.
For 2001, the total volume of buried solid radwaste was 21.80 cubic meters, essentially unchanged from the 16.76 cubic meters of solid waste buried in 2000. The majority was due to shipments of dry compressible materials. The total buried activity for 2001 was 729.36 Curies, 728 of which came from spent resin. This value is considerably higher than the 2000 value of 54.04 Curies primarily due to fuel rod failure and the release of fission products.
Overall, the radioactive effluent monitoring program was conducted in a manner to ensure the activity released and associated dose to the public were maintained as low as reasonably achievable.
2.0 SUPPLEMENTAL INFORMATION 2.1 Regulatory Limits The ODCM Radiological Effluent Control Specifications applicable to the release of radioactive material in liquid and gaseous effluents are described in the following sections.
2.1.1 Fission and Activation Gases (Noble Gases)
The release rate of radioactive material in airborne effluents shall be controlled such that the instantaneous concentrations of radionuclides do not exceed the values specified in 10 CFR 20 for airborne effluents at the unrestricted area boundary. To support plant operations, Supervisor - System Chemistry may increase this limit up to the limits specified in Technical Specification 5.16.1.g.
1-2
5.0 SOLID WASTES The quantities of radioactive material released as solid effluents are summarized in Section VI.
6.0 RELATED INFORMATION 6.1 Operability of Liquid and Gaseous Monitorinc Instrumentation During the reporting period the Condenser Off-Gas Radiation Monitor, RM-057, was out of service from April 28, 2001 at 0821 to June 14, 2001 at 1131. During troubleshooting it was discovered that approximately 6 inches of the detector was missing due to corrosion. EC-26574 was issued for a minor modification to replace the carbon steel detector with a stainless steel unit. The monitor was removed from service for an extended period of time due to problems acquiring the replacement detector from the vendor. The parts arrived on site and the monitor was calibrated and returned to service. During the period the monitor was out of service, condenser off-gas flow was routed through the auxiliary building exhaust stack for monitoring. Routine sampling was performed in accordance with ODCM Table 2.2.1.
6.2 Changes to the Offsite Dose Calculation Manual (ODCM) or Process Control Program (PCP)
During 2001 there were no changes made to the ODCM and one change to the PCP.
6.3 New Locations or Modifications for Dose Calculations or Environmental Monitoring No new receptor locations were identified which resulted in changes to our environmental monitoring sample locations.
6.4 Noncomoliance with Radiological Effluent Control Requirements This section provides a list of any event that did not comply with the applicable requirements of the Radiological Effluent Controls given in the Offsite Dose Calculation Manual (ODCM). Detailed documentation concerning the evaluations and corrective actions is maintained onsite.
1-8
A.
Potential Annual Doses to Individuals from Liquid Releases Total body, skin, and organ mRem for liquid releases were calculated for all significant liquid pathways using the annual configuration of the LADTAP II program.
The inputs to LADTAP II for the annual period from January 1, 2001 through December 31, 2001 were as follows:
(1)
All liquid effluents were as described in Section IV except for entrained noble gases (Ar-41, Xe-131M, Xe-1 33M, Xe-1 33, Xe-1 35M, Xe-1 35, Kr-85M, Kr-87, and Kr-88)
(2)
An average plant discharge rate of 712.0 cubic feet per second (CFS) was utilized for 2001. The average discharge rate during releases was 677.2 cubic feet per second (CFS).
(3)
Dilution factors (inverse of the mixing ratios) were computed based on Regulatory Guide 1.113 (equation 7 in Section 2.a.1 of Appendix A) for a one dimensional transport model.
(4)
Drinking water transport times of 6.6 hours6.944444e-5 days <br />0.00167 hours <br />9.920635e-6 weeks <br />2.283e-6 months <br /> to the Omaha intake and 7.0 hours0 days <br />0 hours <br />0 weeks <br />0 months <br /> to the Council Bluffs intake for the ALARA doses were used. A transport time of 0.0 was used from the plant to the discharge site.
(5)
A shorewidth factor of 0.2 was used.
(6)
All dose factors, transport times from receptor to individual, and usage factors are defined by Regulatory Guide 1.109 and NUREG-0172.
The discharge site was chosen to present the most conservative estimate of mRem dose for an average adult, teenager, child, and infant. A conservative approach is also presented by the assumption that Omaha and Council Bluffs receive all drinking water from the Missouri River.
B.
Potential Annual Doses to Population from Liquid Releases The LADTAP II program in its annual configuration was also used to calculate to total body and organ doses for the population of 853,274 (based on the 2000 Census) within a 50-mile radius of the plant. The same input was used as in the individual cases with the addition of the following:
V-3
TABLE IV-A-1 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
1 RES AT 4.57 MILES N ANNUALBETAAIRDOSE = 1.23E-02 MILLRADS ANNUALGAMMAAIRDOSE = 3.34E-03 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
__---+_____
+____
+___
_+___
_+__
__+_---________-+
+
PLUME
- 1.95E-03 : 1.95E-03 : 1.95E-03 : 1.95E-03 : 1.95E-03 : 1.95E-03 : 2.07E-03 : 7.24E-03
__---+_____
+____
+___
_+___
_+__
__+_---________-+
+
GROUND
- 1.02E-06 : 1.02E-06 : 1.02E-06 : 1.02E-06 : 1.02E-06 : 1.02E-06 : 1.02E-06 : 1.21E-06
_________+__________+__________+__________+__________+__________+__________+__________+__________+
INHAL ADULT 3.70E-06 3.43E-06 4.81E-07 3.99E-06 4.48E-06 2.28E-04 3.31E-06 3.31E-06
__---+_____
+____
+___
_+___
_+__
__+_---____
+
TEEN
- 3.84E-06 : 3.46E-06 : 6.77E-07 : 4.28E-06 : 4.94E-06 : 2.80E-04 : 3.34E-06 : 3.34E-06
__---+_____
+____
+___
_+___
_+__
__+_---________-+
_ +
CHILD
- 3.46E-06 : 3.OOE-06 : 9.19E-07 : 3.87E-06 : 4.45E-06 : 3.10E-04 : 2.95E-06 : 2.95E-06
__---+_____
+____
+___
_+___
_+__
__+_---________+-+
_ +
INFANT : 2.07E-06 : 1.72E-06 : 7.24E-07 : 2.54E-06 : 2.68E-06 : 2.82E-04 : 1.70E-06 : 1.69E-06
_____-___+_-___-____+________-_+________-_+________-_+________-_+_________-+________-_+_______-__+
IV-5 V
I TABLE IV-A-2 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
2 RES AT 1.93 MILES NNE ANNUALBETAAIRDOSE = 6.58E-02 MILLRADS ANNUALGAMMAAIRDOSE = 1.78E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
-_+__________+-
+_
+
+
__--+-
+
_+_-
-__+
PLUME
- 1.04E-02 : 1.04E-02 : 1.04E-02 : 1.04E-02 : 1.04E-02 : 1.04E-02 : 1.10E-02 : 3.87E-02
-_+__________+-
+_
+
+_----_______+___--_
+
GROUND
- 5.38E-06 : 5.38E-06 : 5.38E-06 : 5.38E-06 : 5.38E-OG : 5.38E-06 : 5.38E-06 : 6.40E-06
-_+__________+-
+_
+
+
__--+-
_+__--_
+
INHAL ADULT 2.OOE-05 1.85E-05 2.63E-06 2.16E-05 2.42E-05 1.25E-03 1.79E-05 1.79E-05
-_+__________+-
+_
+
+
-_____+__--_
+
TEEN
- 2.08E-05 : 1.87E-05 : 3.70E-06 : 2.32E-05 : 2.68E-05 : 1.53E-03 : 1.80E-05 : 1.80E-05
-_+__________+-
+_
+
+
+
_+__--_
+
CHILD
- 1.87E-05 : 1.62E-05 : 5.02E-06 : 2.09E-05 : 2.41E-05 : 1.70E-03 : 1.59E-05 : 1.59E-05
-_+__________+-
+_
+
+
-_____+__--_
+
INFANT : 1.12E-05 : 9.27E-06 : 3.96E-06 : 1.38E-05 : 1.45E-05 : 1.54E-03 : 9.15E-06 : 9.15E-06
-_+__________+-
+_
+
+
+
_+__--_
+
IV-6
TABLE IV-A-3 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
3 RES AT 1.52 MILES NE ANNUALBETAAIRDOSE = 7.32E-02 MILLRADS ANNUALGAMMAAIRDOSE = 1.98E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
______-___+__________+__________+_________+__________+__________+__________+_---________-+____-__+
PLUME
- 1.15E-02 : 1.15E-02 : 1.15E-02 : 1.15E-02 : 1.15E-02 : 1.15E-02 : 1.23E-02 : 4.31E-02
_________+__________+__________+__________+__________+__________+__________+__________+__________+
GROUND
- 6.OOE-06 : 6.OOE-06 : 6.OOE-06 : 6.OOE-06 : 6.OOE-06 : 6.00E-06 : 6.OOE-06 : 7.14E-06 INHAL ADULT 2.22E-05 2.06E-05 2.93E-06 2.40E-05 2.69E-05 1.39E-03 1.98E-05 1.98E-05
-__+ __________+__________+__________+____--+-
+
-__+__________+___
_----_+
+
TEEN
- 2.31E-05 : 2.08E-05 : 4.11E-06 : 2.57E-05 : 2.97E-05 : 1.70E-03 : 2.OOE-05 : 2.OOE-05
__---+_____
+____
+___
_+___
_+__
__+_---________-+
_ +
CHILD
- 2.08E-05 : 1.80E-05 : 5.58E-06 : 2.33E-05 : 2.68E-05 : 1.88E-03 : 1.77E-05 : 1.77E-05
__---+_____
+____
+___
_+___
_+__
__+_--+-________- +___-_
+
INFANT : 1.24E-05 : 1.03E-05 : 4.40E-06 : 1.53E-05 : 1.62E-05 : 1.72E-03 : 1.02E-05 : 1.02E-05
__---+_____
+____
+___
_+___
_+__
__+_--+-________- +___-_
+
IV-7
TABLE IV-A-4 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
4 RES AT 4.79 MILES ENE ANNUALBETAAIR DOSE = 5.55E-03 MILLRADS ANNUALGAMMAAIRDOSE = 1.49E-03 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
_______-+__________+__________+__________+__________+__________+__________+__--________+-________+
PLUME
- 8.69E-04 : 8.69E-04 : 8.69E-04 : 8.69E-04 : 8.69E-04 : 8.69E-04 : 9.24E-04 : 3.26E-03
_______-+__________+__________+__________+__________+__________+__________+__--________+-________+
GROUND
- 1.94E-07 : 1.94E-07 : 1.94E-07 : 1.94E-07 : 1.94E-07 : 1.94E-07 : 1.94E-07 : 2.30E-07
_________+__________+__________+__________+__________+__________+__________+__________+__________+
INHAL ADULT 1.70E-06 1.58E-06 2.16E-07 1.83E-06 2.05E-06 1.03E-04 1.52E-06 1.52E-06
________+-_________+_________-+__________+__________+__________+__________+___--+-+-+-_-+___-____+
TEEN
- 1.76E-06 : 1.59E-06
- 3.04E-07
- 1.96E-06 : 2.25E-06 : 1.26E-04
- 1.53E-06 : 1.53E-06
_________+______-___+________-_+________-_+________-_+________-_+_______-__+________-_+________-_+
CHILD
- 1.59E-06
- 1.38E-06
- 4.12E-07 : 1.77E-06 : 2.03E-06 : 1.39E-04 : 1.36E-06 : 1.36E-06
_________+______-___+________-_+_______-__+________-_+_______-__+________-_+________-_+________-_+
INFANT : 9.47E-07 : 7.89E-07 : 3.25E-07 : 1.16E-06 : 1.22E-06 : 1.27E-04 : 7.80E-07 : 7.BOE-07
_____-___+-_________+_________-+_________-+________-_+________-_+________-_+________-_+________-_+
IV-8
TABLE IV-A-5 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
5 RES AT 4.67 MILES E ANNUALBETAAIR DOSE = 8.03E-03 MILLRADS ANNUALGAMMAAIR_DOSE = 2.15E-03 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
_____-___+_-________+________-_+________-_+________-_+________-_+________-_+________-_+________-_+
PLUME
- 1.25E-03 : 1.25E-03 : 1.25E-03 : 1.25E-03 : 1.25E-03 : 1.25E-03 : 1.33E-03 : 4.71E-03
______-__+_-________+________-_+________-_+________-_+_______-__+_______-__+________-_+________-_+
GROUND
- 2.46E-07 : 2.46E-07 : 2.46E-07 : 2.46E-07 : 2.46E-07 : 2.46E-07 : 2.46E-07 : 2.93E-07
_________+__________+__________+__________+__________+__________+__________+__________+__________+
INHAL ADULT 2.47E-06 2.30E-06 3.14E-07 2.66E-06 2.98E-06 1.49E-04 2.22E-06 2.22E-06
__---+_____
+____
+___
_+___
_+__
__+_---________-+____-_
+
TEEN
- 2.56E-06 : 2.32E-06 : 4.42E-07 : 2.85E-06 : 3.28E-06 : 1.83E-04 : 2.24E-06 : 2.24E-06
__---+_____
+____
+___
_+___
_+__
__+_---________-+
+
CHILD
- 2.31E-06 : 2.01E-06 : 6.OOE-07 : 2.57E-06 : 2.95E-06 : 2.03E-04 : 1.97E-06 : 1.97E-06
____-____+_-________+________-_+_________-+________-_+________-_+__________+_________-+________-_+
INFANT : 1.38E-06 : 1.15E-06 : 4.72E-07 : 1.69E-06 : 1.78E-06 : 1.85E-04 : 1.14E-06 : 1.14E-06
______-__+_-________+________-_+________-_+_______-__+________-_+_______-__+________-_+________-_+
IV-9
'1
TABLE IV-A-6 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
6 RES AT 4.22 MILES ESE ANNUALBETAAIRDOSE = 1.43E-02 MILLRADS ANNUALGAMMAAIRDOSE = 3.80E-03 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
_______-_+-_________+_________-+__________+__________+__________+__________+____---____+___--____+
PLUME
- 2.21E-03 : 2.21E-03 : 2.21E-03 : 2.21E-03 : 2.21E-03 : 2.21E-03 : 2.35E-03 : 8.36E-03
_________+______-___+________-_+________-_+_________-+________-_+_______-__+________-_+________-_+
GROUND
- 5.93E-07 : 5.93E-07 : 5.93E-07 : 5.93E-07 : 5.93E-07 : 5.93E-07 : 5.93E-07 : 7.06E-07
_________+__________+__________+__________+__________+__________+__________+__________+__________+
INHAL ADULT 4.42E-06 4.11E-06 5.58E-07 4.76E-06 5.32E-06 2.66E-04 3.97E-06 3.97E-06
_________+-_________+_______-__+________-_+_________-+-_________+__________+_________-+________-_+
TEEN
- 4.59E-06 : 4.15E-06 : 7.85E-07 : 5.09E-06 : 5.86E-06 : 3.25E-04 : 4.OOE-06 : 4.OOE-06
_________+______-___+________-_+________-_+________-_+_________-+_______-__+________-_+________-_+
CHILD
- 4.14E-06 : 3.60E-06 : 1.07E-06 : 4.60E-06 : 5.28E-06 : 3.60E-04 : 3.54E-06 : 3.54E-06
_________+-_________+_______-__+________-_+_______-__+________-_+________-_+________-_+________-_+
INFANT : 2.47E-06 : 2.06E-06 : 8.40E-07 : 3.02E-06 : 3.18E-06 : 3.28E-04 : 2.03E-06 : 2.03E-06
_____-___+-_________+________-_+_________-+__________+__________+__________+_________-+________-_+
IV-10
TABLE IV-A-7 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
7 RES AT 1.67 MILES SE ANNUALBETAAIRDOSE = 1.18E-01 MILLRADS ANNUALGAMMAAIRDOSE = 3.19E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
__---+_____
+____
+___
_+___
_+__
__+_---________-+____-_
+
PLUME
- 1.86E-02 : 1.86E-02 : 1.86E-02 : 1.86E-02 : 1.86E-02 : 1.86E-02 : 1.98E-02 : 6.95E-02
__---+_____
+____
+___
_+___
_+__
__+_---________-+____-_
+
GROUND
- 1.07E-05 : 1.07E-05 : 1.07E-05 : 1.07E-05 : 1.07E-05 : 1.07E-05 : 1.07E-05 : 1.28E-05
_________+__________+__________+__________+__________+__________+__________+__________+__________+
INHAL ADULT 3.59E-05 3.33E-05 4.73E-06 3.88E-05 4.35E-05 2.24E-03 3.21E-05 3.21E-05
______-__+__________+__________+__________+____----__+-_________+__________+_______--_+-_________+
TEEN
- 3.73E-05 : 3.36E-05 : 6.65E-06 : 4.16E-05 : 4.81E-05 : 2.75E-03 : 3.24E-05 ; 3.24E-05
__---+_____
+____
+___
_+___
_+__
__+_--+-________-+___-_
+
CHILD
- 3.37E-05 : 2.91E-05 : 9.02E-06 : 3.76E-05 : 4.33E-05 : 3.05E-03 : 2.86E-05 : 2.86E-05
__---+_____
+____
+___
_+___
_+__
__+_---________-+
_ +
INFANT : 2.01E-05 : 1.67E-05 : 7.11E-06 : 2.48E-05 : 2.61E-05 : 2.77E-03 : 1.64E-05 : 1.64E-05
_________+__________+__________+__________+__________+__________+__________+__________+__________+
IV-ll
TABLE IV-A-8 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
8 RES AT 0.94 MILES SSE ANNUALBETAAIR DOSE = 4.42E-01 MILLRADS ANNUALGAMMAAIRDOSE = 1.20E-01 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
______-__+-_________+________-_+________-_+_______-__+________-_+_______-__+________-_+________-_+
PLUME
- 7.02E-02 : 7.02E-02 : 7.02E-02 : 7.02E-02 : 7.02E-02 : 7.02E-02 : 7.46E-02 : 2.61E-01
_________+______-___+________-_+________-_+________-_+________-_+________-_+________-_+________-_+
GROUND
- 4.98E-05 : 4.98E-05 : 4.98E-05 : 4.98E-05 : 4.98E-05 : 4.98E-05 : 4.98E-05 : 5.93E-05
_________+__________+__________+__________+__________+__________+__________+__________+__________+
INHAL ADULT 1.34E-04 1.24E-04 1.79E-05 1.45E-04 1.63E-04 8.50E-03 1.19E-04 1.19E-04
_________+-_________+________-_+_________-+________-_+_______-__+________-_+________-_+________-_+
TEEN
- 1.39E-04 : 1.25E-04 : 2.52E-05 : 1.55E-04 : 1.80E-04 : 1.04E-02 : 1.20E-04 : 1.20E-04
_________+______-___+________-_+________-_+________-_+________-_+_______-__+_______-__+________-_+
CHILD
- 1.25E-04 : 1.08E-04 : 3.43E-05 : 1.40E-04 : 1.62E-04 : 1.15E-02 : 1.06E-04 : 1.06E-04
_________+______-___+________-_+________-_+________-_+________-_+________-_+________-_+________-_+
INFANT : 7.49E-05 : 6.18E-05 : 2.70E-05 : 9.27E-05 : 9.78E-05 : 1.05E-02 : 6.10E-05 : 6.10E-05
_____-___+-_________+________-_+_________-+__________+__________+__________+_________-+________-_+
IV-12
TABLE IV-A-9 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
9 RES AT 0.74 MILES S ANNUALBETAAIRDOSE = 4.67E-01 MILLRADS ANNUAL_GAMMAAIRDOSE = 1.27E-01 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
_____-___+_-________+_________-+_________-+________-_+_________-+__________+_________-+________-_+
PLUME
- 7.41E-02 : 7.41E-02 : 7.41E-02 : 7.41E-02 : 7.41E-02 : 7.41E-02 : 7.87E-02 : 2.75E-01
_________+__________+__________+__________+__________+__________+__________+__________+__________+
GROUND
- 3.94E-05 : 3.94E-05 : 3.94E-05 : 3.94E-05 : 3.94E-05 : 3.94E-05 : 3.94E-05 : 4.69E-05 INHAL ADULT 1.41E-04 1.30E-04 1.90E-05 1.53E-04 1.72E-04 8.99E-03 1.26E-04 1.26E-04
_____-___+_-________+_________-+________-_+________-_+_______-__+________-_+________-_+________-_+
TEEN
- 1.47E-04 : 1.32E-04 : 2.67E-05 : 1.64E-04 : 1.90E-04 : 1.10E-02 : 1.27E-04 : 1.27E-04
______-__+_-________+________-_+________-_+__________+-_________+__________+_________-+________-_+
CHILD
- 1.32E-04 : 1.14E-04 : 3.62E-05 : 1.48E-04 : 1.71E-04 : 1.22E-02 : 1.12E-04 : 1.12E-04
_________+__________+__________+__________+__________+__________+__________+__________+__________+
INFANT : 7.91E-05 : 6.53E-05 : 2.85E-05 : 9.79E-05 : 1.03E-04 : 1.11E-02 : 6.44E-05 : 6.44E-05
______-__+_-________+________-_+________-_+________-_+________-_+________-_+________-_+________-_+
IV-13
TABLE IV-A-10 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
10 RES AT 0.65 MILES SSW ANNUALBETAAIRDOSE = 4.86E-01 MILLRADS ANNUALGAMMAAIRDOSE = 1.31E-01 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
______-__+-_________+________-_+________-_+_______-__+_______-__+________-_+________-_+________-_+
PLUME
- 7.65E-02 : 7.65E-02 : 7.65E-02 : 7.65E-02 : 7.65E-02 : 7.65E-02 : 8.13E-02 : 2.86E-01
_________+______-___+_________-+_______-__+________-_+________-_+________-_+________-_+________-_+
GROUND
- 2.48E-05 : 2.48E-05 : 2.48E-05 : 2.48E-05 : 2.48E-05 : 2.48E-05 : 2.48E-05 : 2.95E-05
_________+__________+__________+__________+__________+__________+__________+__________+__________+
INHAL ADULT 1.48E-04 1.37E-04 1.97E-05 1.60E-04 1.80E-04 9.36E-03 1.32E-04 1.32E-04
_______-+__________+__________+__________+__________+__________+__________+__--________+-________+
TEEN
- 1.54E-04 : 1.39E-04 : 2.77E-05 : 1.72E-04 : 1.99E-04 : 1.15E-02 : 1.33E-04 : 1.33E-04
_________+ ______
___+__
+_____
____+
__+___
___+_---________-+
+
CHILD
- 1.39E-04 : 1.20E-04 : 3.77E-05 : 1.56E-04 : 1.79E-04 : 1.27E-02 : 1.18E-04 : 1.18E-04
_________+ ______
___+__
+_____
____+
__+___
___+_---+-+-+-___-+
+
INFANT : 8.30E-05 : 6.87E-05 : 2.97E-05 : 1.03E-04 : 1.08E-04 : 1.16E-02 : 6.78E-05 : 6.78E-05
_________+ ______
___+__
+_____
____+
__+___
___+_---________+-+
+
IV-14
TABLE IV-A-11 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
11 RES AT 0.73 MILES SW ANNUALBETAAIRDOSE = 3.19E-01 MILLRADS ANNUALGAMMAAIRDOSE = 8.69E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
______-__+_-________+________-_+_________-+_________-+_________-+________-_+_________-+________-_+
PLUME
- 5.07E-02 : 5.07E-02 : 5.07E-02 : 5.07E-02 : 5.07E-02 : 5.07E-02 : 5.39E-02 : 1.88E-01
__---+_____
____+
____+
___+
___+_
___+_
__+_---________-+____-_
+
GROUND
- 1.76E-05 : 1.76E-05 : 1.76E-05 : 1.76E-05 : 1.76E-05 : 1.76E-05 : 1.76E-05 : 2.10E-05
_________+__________+__________+__________+__________+__________+__________+__________+__________+
INHAL ADULT 9.65E-05 8.93E-05 1.29E-05 1.04E-04 1.17E-04 6.13E-03 8.60E-05 8.60E-05
_________+______-___+________-_+________-_+________-_+________-_+________-_+________-_+_______---_
TEEN
- 1.OOE-04 : 9.02E-05 : 1.82E-05 : 1.12E-04 : 1.30E-04 : 7.52E-03 : 8.68E-05 : 8.67E-05
_________+-_________+_______-__+________-_+________-_+________-_+________-_+________-_+________-_+
CHILD
- 9.05E-05 : 7.82E-05 : 2.47E-05 : 1.01E-04 : 1.17E-04 : 8.33E-03 : 7.66E-05 : 7.66E-05
_________+______-___+________-_+________-_+________-_+________-_+_______-__+________-_+________-_+
INFANT : 5.41E-05 : 4.47E-05 : 1.95E-05 : 6.69E-05 : 7.06E-05 : 7.59E-03 : 4.41E-05 : 4.41E-05
______-__+_-________+________-_+________-_+________-_+_______-__+_______-__+_________-+________-_+
IV-15
TABLE IV-A-12 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
12 RES AT 1.06 MILES WSW ANNUALBETAAIR DOSE = 1.84E-01 MILLRADS ANNUALGAMMAAIRDOSE = 5.02E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
______-__+-_________+_________-+_________-+________-_+_________-+________-_+________-_+________-_+
PLUME
- 2.92E-02 : 2.92E-02 : 2.92E-02 : 2.92E-02 : 2.92E-02 : 2.92E-02 : 3.11E-02 : 1.09E-01
_______-+__________+__________+__________+__________+__________+__________+__--________+-________+
GROUND
- 1.06E-05 : 1.06E-05 : 1.06E-05 : 1.06E-05 : 1.06E-05 : 1.06E-05 : 1.06E-05 : 1.26E-05
_________+__________+__________+__________+__________+__________+__________+__________+__________+
INHAL ADULT 5.56E-05 5.15E-05 7.43E-06 6.02E-05 6.76E-05 3.52E-03 4.96E-05 4.96E-05
_______--+__________+__________+______
___+__________+__________+_________+__--________+-________+
TEEN
- 5.78E-05 : 5.20E-05 : 1.04E-05 : 6.46E-05 : 7.47E-05 : 4.31E-03 : 5.01E-05 : 5.OOE-05
_________+ ______
___+__
+_____
____+
__+___
___+_---________+-+
+
CHILD
- 5.22E-05 : 4.51E-05 : 1.42E-05 : 5.84E-05 : 6.74E-05 : 4.78E-03 : 4.42E-05 : 4.42E-05
_________+ ______
___+__
+_____
____+
__+___
___+_---________-+
+
INFANT : 3.12E-05 : 2.58E-05 : 1.12E-05 : 3.85E-05 : 4.06E-05 : 4.35E-03 : 2.54E-05 : 2.54E-05
_________+ ______
___+__
+_____
____+
__+___
___+_---________-+
+
IV-16
TABLE IV-A-13 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
13 RES AT 1.20 MILES W ANNUALBETAAIRDOSE = 1.14E-01 MILLRADS ANNUALGAMMAAIRDOSE = 3.08E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
-_ +_- ________
+_________-+__________+__________+__________+__________+_______--___+____-
+
PLUME
- 1.80E-02 : 1.80E-02 : 1.80E-02 : 1.80E-02 : 1.80E-02 : 1.80E-02 : 1.91E-02 : 6.69E-02
__---+_____
+____
+___
_+___
_+__
__+_--
_+___
+
GROUND
- 8.28E-06 : 8.28E-06 : 8.28E-06 : 8.28E-06 : 8.28E-06 : 8.28E-06 : 8.28E-06 : 9.86E-06
______-_+__________+__________+__________+__________+__________+__________----+-_________+____-__+
INHAL ADULT 3.45E-05 3.19E-05 4.58E-06 3.73E-05 4.19E-05 2.17E-03 3.08E-05 3.08E-05
__---+_____
+____
+___
_+___
_+__
__+_---________-+
_ +
TEEN
- 3.58E-05 : 3.22E-05 : 6.44E-06 : 4.OOE-05 : 4.63E-05 : 2.66E-03 : 3.10E-05 : 3.10E-05
__---+_____
+____
+___
_+___
_+__
__+_---________-+____-_
+
CHILD
- 3.23E-05 : 2.79E-05 : 8.74E-06 : 3.62E-05 : 4.17E-05 : 2.95E-03 : 2.74E-05 : 2.74E-05
__---+_____
+____
+___
_+___
_+__
__+_---________-+
+
INFANT : 1.93E-05 : 1.60E-05 : 6.89E-06 : 2.38E-05 : 2.52E-05 : 2.69E-03 : 1.58E-05 : 1.58E-05
__---+_____
+____
+___
_+___
_+__
__+_---+-______-+___- __
+
IV-17
TABLE IV-A-14 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
14 RES AT 2.27 MILES WNW ANNUALBETA AIRDOSE = 6.95E-02 MILLRADS ANNUALGAMMAAIRDOSE = 1.88E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
______-__+-_________+________-_+_________-+________-_+_______-__+_______-__+________-_+________-_+
PLUME
- 1.10E-02 : 1.10E-02 : 1.10E-02 : 1.10E-02 : 1.10E-02 : 1.10E-02 : 1.17E-02 : 4.09E-02
_________+______-___+_________-+_________-+________-_+_______-__+________-_+________-_+________-_+
GROUND
- 3.10E-06 : 3.10E-06 : 3.10E-06 : 3.10E-06 : 3.10E-06 : 3.10E-06 : 3.10E-06 : 3.69E-06
_________+__________+__________+__________+__________+__________+__________+__________+__________+
INHAL ADULT 2.11E-05 1.95E-05 2.76E-06 2.28E-05 2.55E-05 1.31E-03 1.89E-05 1.88E-05
_______-+__________+__________+__________+__________+__________+__________+__--________+-________+
TEEN
- 2.19E-05 : 1.97E-05 : 3.88E-06 : 2.44E-05 : 2.82E-05 : 1.60E-03 : 1.90E-05 : 1.90E-05
_________+ ______
___+__
+_____
____+
__+___
___+_--+-________-+
+
CHILD
- 1.98E-05 : 1.71E-05 : 5.26E-06 : 2.21E-05 : 2.54E-05 : 1.78E-03 : 1.68E-05 : 1.68E-05
_________+ ______
___+__
+_____
____+
__+___
___+_---+-+-_____-+
+
INFANT : 1.18E-05 : 9.78E-06 : 4.14E-06 : 1.45E-05 : 1.53E-05 : 1.62E-03 : 9.66E-06 : 9.66E-06
______-__+-_________+_________-+_________-+________-_+_______-__+________-_+________-_+________-_+
IV-18
TABLE IV-A-15 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
15 RES AT 2.40 MILES NW ANNUAL BETA AIR DOSE = 6.09E-02 MILLRADS ANNUALGAMMAAIRDOSE = 1.65E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
_____-___+_-________+________-_+________-_+_______-__+________-_+________-_+________-_+________-_+
PLUME
- 9.60E-03 : 9.60E-03 : 9.60E-03 : 9.60E-03 : 9.60E-03 : 9.60E-03 : 1.02E-02 : 3.58E-02
_____-___+_-________+_________-+________-_+_______-__+_______-__+________-_+________-_+________-_+
GROUND
- 3.31E-06 : 3.31E-06 : 3.31E-06 : 3.31E-06 : 3.31E-06 : 3.31E-06 : 3.31E-06 : 3.94E-06
_________+__________+__________+__________+__________+__________+__________+__________+__________+
INHAL ADULT 1.85E-05 1.72E-05 2.43E-06 2.OOE-05 2.24E-05 1.15E-03 1.65E-05 1.65E-05
_____-___+_-________+_________-+________-_+________-_+________-_+_______-__+_______-__+________-_+
TEEN
- 1.92E-05
- 1.73E-05 : 3.41E-06 : 2.14E-05 : 2.47E-05 : 1.41E-03 : 1.67E-05 : 1.67E-05
_____-___+_-________+_________-+________-_+________-_+________-_+_______-__+________-_+________-_+
CHILD
- 1.73E-05 : 1.50E-05 : 4.63E-06 : 1.94E-05 : 2.23E-05 : 1.56E-03 : 1.47E-05 : 1.47E-05
_____-___+_-________+_________-+_______-__+________-_+________-_+________-_+________-_+________-_+
INFANT : 1.03E-05 : 8.58E-06 : 3.65E-06 : 1.28E-05 : 1.34E-05 : 1.42E-03
- 8.48E-06 : 8.47E-06
_____-___+_-________+_________-+________-_+________-_+_______-__+________-_+________-_+________-_+
IV-19
TABLE IV-A-16 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
16 RES AT 2.08 MILES NNW ANNUALBETAAIRDOSE = 6.46E-02 MILLRADS ANNUALGAMMAAIRDOSE = 1.75E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
_______-+__________+__________+__________+__________+__________+__________+__--________+-________+
PLUME
- 1.02E-02 : 1.02E-02 : 1.02E-02 : 1.02E-02 : 1.02E-02 : 1.02E-02 : 1.08E-02 : 3.80E-02
_______-+__________+__________+__________+__________+__________+__________+__--________+-________+
GROUND
- 6.00E-06 : 6.00E-06 : 6.00E-06 : 6.OOE-06 : 6.00E-06 : 6.OOE-06 : 6.00E-06 : 7.14E-06
_________+__________+__________+__________+__________+__________+__________+__________+__________+
INHAL ADULT 1.96E-05 1.82E-05 2.56E-06 2.12E-05 2.37E-05 1.22E-03 1.75E-05 1.75E-05
_________+ ______
___+__
+_____
____+
__+___
___+_---________-+
+
TEEN
- 2.04E-05 : 1.84E-05 : 3.61E-06 : 2.27E-05 : 2.62E-05 : 1.49E-03 : 1.77E-05 : 1.77E-05
_________+ ______
___+__
+_____
____+
__+___
___+_---________-+
+
CHILD
- 1.84E-05 : 1.59E-05 : 4.90E-06 : 2.05E-05 : 2.36E-05 : 1.65E-03 : 1.56E-05 : 1.56E-05
_________+-_________+_______-__+________-_+________-_+_______-_+_______-__+_______-__+________-_+
INFANT : 1.10E-05 : 9.10E-06 : 3.86E-06 : 1.35E-05 : 1.42E-05 : 1.50E-03 : 8.98E-06 : 8.98E-06
_____-___+-_________+_________-+_________-+_________-+__________+__________+__________+_________-+
IV-20
TABLE IV-A-17 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
17 VEG AT 1.93 MILES NNE ANNUALBETAAIRDOSE = 6.58E-02 MILLRADS ANNUALGAMMAAIRDOSE = 1.78E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
______-_+__________+__________+__________+__________+__________+__________--+--I--+-+-+-+-__+___+
PLUME
- 1.04E-02 : 1.04E-02 : 1.04E-02 : 1.04E-02 : 1.04E-02 : 1.04E-02 : 1.10E-02 : 3.87E-02
__---+_____
+____
+___
_+___
_+__
__+_---________-+____-_
+
GROUND
- 5.38E-06 : 5.38E-06 : 5.38E-06 : 5.38E-06 : 5.38E-06 : 5.38E-06 : 5.38E-06 : 6.40E-06
_________+__________+__________+__________+__________+__________+__________+__________+__________+
VEGET ADULT 6.37E-05 4.62E-05 3.80E-05 8.67E-05 1.23E-04 1.72E-02 3.26E-05 3.24E-05
______-__+_______----_+__________+__________+__________+_________+__________+__----__+_-________+
TEEN
- 7.79E-05 : 5.17E-05 : 5.51E-05 : 1.14E-04 : 1.65E-04 : 2.16E-02 : 3.74E-05 : 3.70E-05
__---+_____
+____
+___
_+___
_+__
__+_---________-+____-_
+
CHILD
- 1.28E-04 : 6.84E-05 : 1.27E-04 : 1.85E-04 : 2.60E-04 : 4.04E-02 : 5.81E-05 : 5.75E-05
__---+_____
+____
+___
_+___
_+__
__+_---+-______-+____-_
+
IV-21
I TABLE IV-A-18 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
18 VEG AT 3.29 MILES NE ANNUALBETAAIR DOSE = 1.14E-02 MILLRADS ANNUALGAMMAAIRDOSE = 3.07E-03 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
______-__+-_________+________-_+__--______+__________+__________+__________+__________+--+_____---
PLUME
- 1.79E-03 : 1.79E-03 : 1.79E-03 : 1.79E-03 : 1.79E-03 : 1.79E-03 : 1.90E-03 : 6.70E-03
_________+-_________+_______-__+________-_+________-_+_______-__+________-_+________-_+________-_+
GROUND
- 7.84E-07 : 7.84E-07 : 7.84E-07 : 7.84E-07 : 7.84E-07 : 7.84E-07 : 7.84E-07 : 9.33E-07
_________+__________+__________+__________+__________+__________+__________+__________+__________+
VEGET ADULT 1.02E-05 7.65E-06 5.53E-06 1.35E-05 1.88E-05 2.50E-03 5.67E-06 5.63E-06
_________+______-___+_________-+________-_+________-_+________-_+________-_+________-_+________-_+
TEEN
- 1.24E-05 : 8.58E-06 : 8.02E-06 : 1.77E-05 : 2.51E-05 : 3.15E-03 : 6.50E-06 : 6.44E-06
_________+-_________+________-_+_________-+________-_+_______-__+_______-__+________-_+________-_+
CHILD
- 2.02E-05 : 1.16E-05 : 1.84E-05 : 2.86E-05 : 3.94E-05 : 5.88E-03 : 1.01E-05 : 1.OOE-05
_____-___+-_________+________-_+_________-+________-_+________-_+________-_+_________-+_________-+
IV-22
TABLE IV-A-19 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
19 VEG AT 4.79 MILES ENE ANNUAL BETAAIRDOSE = 5.55E-03 MILLRADS ANNUALGAMMAAIRDOSE = 1.49E-03 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
__---+_____
+____
+___
_+___
_+__
__+_---________-+____-_
+
PLUME
- 8.69E-04 : 8.69E-04 : 8.69E-04 : 8.69E-04 : 8.69E-04 : 8.69E-04 : 9.24E-04 : 3.26E-03
__---+_____
+____
+___
_+___
_+__
__+_---________-+____-_
+
GROUND
- 1.94E-07 : 1.94E-07 : 1.94E-07 : 1.94E-07 : 1.94E-07 : 1.94E-07 : 1.94E-07 : 2.30E-07
_________+__________+__________+__________+__________+__________+__________+__________+__________+
VEGET ADULT 3.88E-06 3.25E-06 1.36E-06 4.71E-06 6.OOE-06 6.18E-04 2.76E-06 2.76E-06
_____-___+_-________+_________-+________-_+_______-__+_______-__+_______-__+_______-__+________-_+
TEEN
- 4.62E-06 : 3.68E-06 : 1.98E-06 : 5.92E-06 :17.76E-06 : 7.77E-04 : 3.17E-06 : 3.15E-06
______-__+_-________+________-_+________-_+_______-__+_______-__+_______-__+________-_+________-_+
CHILD
- 7.41E-06 : 5.29E-06 : 4.55E-06 : 9.47E-06 : 1.21E-05 : 1.45E-03 : 4.92E-06 : 4.90E-06
_____-___+_-___-____+________-_+________-_+_________-+__________+__________+__________+_________-+
IV-23
t TABLE IV-A-20 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
20 VEG AT 1.74 MILES SE ANNUALBETAAIR DOSE = 1.11E-01 MILLRADS ANNUALGAMMAAIRDOSE = 2.99E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
_______-_+_-_____-
+__________+_______+_______+_______+----
+-
+
-__--+_+
PLUME
- 1.74E-02 : 1.74E-02 : 1.74E-02 : 1.74E-02 : 1.74E-02 : 1.74E-02 : 1.85E-02 : 6.51E-02
_______-+__________+__________+__________+__________+__________+__________+__--________+-________+
GROUND
- 9.92E-06 : 9.92E-06 : 9.92E-06 : 9.92E-06 : 9.92E-06 : 9.92E-06 : 9.92E-06 : 1.18E-05
_________+__________+__________+__________+__________+__________+__________+__________+__________+
VEGET ADULT 1.12E-04 8.00E-05 7.OOE-05 1.55E-04 2.21E-04 3.16E-02 5.49E-05 5.45E-05
_________+______-___+_________-+_________-+________-_+________-_+________-_+________-_+________-_+
TEEN
- 1.38E-04 : 8.94E-05 : 1.02E-04 : 2.05E-04 : 2.99E-04 : 3.98E-02 : 6.31E-05 : 6.23E-05
_________+-_________+_________-+_________-+________-_+________-_+________-_+________-_+________-_+
CHILD
- 2.26E-04 : 1.17E-04 : 2.34E-04 : 3.32E-04 : 4.69E-04 : 7.45E-02 : 9.80E-05 : 9.68E-05
______-__+_-________+_________-+_________-+________-_+________-_+________-_+________-_+________-_+
IV-24
TABLE IV-A-21 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
21 VEG AT 0.94 MILES SSE ANNUALBETAAIRDOSE = 4.42E-01 MILLRADS ANNUALGAMMAAIRDOSE = 1.20E-01 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
_____-___+_-________+_________-+_________-+________-_+________-_+________-_+_______-__+________-_+
PLUME
- 7.02E-02 : 7.02E-02 : 7.02E-02 : 7.02E-02 : 7.02E-02 : 7.02E-02 : 7.46E-02 : 2.61E-01
__---+_____
+____
+___
_+___
_+__
__+_---________+-+___-_
+
GROUND
- 4.98E-05 : 4.98E-05 : 4.98E-05 : 4.98E-05 : 4.98E-05 : 4.98E-05 : 4.98E-05 : 5.93E-05
_________+__________+__________+__________+__________+__________+__________+__________+__________+
VEGET ADULT 5.06E-04 3.44E-04 3.52E-04 7.20E-04 1.05E-03 1.59E-01 2.18E-04 2.16E-04
__---+_____
+____
+___
_+___
_+__
__+_---________-+____-_
+
TEEN
- 6.26E-04 : 3.83E-04 : 5.11E-04 : 9.62E-04 : 1.44E-03 : 2.OOE-01 : 2.50E-04 : 2.47E-04
__---+_____
+____
+___
_+___
_+__
__+_---________-+____-_
+
CHILD
- 1.03E-03 : 4.84E-04 : 1.17E-03 : 1.56E-03 : 2.26E-03 : 3.75E-01 : 3.89E-04 : 3.83E-04
__---+_____
+____
+___
_+___
_+__
__+_---________-+____-_
+
IV-25
TABLE IV-A-22 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
22 VEG AT 0.74 MILES S ANNUALBETAAIRDOSE = 4.67E-01 MILLRADS ANNUALGAMMAAIRDOSE = 1.27E-01 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
___-+-_________
+_________-+__________+__________+__________+__________+_____---____-+__-
+
PLUME
- 7.41E-02 : 7.41E-02 : 7.41E-02 : 7.41E-02 : 7.41E-02 : 7.41E-02 : 7.87E-02 : 2.75E-01
_____-___+_________-.+_-_______+_________-+_________-+_________-+__________+-_________+_________-+
GROUND
- 3.94E-05 : 3.94E-05 : 3.94E-05 : 3.94E-05 : 3.94E-05 : 3.94E-05 : 3.94E-05 : 4.69E-05
_________+__________+__________+__________+__________+__________+__________+__________+__________+
VEGET ADULT 4.58E-04 3.29E-04 2.79E-04 6.27E-04 8.91E-04 1.26E-01 2.29E-04 2.28E-04
_________+______-___+________-_+________-_+________-_+________-_+________-_+________-_+________-_+
TEEN
- 5.60E-04 : 3.68E-04 : 4.04E-04 : 8.27E-04 : 1.20E-03 : 1.59E-01 : 2.63E-04 : 2.60E-04
_________+-_________+_______-__+________-_+________-_+________-_+________-_+________-_+________-_+
CHILD
- 9.20E-04 : 4.84E-04 : 9.30E-04 : 1.34E-03 : 1.89E-03 : 2.97E-01 : 4.09E-04 : 4.04E-04
______-__+-_________+_________-+_________-+________-_+________-_+_________-+__________+_________-+
IV-26
TABLE IV-A-23 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
23 VEG AT 0.65 MILES SSW ANNUALBETAAIRDOSE = 4.86E-01 MILLRADS ANNUALGAMMAAIRDOSE = 1.31E-01 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
_____-___+_-________+________-_+_________-+__________+__________+_________-+_______-__+________-_+
PLUME
- 7.65E-02 : 7.65E-02 : 7.65E-02 : 7.65E-02 : 7.65E-02 : 7.65E-02 : 8.13E-02 : 2.86E-01
______-_+_-________+________-_+________-_+________---_+_________+_________+_____--___-+_-________+
GROUND
- 2.48E-05 : 2.48E-05 : 2.48E-05 : 2.48E-05 : 2.48E-05 : 2.48E-05 : 2.48E-05 : 2.95E-05
_________+__________+__________+__________+__________+__________+__________+__________+__________+
VEGET ADULT 3.84E-04 3.03E-04 1.75E-04 4.90E-04 6.56E-04 7.92E-02 2.41E-04 2.40E-04
______-__+_-________+_________-+_________-+__________+-_________+__________+_________-+________-_+
TEEN
- 4.62E-04 : 3.42E-04 : 2.54E-04 : 6.29E-04 : 8.65E-04 : 9.96E-02 : 2.76E-04 : 2.74E-04
_____-___+_-________+_________-+_________-+________-_+________-_+________-_+________-_+________-_+
CHILD
- 7.49E-04 : 4.76E-04 : 5.83E-04 : 1.01E-03 : 1.36E-03 : 1.86E-01 : 4.29E-04 : 4.26E-04
______-__+_-________+_________-+_________-+_________-+________-_+_________-+________-_+_______-__+
IV-27
TABLE IV-A-24 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
24 VEG AT 1.41 MILES SW ANNUALBETAAIRDOSE = 6.26E-02 MILLRADS ANNUALGAMMAAIRDOSE = 1.71E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
______-__+-_________+________-_+_______-__+________-_+________-_+________-_+________-_+________-_+
PLUME
- 9.94E-03 : 9.94E-03 : 9.94E-03 : 9.94E-03 : 9.94E-03 : 9.94E-03 : 1.06E-02 : 3.69E-02
_________+-_________+_________-+_________-+________-_+________-_+________-_+________-_+________-_+
GROUND
- 3.32E-06 : 3.32E-06 : 3.32E-06 : 3.32E-06 : 3.32E-06 : 3.32E-06 : 3.32E-06 : 3.95E-06
_________+__________+__________+__________+__________+__________+__________+__________+__________+
VEGET ADULT 4.99E-05 3.91E-05 2.35E-05 6.42E-05 8.64E-05 1.06E-02 3.07E-05 3.06E-05
_________+-_________+________-_+_________-+________-_+________-_+________-_+________-_+________-_+
TEEN
- 6.02E-05 : 4.40E-05 : 3.41E-05 : 8.26E-05
- 1.14E-04 : 1.34E-02
- 3.52E-05
- 3.49E-05
_________+______-___+________-_+________-_+________-_+________-_+________-_+________-_+________-_+
CHILD
- 9.77E-05 : 6.10E-05 : 7.83E-05 : 1.33E-04 : 1.79E-04 : 2.50E-02 : 5.47E-05 : 5.43E-05
______-__+-_________+________-_+_______-__+________-_+________-_+________-_+________-_+________-_+
IV-28
TABLE IV-A-25 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
25 VEG AT 1.21 MILES WSW ANNUALBETA AIR DOSE = 1.23E-01 MILLRADS ANNUALGAMMAAIRDOSE = 3.34E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
+ _ _ _ _ _ _ _ _ _ _ + _ _ _ _ _ _ _ _ _ _ + _ _ _ _ _ _ _ _ _ _ + _ _ _ _ _ _ _ _ _ _ + _ _ _ _ _ _ _ _ _ _ + _ _ _ _ _ _ _ _ _ _ + _ __-
+-
-+
PLUME
- 1.95E-02 : 1.95E-02 : 1.95E-02 : 1.95E-02 : 1.95E-02 : 1.95E-02 : 2.07E-02 : 7.24E-02
______-___+__________+__________+_________+______-___+__________+__________+_--+-+-______-+___-__+
GROUND
- 7.05E-06 : 7.05E-06 : 7.05E-06 : 7.05E-06 : 7.05E-06 : 7.05E-06 : 7.05E-06 : 8.40E-06
_________+__________+__________+__________+__________+__________+__________+__________+__________+
VEGET ADULT 1.01E-04 7.81E-05 4.99E-05 1.31E-04 1.79E-04 2.26E-02 6.02E-05 5.99E-05
__---+_____
+____
+___
_+___
_+__
__+_---________-+
+
TEEN
- 1.22E-04 : 8.78E-05 : 7.24E-05 : 1.70E-04 : 2.37E-04 : 2.84E-02 : 6.91E-05 : 6.85E-05
__---+_____
+____
+___
_+___
_+__
__+_---________-+
_ +
CHILD
- 1.99E-04 : 1.21E-04 : 1.66E-04 : 2.74E-04 : 3.72E-04 : 5.31E-02 : 1.07E-04 : 1.06E-04
__---+_____
+____
+___
_+___
_+__
__+_---________-+
_ +
IV-29
TABLE IV-A-26 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
26 VEG AT 1.23 MILES W ANNUALBETAAIR DOSE = 1.05E-01 MILLRADS ANNUAL_GAMMAAIRDOSE = 2.85E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
_______-+__________+__________+__________+__________+__________+__________+__--________+-________+
PLUME
- 1.66E-02 : 1.66E-02 : 1.66E-02 : 1.66E-02 : 1.66E-02 : 1.66E-02 : 1.77E-02 : 6.19E-02
_______-+__________+__________+__________+__________+__________+__________+__--________+-________+
GROUND
- 7.66E-06 : 7.66E-06 : 7.66E-06 : 7.66E-06 : 7.66E-06
- 7.66E-06 : 7.66E-06 : 9.12E-06
_________+__________+__________+__________+__________+__________+__________+__________+__________+
VEGET ADULT 9.62E-05 7.13E-05 5.41E-05 1.29E-04 1.80E-04 2.45E-02 5.18E-05 5.15E-05
_________+______-___+________-_+________-_+________-_+________-_+________-_+________-_+________-_+
TEEN
- 1.17E-04 : 7.98E-05: 7.85E-05 : 1.69E-04 : 2.42E-04 : 3.08E-02 : 5.95E-05 : 5.89E-05
_________+-_________+________-_+_________-+________-_+________-_+________-_+________-_+________-_+
CHILD
- 1.92E-04 : 1.07E-04 : 1.81E-04 : 2.73E-04 : 3.80E-04 : 5.76E-02 : 9.24E-05 : 9.15E-05
_____-___+_-________+________-_+________-_+________-_+________-_+________-_+_________-+_________-+
IV-30
TABLE IV-A-27 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
27 VEG AT 2.64 MILES WNW ANNUALBETA AIR DOSE = 4.49E-02 MILLRADS ANNUAL_GAMMAAIRDOSE = 1.21E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
______-__+_-________+_________-+_________-+_________-+_________-+__________+_________-+________-_+
PLUME
- 7.07E-03 : 7.07E-03 : 7.07E-03 : 7.07E-03 : 7.07E-03 : 7.07E-03 : 7.51E-03 : 2.64E-02
_____-___+_-________+________-_+_________-+__________+-_________+__________+_________-+________-_+
GROUND
- 1.88E-06 : 1.88E-06 : 1.88E-06 : 1.88E-06 : 1.88E-06 : 1.88E-06 : 1.88E-06 : 2.24E-06
_________+__________+__________+__________+__________+__________+__________+__________+__________+
VEGET ADULT 3.31E-05 2.70E-05 1.33E-05 4.11E-05 5.37E-05 6.00E-03 2.22E-05 2.22E-05
_____-___+_-________+________-_+_______-__+________-_+________-_+________-+-_________+_________+-
TEEN
- 3.96E-05
- 3.05E-05 : 1.92E-05 : 5.23E-05 : 7.01E-05 : 7.55E-03 : 2.55E-05
- 2.53E-05
_____-___+_-________+_______--_+__________+__________+__________+__________+__---_-___-+__-______+
CHILD
- 6.39E-05 : 4.32E-05 : 4.42E-05 : 8.39E-05 : 1.10E-04 : 1.41E-02 : 3.96E-05 : 3.94E-05
_____-___+_-________+_________-+________-_+________-_+________-_+________-_+________-_+________-_+
IV-31
TABLE IV-A-28 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
28 VEG AT 2.63 MILES NW ANNUALBETAAIRDOSE = 4.74E-02 MILLRADS ANNUALGAMMAAIRDOSE = 1.28E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
______-__+_-________+________-_+________-_+________-_+_______-__+________-_+________-_+________-_+
PLUME
- 7.46E-03 : 7.46E-03 : 7.46E-03 : 7.46E-03 : 7.46E-03 : 7.46E-03 : 7.93E-03 : 2.79E-02
_________+______-___+_________-+________-_+________-_+________-_+________-_+________-_+________-_+
GROUND
- 2.48E-06 : 2.48E-06 : 2.48E-06 : 2.48E-06 : 2.48E-06 : 2.48E-06 : 2.48E-06 : 2.95E-06
_________+__________+__________+__________+__________+__________+__________+__________+__________+
VEGET ADULT 3.78E-05 2.97E-05 1.75E-05 4.84E-05 6.50E-05 7.91E-03 2.35E-05 2.34E-05
_________+-_________+_______-__+________-_+________-_+________-_+________-_+________-_+________-_+
TEEN
- 4.55E-05 : 3.35E-05 : 2.54E-05 : 6.22E-05 : 8.58E-05 : 9.96E-03 : 2.69E-05 : 2.67E-05
_________+-_________+_______-__+________-_+________-_+________-_+________-_+________-_+________-_+
CHILD
- 7.38E-05 : 4.65E-05 : 5.83E-05 : 1.00E-04 : 1.35E-04 : 1.86E-02 : 4.18E-05 : 4.15E-05
______-__+-_________+________-_+________-_+________-_+________-_+________-_+________-_+________-_+
IV-32
TABLE IV-A-29 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
29 VEG AT 4.01 MILES NNW ANNUALBETAAIRDOSE = 1.55E-02 MILLRADS ANNUALGAMMAAIRDOSE = 4.14E-03 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
_____-___+_-________+________-_+________-_+_________-+__________+__________+__________+_________-+
PLUME
- 2.41E-03 : 2.41E-03 : 2.41E-03 : 2.41E-03 : 2.41E-03 : 2.41E-03 : 2.56E-03 : 9.08E-03
_________+__________+__________+__________+__________+__________+__________+__________+__________+
GROUND
- 1.19E-06 : 1.19E-06 : 1.19E-06 : 1.19E-06 : 1.19E-06 : 1.19E-06 : 1.19E-06 : 1.41E-06 VEGET ADULT 1.47E-05 1.08E-05 8.33E-06 1.97E-05 2.76E-05 3.76E-03 7.84E-06 7.79E-06
_____-___+_-________+_________-+________-_+__________+-_________+_________-+_________-+_________-+
TEEN
- 1.79E-05 : 1.21E-05 : 1.21E-05 : 2.58E-05 : 3.70E-05 : 4.74E-03 : 9.00E-06 : 8.91E-06
_____-___+_-___-____+_________-+_________-+________-_+_______-__+_______-__+________-_+________-_+
CHILD
- 2.92E-05 : 1.62E-05 : 2.78E-05 : 4.18E-05 : 5.81E-05 : 8.86E-03 : 1.40E-05 : 1.38E-05
______-__+_-________+________-_+__________+-__________+__________+__________+__---____+__-_______+
IV-33
TABLE IV-A-30 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
30 BEEF AT 4.73 MILES SE ANNUALBETA AIRDOSE = 1.23E-02 MILLRADS ANNUALGAMMA_AIRDOSE = 3.34E-03 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
__---+_____
+____
+___
_+___
_+__
__+_---+-+-_____-+___-_
+
PLUME
- 1.95E-03 : 1.95E-03 : 1.95E-03 : 1.95E-03 : 1.95E-03 : 1.95E-03 : 2.07E-03 : 7.24E-03
__---+_____
+____
+___
_+___
_+__
__+_--+-________-+
+
GROUND
- 8.50E-07 : 8.50E-07 : 8.50E-07 : 8.50E-07 : 8.50E-07 : 8.50E-07 : 8.50E-07 : 1.01E-06
_________+__________+__________+__________+__________+__________+__________+__________+__________+
MEAT ADULT 1.10E-06 9.60E-07 2.85E-07 1.27E-06 1.51E-06 1.23E-04 8.65E-07 8.61E-07
__---+_____
+____
+___
_+___
_+__
__+_--+-+-______+-+
+
TEEN
- 6.86E-07 : 5.74E-07 : 2.36E-07 : 8.44E-07 : 1.05E-06 : 8.91E-05 : 5.17E-07 : 5.13E-07
__---+_____
+____
+___
_+___
_+__
__+_--+-+-______+-+__-_
+
CHILD
- 8.57E-07 : 6.58E-07 : 4.38E-07 : 1.06E-06 : 1.30E-06 : 1.34E-04 : 6.26E-07 : 6.22E-07
__---+_____
+____
+___
_+___
_+__
__+_---+-+-+-+-+-+___-_
+
IV-34
TABLE IV-A-31 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
31 BEEF AT 1.82 MILES SSE ANNUALBETAAIRDOSE = 9.28E-02 MILLRADS ANNUALGAMMAAIRDOSE = 2.52E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
__---+_____
+___
_+__
__+_
___+
____--+-
___+
+
PLUME
- 1.47E-02 : 1.47E-02 : 1.47E-02 : 1.47E-02 : 1.47E-02 : 1.47E-02 : 1.56E-02 : 5.46E-02
-__+__________+--+
+_
+
+
+
+_____+__--_
+
GROUND
- 9.73E-06 : 9.73E-06 : 9.73E-06 : 9.73E-06 : 9.73E-06 : 9.73E-06 : 9.73E-06 : 1.16E-05
______-__+__________+__________+__________+_____----__+___--______+__________+______-------+--__+
MEAT ADULT 9.25E-06 7.68E-06 3.25E-06 1.12E-05 1.40E-05 1.40E-03 6.59E-06 6.54E-06
+-
+-------------------+-
+
+
+--
TEEN
- 5.88E-06 : 4.59E-06 : 2.70E-06 : 7.68E-06 : 9.98E-06 : 1.02E-03 : 3.94E-06 : 3.90E-06
+-
+------------------
+
+
+--
CHILD
- 7.41E-06 : 5.14E-06 : 5.00E-06 : 9.76E-06 : 1.24E-05 : 1.53E-03 : 4.77E-06 : 4.72E-06
______-__+__________+-
+_
+
+
+
_+__--_
+
IV-35
TABLE IV-A-32 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
32 BEEF AT 2.01 MILES S ANNUALBETA AIRDOSE = 4.42E-02 MILLRADS ANNUALGAMMAAIRDOSE = 1.20E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
______-__+-_________+________-_+_________-+_________-+__________+__________+__________+_________-+
PLUME
- 7.02E-03 : 7.02E-03 : 7.02E-03 : 7.02E-03 : 7.02E-03 : 7.02E-03 : 7.46E-03 : 2.61E-02
_________+______-___+_________-+________-_+________-_+_______-__+________-_+________-_+________-_+
GROUND
- 3.32E-06 : 3.32E-06 : 3.32E-06 : 3.32E-06 : 3.32E-06 : 3.32E-06 : 3.32E-06 : 3.95E-06
_________+__________+__________+__________+__________+__________+__________+__________+__________+
MEAT ADULT 4.02E-06 3.49E-06 1.11E-06 4.69E-06 5.64E-06 4.81E-04 3.11E-06 3.10E-06
_________+ ______
___+__
+_____
____+
__+___
___+_---________-+
+
TEEN
- 2.52E-06 : 2.08E-06 : 9.23E-07 : 3.14E-06 : 3.92E-06 : 3.48E-04 : 1.86E-06 : 1.85E-06
_________+ ______
___+__
+_____
____+
__+___
___+_---+-______-+____-_
+
CHILD
- 3.16E-06 : 2.38E-06 : 1.71E-06 : 3.96E-06 : 4.88E-06 : 5.24E-04 : 2.25E-06 : 2.24E-06
______-__+-_________+_________-+_________-+________-_+_______-__+________-_+________-_+________-_+
IV-36
TABLE IV-A-33 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
33 BEEF AT 2.07 MILES SSW ANNUAL BETA AIR DOSE = 3.19E-02 MILLRADS ANNUALGAMMA_AIRDOSE = 8.69E-03 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
_____-___+_-________+________-_+_________-+__________+__________+__________+_________-+________-_+
PLUME
- 5.07E-03 : 5.07E-03 : 5.07E-03 : 5.07E-03 : 5.07E-03 : 5.07E-03 : 5.39E-03 : 1.88E-02
_____-___+_-________+________-_+________-_+_________-+-_________+__________+_________-+________-_+
GROUND
- 1.45E-06 : 1.45E-06 : 1.45E-06 : 1.45E-06 : 1.45E-06 : 1.45E-06 : 1.45E-06 : 1.73E-06
_________+__________+__________+__________+__________+__________+__________+__________+__________+
MEAT ADULT 2.64E-06 2.41E-06 4.86E-07 2.93E-06 3.35E-06 2.11E-04 2.25E-06 2.24E-06
_____-___+_-________+_________-+_______-__+________-_+________-_+________-_+________-_+________-_+
TEEN
- 1.63E-06 : 1.44E-06 : 4.04E-07 : 1.90E-06 : 2.24E-06 : 1.53E-04 : 1.34E-06 : 1.33E-06
_____-___+_-________+_________-+________-_+________-_+________-_+________-_+________-_+________-_+
CHILD
- 2.02E-06 : 1.68E-06 : 7.48E-07 : 2.37E-06 : 2.77E-06 : 2.30E-04 : 1.62E-06 : 1.62E-06
______-__+_-________+________-_+_________-+_________-+________-_+_________-+_________-+________-_+
IV-37 4
TABLE IV-A-34 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
34 BEEF AT 0.85 MILES SW ANNUALBETAAIRDOSE = 2.33E-01 MILLRADS ANNUALGAMMAAIRDOSE = 6.35E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
_____-___+-_________+_________-+_________-+________-_+________-_+________-_+________-_+________-_+
PLUME
- 3.70E-02 : 3.70E-02 : 3.70E-02 : 3.70E-02 : 3.70E-02 : 3.70E-02 : 3.94E-02 : 1.38E-01
_______-_+__________+__________+__________+__________+__---_____+__-_______+_______--_+-_________+
GROUND
- 1.27E-05 : 1.27E-05 : 1.27E-05 : 1.27E-05 : 1.27E-05 : 1.27E-05 : 1.27E-05 : 1.51E-05
_________+__________+__________+__________+__________+__________+__________+__________+__________+
MEAT ADULT 1.99E-05 1.78E-05 4.23E-06 2.24E-05 2.61E-05 1.84E-03 1.64E-05 1.64E-05
_________+ ______
___ + __
+ _____
____ + ______
__ + ___
___ +_---________-+
+
TEEN
- 1.23E-05 : 1.06E-05 : 3.52E-06 : 1.47E-05 : 1.77E-05 : 1.33E-03 : 9.80E-06 : 9.75E-06
_________+ ______
___+__
+_____
____+
__+___
___+_---________-+
+
CHILD
- 1.53E-05 : 1.23E-05 : 6.52E-06 : 1.84E-05 : 2.19E-05 : 2.OOE-03 : 1.19E-05 : 1.18E-05
_____-___+-_________+________-_+________-_+________-_+________-_+_________-+_________-+________-_+
IV-38
TABLE IV-A-35 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
35 BEEF AT 2.42 MILES WSW ANNUALBETAAIRDOSE = 2.33E-02 MILLRADS ANNUALGAMMAAIRDOSE = 6.35E-03 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
___-_+- _________ +________-_
+__________+__________+__________+__________+_____---____-+__-
+
PLUME
- 3.70E-03 : 3.70E-03 : 3.70E-03 : 3.70E-03 : 3.70E-03 : 3.70E-03 : 3.94E-03 : 1.38E-02
______-_+_-________+_______-__+________-_+__________+__________+________--+_______-__--+
+
GROUND
- 1.16E-06 : 1.16E-06 : 1.16E-06 : 1.16E-06 : 1.16E-06 : 1.16E-06 : 1.16E-06 : 1.38E-06
_________+__________+__________+__________+__________+__________+__________+__________+__________+
MEAT ADULT 1.96E-06 1.77E-06 3.89E-07 2.19E-06 2.53E-06 1.69E-04 1.64E-06 1.64E-06
_____-___+_-___-____+_________-+________-_+________-_+__________-+_________+_________-+________-_+
TEEN
- 1.21E-06 : 1.06E-06 : 3.23E-07 : 1.43E-06 : 1.70E-06 : 1.22E-04 : 9.80E-07 : 9.75E-07
_____-___+_-________+________-_+_________-+__________+-_________+__________+_________-+________-_+
CHILD
- 1.50E-06 : 1.23E-06 : 5.98E-07 : 1.78E-06 : 2.10E-06 : 1.84E-04 : 1.19E-06 : 1.18E-06
______-__+_-________+________-_+_________-+__________+__________+_________-+________-_+________-_+
IV-39
0 TABLE IV-A-36 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
36 BEEF AT 3.25 MILES W ANNUAL BETAAIR DOSE = 1.05E-02 MILLRADS ANNUALGAMMAAIR_DOSE = 2.84E-03 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
_______-_+-_________+________-_+__________+__________+__________+__________+____---+____+___--___+
PLUME
- 1.65E-03 : 1.65E-03 : 1.65E-03 : 1.65E-03 : 1.65E-03 : 1.65E-03 : 1.76E-03 : 6.19E-03
+__________+______--+ -
__+
-_________+__________+__________+__________--+-+
-+-
+ -____
+
GROUND
- 6.19E-07 : 6.19E-07 : 6.19E-07 : 6.19E-07 : 6.19E-07 : 6.19E-07 : 6.19E-07 : 7.36E-07
_________+__________+__________+__________+__________+__________+__________+__________+__________+
MEAT ADULT 9.21E-07 8.21E-07 2.06E-07 1.04E-06 1.22E-06 8.94E-05 7.52E-07 7.49E-07
_________+-_________+_______-__+_______-__+_________-+________-_+________-_+_______-__+________-_+
TEEN
- 5.72E-07 : 4.90E-07 : 1.71E-07 : 6.86E-07 : 8.32E-07 : 6.47E-05 : 4.49E-07 : 4.46E-07
_________+______-___+________-_+________-_+_________-+________-_+________-_+________-_+________-_+
CHILD
- 7.11E-07 : 5.67E-07 : 3.18E-07 : 8.60E-07 : 1.03E-06 : 9.75E-05 : 5.44E-07 : 5.41E-07
_____-___+-_________+________-_+________-_+________-_+_________-+__________+__________+_________-+
IV-40
TABLE IV-A-37 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
37 BEEF AT 2.74 MILES WNW ANNUAL BETAAIRDOSE = 4.13E-02 MILLRADS ANNUALGAMMAAIRDOSE = 1.11E-02 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
__---+_____
+____
+___
_+___
_+__
__+_---________-+____-_
+
PLUME
- 6.48E-03 : 6.48E-03 : 6.48E-03 : 6.48E-03 : 6.48E-03 : 6.48E-03 : 6.89E-03 : 2.43E-02
__---+_____
+____
+___
_+___
_+__
__+_--+-________-+___-_
+
GROUND
- 1.67E-06 : 1.67E-06 : 1.67E-06 : 1.67E-06 : 1.67E-06 1.67E-06 : 1.67E-06 : 1.99E-06
__---+____
+___
_+_
___+
___---______+____- _____
+_______--I--_
+
MEAT ADULT 3.39E-06 3.12E-06 5.58E-07 3.73E-06 4.20E-06 2.43E-04 2.94E-06 2.93E-06
__---+_____
+____
+___
_+___
_+__
__+_---________+-+___-_
+
TEEN
- 2.08E-06 : 1.86E-06 : 4.63E-07 : 2.39E-06 : 2.79E-06 : 1.75E-04 : 1.75E-06 : 1.74E-06
_____-___+_-___-____+_________-+_________-+________-_+________-_+_______-__+________-_+________-_+
CHILD
- 2.57E-06 : 2.18E-06 : 8.59E-07 : 2.98E-06 : 3.44E-06 : 2.64E-04 : 2.12E-06 : 2.11E-06
_____-___+_-________+_________-+_________-+_________-+__________+__________+__________+_________-+
IV-41
TABLE IV-A-38 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
38 COW AT 2.77 MILES S ANNUALBETAAIR DOSE = 1.79E-02 MILLRADS ANNUALGAMMAAIRDOSE = 4.80E-03 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
______-__+-_________+________-_+_________-+__________+__________+__________+__________+_________-+
PLUME
- 2.79E-03 : 2.79E-03 : 2.79E-03 : 2.79E-03 : 2.79E-03 : 2.79E-03 : 2.97E-03 : 1.05E-02
_________+-_________+_______-__+_________-+__________+________--+________-_+_______-__+________-_+
GROUND
- 1.25E-06 ; 1.25E-06 : 1.25E-06 : 1.25E-0G : 1.25E-06 : 1.25E-06 : 1.25E-06 : 1.49E-06
_________+__________+__________+__________+__________+__________+__________+__________+__________+
COW MILK:
ADULT
- 7.55E-06 5.02E-06 : 5.47E-06 1.09E-05 : 1.60E-05 2.47E-03 3.07E-06 : 3.03E-06
_________+______-___+________-_+________-_+________-_+________-_+________-_+________-_+________-_+
TEEN
- 1.13E-05 : 6.60E-06 : 9.92E-06 : 1.78E-05 : 2.71E-05 : 3.90E-03 : 4.02E-06 : 3.95E-06
_________+______-___+________-_+________-_+_______-__+________-_+________-_+________-_+________-_+
CHILD
- 1.96E-05 : 8.33E-06 : 2.41E-05 : 3.05E-05 : 4.47E-05 : 7.70E-03 : 6.36E-06 : 6.25E-06
_________+-_________+_______-__+________-_+________-_+________-_+________-_+________-_+________-_+
INFANT : 3.46E-05 : 1.15E-05 : 4.98E-05 : 6.82E-05 : 7.64E-05 : 1.87E-02 : 9.68E-06 : 9.49E-06
______-__+-_________+_________-+_________-+________-_+________-_+________-_+________-_+________-_+
IV-42
TABLE IV-A-39 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS SPECIAL LOCATION NO.
39 GOAT AT 0.65 MILES SSW ANNUALBETAAIRDOSE = 4.86E-01 MILLRADS ANNUALGAMMAAIRDOSE = 1.31E-01 MILLRADS PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
__---+_____
+____
+___
_+___
_+__
__+_---________-+
+
PLUME
- 7.65E-02 : 7.65E-02 : 7.65E-02 : 7.65E-02 : 7.65E-02 : 7.65E-02 : 8.13E-02 : 2.86E-01
__---+_____
+____
+___
_+___
_+__
__+_---________-+
+
GROUND
- 2.48E-05 : 2.48E-05 : 2.48E-05 : 2.48E-05 : 2.48E-05 : 2.48E-05 : 2.48E-05 : 2.95E-05
_________+__________+__________+__________+__________+__________+__________+__________+__________+
GOATMILK :
ADULT
- 3.88E-04 2.60E-04 2.69E-04 5.50E-04 7.89E-04 1.18E-01 1.68E-04 1.65E-04
__---+_____
____+
____+
___+
___+_
___+_
__+_---+-______-+
_ +
TEEN
- 5.74E-04 : 3.42E-04 : 4.87E-04 : 8.97E-04 : 1.33E-03 : 1.86E-01 : 2.21E-04 : 2.15E-04
__---+_____
+____
+___
_+___
_+__
__+_---________+-+
_ +
CHILD
- 9.84E-04 : 4.40E-04 : 1.18E-03 : 1.53E-03 : 2.19E-03 : 3.68E-01 : 3.49E-04 : 3.40E-04
__---+_____
____+
____+
___+
___+_
___+_
__+_---________+-+
_ +
INFANT : 1.72E-03 : 6.14E-04 : 2.43E-03 : 3.38E-03 : 3.73E-03 : 8.94E-01 : 5.32E-04 : 5.16E-04
__---+_____
+____
+___
_+___
_+__
__+_---________-+____-_
+
IV-43
TABLE IV-B-1 FORT CALHOUN 1 DOSE CONTRIBUTIONS FROM GASEOUS EFFLUENTS UNRESTRICTED AREA BOUNDARY REQUIRED BY TECHNICAL SPECIFICATION 5.9.4.a.
ANNUAL FOR JANUARY 1, 2001 TO DECEMBER 31, 2001 MAXIMUM SITE BOUNDARY GAMMA AIR DOSE -
MAXIMUM SITE BOUNDARY BETA AIR DOSE -
3.24E-01 MILLRADS 1.19E+00 MILLRADS IV-44
TABLE IV-C-1 FORT CALHOUN ANNUAL 2001, DOSE PROJECTIONS ALARA ANNUAL INTEGRATED POPULATION DOSE
SUMMARY
(PERSON-REM)
PATHWAY T.BODY GI-TRACT BONE LIVER KIDNEY THYROID LUNG SKIN
______-__+_-________+__________+_________-+________-_+________-_+_________-+__________+________--+
PLUME 1.60E-01 : 1.60E-01 : 1.60E-01 : 1.60E-01 1.60E-01 : 1.60E-01 : 1.75E-01 7.67E-01 99.28% :
99.37%
99.78% :
99.18% :
99.03%
57.68% :
99.46% :
99.88%
____-____+_-_______+________--_+__________+__________+__________+__________+__---+-___-+__-______+
GROUND 4.43E-05 4.43E-05 : 4.43E-05 : 4.43E-05 : 4.43E-05 4.43E-05 : 4.43E-05 : 5.27E-05 0.03% :
0.03% :
0.03%;
0.03% :
0.03%
0.02% :
0.03% :
0.01%
_____-___+_-________+_________-+_________-+________-_+_______-__+________-_+________-_+________-_+
INHAL 4.54E-04 4.18E-04 6.63E-05 4.91E-04 : 5.50E-04 2.85E-02 4.05E-04 : 4.05E-04 0.28% :
0.26% :
0.04% :
0.30% :
0.34%
10.23%
0.23% :
0.05%
_____-___+_--_______+________+_________-+_______-__+__________+__________+_____--____-+__-_______+
VEGET
- 3.55E-04 3.47E-04 : 1.52E-05 3.65E-04 : 3.59E-04 : 2.OOE-03 3.48E-04 : 3.46E-04 0.22%
0.22% :
0.01% :
0.23% :
0.22%
0.72%
0.20% :
0.05%
_____-___+_-________+_________-+_________-+_________-+-_________+__________+_________-+_______-__+
COW MILK : 2.19E-04 : 1.20E-04 : 2.13E-04 : 3.32E-04 : 4.94E-04 : 7.98E-02 7.77E-05 : 7.68E-05 0.14% :
0.07%
0.13%
0.20%
0.31%
28.69% :
0.04% :
0.01%
_________+_________+__________+____---____+__-_____+__________+__________+_______--___-+-________+
MEAT 9.20E-05 : 8.31E-05 : 1.87E-05 : 1.03E-04 : 1.17E-04 7.42E-03 : 7.83E-05 : 7.80E-05 0.06%:
0.05%:
0.01%:
0.06%:
0.07%:
2.67% :
0.04% :
0.01%:
_____-___+_-________+_________-+________-_+________-_+________-_+________-_+_______-__+________-_+
- TOTAL*
- 1.62E-01 : 1.61E-01 : 1.61E-01 : 1.62E-01 : 1.62E-01 : 2.78E-01 : 1.76E-01 : 7.68E-01
_____-___+_-________+_________-+_________-+________-_+_________-+________-_+_________-+________-_+
IV-45
SECTION VII ATTACHMENT I ODCM and PCP revisions for the period January 1, 2001 through December 31, 2001 in accordance with Technical Specification 5.17d and 5.18d, the radioactive effluent release report shall include any revisions to the Offsite Dose Calculation Manual (ODCM) and the Process Control Program (PCP).
0 revisions were made to the Offsite Dose Calculation Manual (ODCM).
1 revisions were made to the Process Control Program (PCP).
January 1, 2001 - December 31, 2001 VII-1
WP8 Fort Calhoun Station Unit No. 1 RW-200 RADIATION PROTECTION
Title:
PROCESS CONTROL PROGRAM FC-68 Number:
EC 27167 Reason for Change:
Requestor:
Preparer:
Changes due to new 50.59 rule change.
Anne Lollis Anne Lollis ISSUED:
06-01-01 3:00 pmr R4
FORT CALHOUN STATION RW-200 RADIATION PROTECTION PAGE 1 OF 14 PROCESS CONTROL PROGRAM
- 1. PURPOSE To provide guidance and boundary conditions for preparation of specific procedures for processing, sampling, analyzing, packaging and shipping solid radioactive waste in accordance with State and Federal regulatory requirements.
This program is applicable to the Fort Calhoun Station Unit No. 1 solid radwaste system.
Wastes considered in this program are primary and radwaste liquid processing resins, oil and filters. Dry Active Waste is only included as it applies to assurance that packaged waste is suitable for shipment and burial in accordance with applicable State and Federal regulations. Concentrates and aqueous liquids are not considered due to the present decisions not to utilize the waste evaporator as a means for processing liquid wastes.
- 2. RESPONSIBILITIES 2.1 The Supervisor-Radioactive Waste Operations is responsible for:
2.1.1 Maintenance of and compliance with this Process Control Program; 2.1.2 Record keeping and document control of shipping and processing data; and 2.1.3 Assuring Radwaste Personnel are appropriately trained and qualified to perform waste processing and packaging activities.
2.2 The Supervisor-Operations is responsible for:
2.2.1 Providing trained personnel to operate appropriate radwaste process equipment; and 2.2.2 Defining those Operations positions which require training.
2.3 The Manager Training is responsible for:
2.3.1 Development and implementation of performance-based training for designated personnel in accordance with Training Division procedures.
2.4 All OPPD and OPPD contract personnel are responsible for:
2.4.1 Implementation of procedures and good practices so as to provide Quality Assurance and maintain exposures ALARA.
R4
FORT CALHOUN STATION RW-200 RADIATION PROTECTION PAGE 2 OF 14 2.5 The Nuclear Quality Assurance Department is responsible for:
2.5.1 Establishment of a Quality Assurance Program addressing Radwaste processing and packaging; and 2.5.2 Performing audits of activities associated with this Process Control Program to assure compliance with the Quality Assurance Plan.
2.6 The Plant Review Committee is responsible for:
2.6.1 Reviewing and approving changes to this Process Control Program prior to implementation of the changes; and 2.6.2 Reviewing and approving engineering and 50.59 reviews performed in support of changes to this Process Control Program.
2.7 The Station Engineering Manager is responsible for:
2.7.1 Ensuring engineering and 50.59 reviews are performed for changes made to this Process Control Program; and 2.7.2 Submitting these reviews to the Plant Review Committee for review and approval prior to implementation of the changes evaluated.
- 3. DEFINITIONS 3.1 Batch - An isolated quantity of feed waste to be processed having essentially constant physical and chemical characteristics. For the purpose of resin type wastes a batch is defined as the volume of resins in the Spent Resin Storage Tank or in a vendor supplied system intended to process a quantity of feed waste.
3.2 Operable - A system, subsystem, train, component or device shall be OPERABLE or have OPERABILITY when it is capable of performing its specified function(s), and when all necessary attendant instrumentation, controls, electrical power, cooling or seal water, lubrication or other auxiliary equipment that are required for the system, subsystem, train, component, or device to perform its function(s) are also capable of performing their related support function(s).
3.3 ProcessinQ - Changing, modifying, and/or packaging plant generated radioactive waste into a form that is acceptable to a disposal facility.
R4
FORT CALHOUN STATION RW-200 RADIATION PROTECTION PAGE 3 OF 14 3.4 Quality Assurance/Quality Control - As used in this document, "quality assurance" comprises those planned and systematic actions necessary to provide adequate confidence that a structure, system, or component will perform satisfactorily in service. Quality assurance includes quality control, which comprises those quality assurance actions related to the physical characteristics of a material, structure, component, or system which provide a means to control the quality of the material, structure, component, or system to predetermined requirements.
3.5 Samrpling Plan - A sampling program implemented to ensure that representative samples from the feed waste and the final waste form are obtained and tested for conformance with parameters stated in the Process Control Program and waste form acceptance criteria.
3.6 Low-Level Radioactive Waste (LLW) -Those low-level radioactive wastes containing source, special nuclear, or by-product material that are acceptable for disposal in a land disposal facility. For the purposes of this definition, low-level radioactive waste has the same meaning as in the Low-Level Waste policy Act, that is radioactive waste not classified as high-level radioactive waste, transuranic waste, spent nuclear fuel, or by-product material as defined in Section 1 1e.(2) of the Atomic Energy Act (uranium or thorium tailings and waste).
3.7 Waste Container - A vessel of any shape, size, and composition used to contain the final processed waste.
3.8 Waste Form - Waste in a waste container acceptable for disposal at a licensed disposal facility.
3.9 Stability -As used in this program, STABILITY means structural stability. Stability requires that the waste form maintain its structural integrity under the expected disposal conditions.
3.10 Chelating Agent - For the purpose of this program CHELATING AGENTS are amine polycarboxylic acids (e.g., EDTA, DTPA), hydroxy-carboxylic acids, and polycarboxylic acids (e.g., citric acid, carbolic acid, picolanic acid and gluconic acid ) as defined in 1 OCFR61.2.
- 4. APPARATUS None
- 5. PREREQUISITES 5.1 All personnel performing activities under the control of and described by this Process Control Program shall have been successfully trained and qualified to perform the described activities before actually performing the activities.
R4
FORT CALHOUN STATION RW-200 RADIATION PROTECTION PAGE 4 OF 14 5.2 Procedures shall have been developed for implementation of this Process Control Program and shall be reviewed and approved by the Plant Review Committee prior to performing activities described and required by this Process Control Program.
- 6. PRECAUTIONS None
- 7. PROCEDURE 7.1 WASTE TYPES 7.1.1 Primary Resin A.
The contaminated waste product generated as a result of reactor water purification and demineralization, cation ion exchange, deborating ion exchange and spent fuel pool demineralization.
B. Waste consists of contaminated bead ion exchange resins at varying degrees of exhaustion, small concentrations of various solids, activated and non-activated corrosion products and fission products.
7.1.2 Radwaste Liquid Processing Resin A. The contaminated waste product generated as a result of processing radwaste liquids using a demineralization system. This system may be vendor supplied.
B. Waste consists of contaminated bead ion exchange resins at varying degrees of exhaustion, small concentrations of various solids, activated and non-activated corrosion products and fission products.
7.1.3 Filters A. The contaminated waste product generated as a result of liquid processing activities and the removal of cartridge elements from the processing systems.
B. Waste consists of contaminated mechanical filtration cartridges containing various amounts of particulate solids, corrosion products, activation and fission products.
R4
FORT CALHOUN STATION RW-200 RADIATION PROTECTION PAGE 5 OF 14 7.1.4 Oil A. The contaminated waste product generated as a result of leakage or intentional drainage and replacement of various plant component lubricating and/or control fluids.
B. Waste consists of contaminated oils and greases of various grades both synthetic and natural, in free form or containing various amounts of solid material.
7.1.5 Dry Active Waste A.
The contaminated waste product generated as a result of plant maintenance and repair and routine plant operations.
B. Waste generally consists of contaminated trash in the form of plastics, papers, wood, steel and cloth items with varying concentrations of corrosion, activation and fission products.
7.1.6 Non-Standard Wastes A.
The contaminated waste product generated as a result of non-routine plant operation, maintenance and or repair activities.
B. Waste consists of plant components, irradiated hardware and other specialty items contaminated with varying concentrations of corrosion, activation and fission products. The waste may also be those items which have become activated with contamination being a minimal fraction of the total radioactivity.
7.2 PROCESS DESCRIPTION 7.2.1 Primary Resin A.
Primary resins are obtained from the demineralizer filtration system, purification ion exchangers, the cation ion exchanger, the deborating ion exchanger and the spent fuel storage pool demineralizer.
B. The resins from the demineralizer filtration system are sluiced into a container for processing and shipment from the plant.
C. The resins from other sources and their sluice water are collected in the spent resin storage tank.
R4
FORT CALHOUN STATION RW-200 RADIATION PROTECTION PAGE 6 OF 14 7.2.1 D. The contents of the spent resin storage tank are recirculated with sufficient liquid to keep resin flowing. Nitrogen gas is used to break up solid chunks during this recirculation process.
E. The contents of the tank are pumped into a disposable container within a shielded shipping cask or process shield after which the contents are processed and shipped from the plant.
F. Due to the infrequent need to dispose of spent primary resins (approximately every 2-3 years) the most efficient method of disposal is to use a vendor supplied processing system. A NRC approved container (e.g. high Integrity Container or HIC) or solidification process shall provide the required stability.
7.2.2 Radwaste Liquid Processing Resin A.
Radwaste liquids are processed using a demineralization system in lieu of using the installed plant evaporator system.
B. Radioactive liquids are normally transferred from the waste holdup tanks to the demineralization system using the waste holdup transfer pumps.
Specific maintenance and/or decontamination activities may require the use of portable transfer pumps and hoses.
C. The processed liquids are directed to the monitor tanks to be analyzed and discharged to the Missouri River through the overboard discharge piping.
D. The depleted resins in the demineralization system vessels are sluiced from the demineralizer vessels into a container which will provide the required stability either through design (HIC) or by solidification.
E. Multiple sluices may be performed to fill the container.
F. Once the container is filled, processed and stabilized; the waste will be shipped for disposal.
7.2.3 Filters A.
Used filter cartridges originate from the purification filters, the waste filters, the spent fuel pool cooling system filter, ultrasonic cleaning unit, laundry machines and various other decontamination equipment.
B. Filters are removed from their respective system and permitted to drain excess liquids from the elements.
R4
FORT CALHOUN STATION RW-200 RADIATION PROTECTION PAGE 7 OF 14 7.2.3 C. The filters are then transferred in a container for disposal.
- 1) When stabilization is required, (i.e. Class B or C) the filters shall be disposed of in a HIC or shall be solidified.
7.2.4 Oil A.
Oil generated during operation and maintenance is collected in containers in appropriate approved areas of the plant.
B. The filled and labeled containers are sealed and moved to available areas for temporary storage.
C. Oils may be shipped off site to a contracted and licensed vendor for processing or incineration.
7.2.5 Dry Active Waste A.
Dry Active Wastes are collected from radiologically controlled areas throughout the plant.
B. The waste is sorted to remove reusable and wet items.
C. The contaminated waste material is then either compacted into metal 55 gallon drums in the waste baler, packaged in metal boxes, or placed into a seal/land container for shipment to a process facility. Contaminated waste will be disposed of by an approved burial site or processed (e.g.
incinerated, etc.) by an approved vendor.
7.2.6 Non-Standard Waste A.
Reactor components and irradiated hardware are waste which are not routinely generated.
B. These types of non-standard waste will be handled on a case-by-case basis through the implementation of special procedures approved by the Plant Review Committee.
7.3 PROCESS CONTROL 7.3.1 Radioactive waste processing instrumentation and equipment shall be subject to formal calibration and preventative maintenance programs.
R4
FORT CALHOUN STATION RW-200 RADIATION PROTECTION PAGE 8 OF 14 7.3.2 Primary and Radwaste Liquid Processing Resin A.
Primary resins will be transferred into containers for processing using plant installed and vendor supplied equipment.
B. Radwaste Liquid Processing will be performed using a vendor supplied system with transfer of depleted resins from the demineralizer vessels into a processing container by means of sluicing.
C. Primary and Radwaste Liquid Processing Resin dewatering will be performed using an NRC and PRC approved Process Control Program.
D. Referenced Radwaste Procedures controlling the processing, transfer and dewatering activities shall be observed.
E. The Process Control Program which specifically controls processing of the waste (i.e. the vendors PCP) shall identify the mechanisms and frequency of test/measurements used to verify stability and free standing liquid requirements are satisfied.
F. Successful completion of applicable portions of the vendor Process Control Program shall serve as an indicator of system operability.
G. Containers used for dewatering and packaging for disposal at the Barnwell disposal facility shall be approved for use and disposal by the South Carolina Department of Health and Environmental Control.
H. The vendor supplied system shall be operated in accordance with the system operating procedures and applicable station Radwaste Procedures.
I.
Station to vendor interfacing is addressed in the safety assessment for the processing and dewatering operations.
7.3.3 Filters A.
Filter processing is controlled by referenced Radwaste Procedures.
B. Filters requiring stability are packaged as described in Section 7.2.3.
The containers and/or process used shall be approved by the South Carolina Department of Health and Control.
R4
FORT CALHOUN STATION RW-200 RADIATION PROTECTION PAGE 9 OF 14 7.3.4 Oil A.
Processing of oil shall be performed in accordance with referenced Radwaste Procedures and applicable vendor procedures and topical reports for the methodology applied to the processing activity.
7.3.5 Dry Active Waste A.
Dry Active Waste is processed in accordance with referenced Radwaste Procedures.
7.3.6 Non-Standard Waste A. Non-Standard Waste is processed in accordance with special Radwaste Procedures germane to the specific non-standard waste being processed.
7.4 PRODUCT CONTROL 7.4.1 A sample from each batch of waste shall be analyzed quantitatively for activity and isotopic identity as required in station procedures. If radionuclide distributions are shown to be consistent between similar batches, consideration may be given to decreasing the frequency of routine measurements. Frequency of sampling is as described in Radiation Protection Procedure RW-221, "10CFR61 Sampling". This constitutes the sampling plan.
7.4.2 Scaling factors for nuclides which are hard to identify are established for waste streams by using analyses performed and provided by an off-site vendor.
7.4.3 This frequency of sampling shall be raised or lowered based upon consideration of waste stream or radionuclide characteristics. Factors which would influence this consideration include the frequency of process vessel changeout or waste shipment, the difficulty (e.g. Costs, occupational exposures) in obtaining a representative sample of a particular waste stream, the variability of the radionuclide distribution within the waste stream over time, and the availability of analytical capability for particular radionuclides. If radionuclide distributions are shown to be consistent between similar batches, consideration may be given to decreasing the frequency of routine measurements. If onsite samples show a variation from presently used scaling factors by more than a factor of 10, samples will be sent offsite for analysis to establish new scaling factors.
R4
FORT CALHOUN STATION RW-200 RADIATION PROTECTION PAGE 10 OF 14 7.4.4 Radionuclide concentrations and classification of future waste shipments are expected to be similar to those of previous shipments for each specific waste stream. Values are available from shipment manifest forms.
7.4.5 Administrative controls for preventing unsatisfactory waste forms from being released for shipment are described in referenced station procedures.
7.4.6 Referenced Radwaste Procedures ensure wastes shall have no detectable free standing liquids. No detectable free standing liquid is defined as low as practical but not more than 1 % of the volume of the waste when the waste is in a disposable container designed to ensure stability or not more than 0.5%
of the volume of the waste for waste processed in any other container.
7.4.7 Processed resin shall be sampled in accordance with regulatory guidance and referenced station procedures to verify that the free liquid content of the packaged product is within limits established by applicable regulatory agencies. Sampling and measurement of free liquid content shall be performed whenever process changes occur that may significantly alter system performance, until compliance with moisture content limits under these conditions can be demonstrated.
7.4.8 Each waste shipment shall be accompanied by a shipping manifest giving a physical description of the waste, the volume, the radionuclide identity and quantity, the total radioactivity, the principal chemical form and waste class, based on 10CFR61.55.
7.4.9 Sufficient analysis shall be performed to verify that the quality of waste forms prepared for disposal by vendor's onsite processing shall be similar to vendor's test results.
7.5 TRAINING 7.5.1 Processing of solid radioactive waste shall be performed by qualified and trained personnel.
7.5.2 Training records of processing personnel shall be maintained by the Training Division.
7.5.3 Training and qualification records for operators of mobile vendor processing units shall be maintained by the Supervisor-Radioactive Waste Operations while the vendor is active on site. These records shall be sent to the Nuclear Records Management System after the vendor has completed work on site.
R4
FORT CALHOUN STATION RW-200 RADIATION PROTECTION PAGE 11 OF 14 7.6 PROCEDURE CONTROL 7.6.1 On site processing of radioactive waste shall be performed in accordance with approved station procedures.
7.6.2 Processing of radioactive waste by onsite vendors shall be performed in accordance with applicable Process Control Programs, procedures and applicable NRC guidance.
7.6.3 Procedures for processing, containerization and transport of wastes shall ensure that specific DOT, 10CFR and burial site requirements are satisfied.
7.6.4 Process Control Programs for specific radwaste systems supplied by vendors for on site processing shall be presented to the Plant Review Committee for review and approval prior to use of the system.
7.7 RECORDS 7.7.1 Waste classification records, waste form records and other records required for the preparation of the Fort Calhoun Station Unit No. 1 Annual Radioactive Effluent Release Report shall be prepared and retained in accordance with the requirements of 10CFR20, 10CFR71, 49CFR1 70-178 and the Fort Calhoun Station Technical Specifications.
7.7.2 Records of processing data, test and analysis results and results of training, inspection and audits are retained in accordance with the Fort Calhoun Station Quality Assurance Plan and applicable station Administrative Procedures.
7.7.3 All certificates of compliance, licenses, criteria and regulations pertaining to processing, packaging, shipment and disposal of radioactive materials controlled under this Process Control Program shall be maintained in the most current status. OPPD, Fort Calhoun Station Unit No. 1 shall be currently registered, as necessary, to use applicable packagings.
7.7.4 Sufficient documentation shall be maintained to demonstrate compliance of solid radwaste processing with this Process Control Program.
7.8 QUALITY ASSURANCE 7.8.1 Quality Assurance shall be maintained as defined by the Fort Calhoun Station Quality Assurance Plan, Section 11.
7.8.2 The QA Plan shall ensure compliance with NRC and burial site criteria for waste classification and waste form.
R4
FORT CALHOUN STATION RW-200 RADIATION PROTECTION PAGE 12 OF 14 7.8.3 Audits shall be conducted in accordance with NQA Audit Section Instructions.
7.8.4 The Topical Reports of vendor supplied radwaste processing systems shall undergo review either by the Supervisor-Radioactive Waste Operations or the Manager-Radiation Protection. The review shall ensure the vendor supplied system will be compatible with plant operations and that the Topical report has been submitted to the NRC for review. The review shall be documented by a memo addressed to file.
7.8.5 Audits of a sampling of implementing procedures shall be performed at least once every 24 months. Procedures should be reviewed to ensure continual compliance with the requirements and process parameters of this Process Control Program.
7.8.6 Radioactive wastes not described within this document must be evaluated and approved for inclusion in this Process Control Program or in a vendor Process Control Program prior to processing.
7.9 REVISIONS 7.9.1 Changes or modifications made to design and/or operation of radioactive waste processing, treatment and/or packaging systems or activities, as described within this Process Control Program, shall require formal engineering evaluation and performance of a 50.59 review in accordance with 10CFR50.59 and USNRC IE Circular No. 80-18.
7.9.2 Changes made to this Process Control Program and supporting engineering and 50.59 reviews shall be reviewed and approved by the Plant review Committee prior to implementing the changes.
7.9.3 Changes to the Process Control Program approved by the Plant Review Committee shall be submitted to the Nuclear Engineer-In-Charge of Licensing, for input to the Annual Radioactive Effluent Release Report.
- 8. REFERENCES/COMMITMENT DOCUMENTS 8.1 RW-201, Control of Containers 8.2 RW-202, Collection/Sorting/Segregation of Dry Active Waste (DAW) 8.3 RW-203, Compacting Dry Active Waste (DAW) 8.4 RW-204, Packaging Non-Compactable Dry Active Waste R4
FORT CALHOUN STATION RW-200 RADIATION PROTECTION PAGE 13 OF 14 8.5 RW-206, Transfer of Spent Primary Resin to Disposal Containers 8.6 RW-207, Operation of the Fix Radwaste Liquid Processing System 8.7 RW-208, Transfer of Spent Fix System Resin to Disposal Containers 8.8 RW-209, Dewatering Spent Radwaste Liquid Processing Resin and Primary Resin In Disposal Containers 8.9 RW-21 1, Storage of Filters From Radwaste Systems 8.10 RW-212, Loading HIC Overpacks 8.11 RW-214, Collection Of Oils 8.12 RW-215, Processing of Contaminated Oils 8.13 RW-216, Testing of Sorbent Materials 8.14 RW-218, I0CFR61 Classification 8.15 RW-221, 10CFR61 Sampling 8.16 49CFR Parts 170 through 178 8.17 10CFR Parts 20, 50, 61, and 71 8.18 USNRC IE Circular No. 80-18 8.19 USNRC Low Level Waste Licensing Branch; Technical Position on Radioactive Waste Classification, Current Revision 8.20 USNRC Low Level Waste Licensing Branch; Technical Position on Waste Form, Current Revision 8.21 South Carolina Department of Health and Environmental Control Radioactive Material License No. 097, Current Revision 8.22 Bamwell Special Nuclear Material License No. 12-13536-01, issued to Chem-Nuclear Systems, Inc.
8.23 Barnwell Site Disposal Criteria, (Chem-Nuclear Systems, Inc.) November 1982 8.24 Current Vendor Processing Topical Report R4
FORT CALHOUN STATION RW-200 RADIATION PROTECTION PAGE 14 OF 14 8.25 Current Vendor Operating Procedures as referenced in RW-207 8.26 FCS Quality Assurance Plan, Section 11.1 and 11.2 8.27 Fort Calhoun Station Unit No. 1, Updated Safety Analysis Report 8.28 Fort Calhoun Station Unit No. 1 Technical Specifications Sections 5.18 and 5.9.4
- 9. ATTACHMENTS None R4
Omaha Public Power District Fort Calhoun Nuclear Station JOINT FREQUENCY DISTRIBUTION BY EVENTS EXTREMELY UNSTABLE (delta T/ delta z < -1.9)
PERIOD OF RECORD:
JAN 2001 -
DEC 2001 PASQUILL A WIND SPEED (mph) AT 10-m LEVEL Wind 1.0-4.0-8.0-13.0-19.0-Direct 3.9 7.9 12.9 18.9 24.0
+24.0 Total N
NNE NE ENE E
WNW NW NNW 6
3 2
9 4
2 3
0 3
4 5
5 1
2 5
8 14 7
9 24 12 7
15 8
14 12 26 11 4
15 22 40 11 4
2 2
6 8
12 23 25 16 12 2
1 9
41 30 1
0 0
0 0
4 9
16 3 0 12 2
0 1
11 11 6
0 0
0 0
0 0
0 0
4 5
0 0
0 0
0 0
0 0
0 0
0 0
0 0
4 1
0 0
0 0
0 0
32 14 13 35 22 21 39 47 80 50 45 18 7
37 79 84 Total 62 240 204 103 9
Number of Calms 0
Number of Invalid Hours 0
Number of Valid Hours 623 5
623 VII-4
Omaha Public Power District Fort Calhoun Nuclear Station JOINT FREQUENCY DISTRIBUTION BY EVENTS MODERATELY UNSTABLE (-1.9 <= delta T/ delta z <= -1.7)
PERIOD OF RECORD:
JAN 2001 -
DEC 2001 PASQUILL B WIND SPEED (mph) AT 10-m LEVEL Wind 1.0-4.0-8.0-13.0-19.0-Direct 3.9 7.9 12.9 18.9 24.0
+24.0 Total N
NNE NE ENE E
WNW NT NNW Total 8
2 8
4 0
4 4
3 4
3 5
2 2
3 12 6
32 9
13 4
7 6
5 5
11 12 9
6 4
7 32 38 8
1 1
4 8
7 15 13 20 8
5 1
3 10 12 36 2
0 0
0 0
1 4
15 22 22 2
1 0
0 2
1 0
0 0
0 0
0 0
2 4
5 0
0 0
0 0
0 0
0 0
0 0
0 1
0 0
0 0
0 0
0 0
0 50 12 22 12 15 18 29 38 61 50 21 10 9
20 59 81 70 200 152 72 11 1
506 Number of Calms 1
Number of Invalid Hours 0
Number of Valid Hours 507 VII-5
Omaha Public Power District Fort Calhoun Nuclear Station JOINT FREQUENCY DISTRIBUTION BY EVENTS SLIGHTLY UNSTABLE (-1.7 < delta T/ delta z <= -1.5)
PERIOD OF RECORD:
JAN 2001 -
DEC 2001 PASQUILL C WIND SPEED (mph) AT 10-m LEVEL Wind 1.0-4.0-8.0-13.0-19.0-Direct 3.9 7.9 12.9 18.9 24.0
+24.0 Total N
NNE NE ENE E
WNW NW NNW 13 4
5 3
1 4
1 4
0 0
1 1
2 4
5 9
34 9
6 16 3
6 5
11 11 10 13 6
6 6
18 42 11 2
2 3
10 16 10 11 23 9
8 3
1 11 25 33 1
0 0
0 0
1 6
14 12 8
3 2
1 2
3 4
0 0
0 0
0 0
0 2
5 2
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
59 15 13 22 14 27 22 42 51 29 25 12 10 23 51 89 Total 57 202 178 57 9
0 503 Number of Calms 1
Number of Invalid Hours 0
Number of Valid Hours 504 VII-6
I - S I
I Omaha Public Power District Fort Calhoun Nuclear Station JOINT FREQUENCY DISTRIBUTION BY EVENTS NEUTRAL (-1.5 < delta T/ delta z <= -0.5)
PERIOD OF RECORD:
JAN 2001 -
DEC 2001 PASQUILL D WIND SPEED (mph) AT 10-m LEVEL Wind 1.0-4.0-8.0-13.0-19.0-Direct 3.9 7.9 12.9 18.9 24.0
+24.0 Total N
NNE NE ENE E
WNW NW NNW 62 45 31 35 35 29 21 21 12 14 28 19 19 26 38 66 112 39 41 63 74 88 102 74 64 68 49 26 21 69 212 272 43 14 10 22 58 78 98 142 152 67 34 5
9 44 141 166 1
1 0
0 2
13 35 ill 113 53 24 4
2 13 26 26 0
0 0
0 0
0 6
9 8
10 6
3 1
0 0
0 0
0 0
0 0
0 0
1 1
0 2
1 0
0 0
0 218 99 83 120 170 208 262 358 350 212 143 58 52 152 417 530 Total_____501____1374____1083_____424___43___5___3430__
Total 501 1374 1083 424 43 5
3430 Number of Calms 2
Number of Invalid Hours 0
Number of Valid Hours 3432 VII-7
Omaha Public Power District Fort Calhoun Nuclear Station JOINT FREQUENCY DISTRIBUTION BY EVENTS SLIGHTLY STABLE (-0.5 < delta T/ delta z <= 1.5)
PERIOD OF RECORD:
JAN 2001 -
DEC 2001 PASQUILL E WIND SPEED (mph) AT 10-m LEVEL Wind 1.0-4.0-8.0-13.0-19.0-Direct 3.9 7.9 12.9 18.9 24.0
+24.0 Total N
NNE NE ENE E
WNW NW NNW 53 25 19 32 32 63 45 44 30 29 42 35 56 98 86 80 16 7
6 9
29 100 147 109 91 40 20 13 35 80 98 64 2
3 4
2 5
11 49 151 150 77 36 15 10 12 16 13 2
0 0
1 0
0 3
22 45 44 33 1
0 0
1 3
0 0
0 0
0 0
0 1
4 4
3 0
0 0
0 0
0 0
0 0
0 0
0 0
1 1
1 0
0 0
0 0
73 35 30 44 68 174 245 328 322 195 135 67 101 192 202 160 Total 769 864 556 155 12 3
2359 Number of Calms 12 Number of Invalid Hours 0
Number of Valid Hours 2371 VII-8
I-Omaha Public Power District Fort Calhoun Nuclear Station JOINT FREQUENCY DISTRIBUTION BY EVENTS MODERATELY STABLE (1.5 < delta T/ delta z <= 4.0)
PERIOD OF RECORD:
JAN 2001 -
DEC 2001 PASQUILL F WIND SPEED (mph) AT 10-m LEVEL Wind 1.0-4.0-8.0-13.0-19.0-Direct 3.9 7.9 12.9 18.9 24.0
+24.0 Total I
N NNE NE ENE E
WNW NW NNW 18 18 19 22 16 48 49 27 42 31 25 19 47 66 48 35 2
1 3
5 5
27 50 46 26 13 9
4 3
3 6
5 0
0 0
0 0
0 10 5
16 20 5
1 2
2 0
0 0
0 0
0 0
1 0
0 1
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 30 22 24 29 22 77 112 80 88 65 43 28 56 74 58 42 Total 530 208 61 2
0 0
801 Number of Calms 49 Number of Invalid Hours 0
Number of Valid Hours 850 VII-9
Omaha Public Power District Fort Calhoun Nuclear Station JOINT FREQUENCY DISTRIBUTION BY EVENTS EXTREMELY STABLE (delta T/ delta z > 4.0)
PERIOD OF RECORD:
JAN 2001 -
DEC 2001 PASQUILL G WIND SPEED (mph) AT 10-m LEVEL Wind 1.0-4.0-8.0-13.0-19.0-Direct 3.9 7.9 12.9 18.9 24.0
+24.0 Total N
NNE NE ENE E
WNW NW NNW 14 20 16 22 15 65 61 28 23 31 11 17 13 16 14 11 0
0 2
1 4
6 8
2 10 8
3 0
0 0
0 0
0 0
0 0
0 0
1 0
1 1
0 0
0 1
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
0 0
15 23 21 28 22 74 78 34 36 43 16 22 13 19 17 12 Total_________377______44_____4____0___0____0____425___
Total 377 44 4
0 0
0 425 Number of Calms 48 Number of Invalid Hours 0
Number of Valid Hours 473 Hours Accounted For:
8760 VII-10
11-C, Omaha Public Power District Fort Calhoun Nuclear Station JOINT FREQUENCY DISTRIBUTION BY PERCENT EXTREMELY UNSTABLE (delta T/ delta z < -1.9)
PERIOD OF RECORD:
JAN 2001 -
DEC 2001 PASQUILL A WIND SPEED (mph) AT 10-m LEVEL Wind 1.0-4.0-8.0-13.0-19.0-Direct 3.9 7.9 12.9 18.9 24.0
+24.0 Total N
NNE NE ENE E
WNW NW NNW 0.07
- 0. 03
- 0. 02
- 0. 10 0.05 0.02 0.03 0.00 0.03 0.05 0.06 0.06 0.01
- 0. 02 0.06 0. 0 9 0.16 0.08 0. 10 0.27 0. 14 0.08
- 0. 17 0.09
- 0. 16
- 0. 14 0.30
- 0. 13 0.05
- 0. 17 0.25 0.46 0
. 13 0.05
- 0. 02 0
. 02 0.07 0.09
- 0. 14 0.26 0.29 0.18
- 0. 14
- 0. 02 0.01
- 0. 10 0.47 0.34 0.01 0.00 0. 0 0 0. 0 0 0. 0 0 0.05 0. 10 0.18 0.34 0. 14 0. 02 0. 0 0 0. 01 0. 13
- 0. 13 0.07 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.05 0.06 0.00 0.00 0.00 0. 0 0 0. 0 0 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.05 0.01 0.00 0.00 0.00 0.00 0.00 0.00 0.37 0
. 16
- 0. 15 0.40 0.25 0.24 0.45
- 0. 54 0.91 0.57 0.51 0.21 0.08 0.42 0.90
- 0. 96 Total____0.71___2.74__2.33___1.18___0.10___0__06__7.11_
Total 0.71 2.74 2.33 1.18 0.10 0.06 7.11 Percent of Calms 0.00 Percent of Invalid Hours Percent of Valid Hours 0. 00 7.11 VII-ll
Omaha Public Power District Fort Calhoun Nuclear Station JOINT FREQUENCY DISTRIBUTION BY PERCENT MODERATELY UNSTABLE (-1.9 <= delta T/ delta z <= -1.7)
PERIOD OF RECORD:
JAN 2001 -
DEC 2001 PASQUILL B WIND SPEED (mph) AT 10-m LEVEL Wind 1.0-4.0-8.0-13.0-19.0-Direct 3.9 7.9 12.9 18.9 24.0
+24.0 Total N
NNE NE ENE E
WNW NW NNW
- 0. 09 0. 02 0.09 0.05 0.00 0.05 0.05
- 0. 03 0.05
- 0. 03 0.06 0.02
- 0. 02
- 0. 03
- 0. 14 0.07 0.37 0.10
- 0. 15
- 0. 05 0.08
- 0. 07 0.06 0.06
- 0. 13
- 0. 14 0.10 0.07
- 0. 05 0.08 0.37 0.43 0.09 0.01 0.01
- 0. 05 0.09 0.08
- 0. 17
- 0. 15 0.23
- 0. 09 0.06
- 0. 01 0
. 03 0.11
- 0. 14 0.41
- 0. 02 0.00 0. 00 0. 00
- 0. 00 0.01 0. 05 0. 17 0.25 0.25 0
. 02 0.01 0.00 0.00 0
. 02 0.01 0.00
- 0. 0 0 0.00 0.00 0.00 0.00 0.00
- 0. 02
- 0. 05 0.06 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.01 0.00 0.00
- 0. 00 0.00 0.00 0.00 0.00 0.00 0.00 0.57
- 0. 14 0.25
- 0. 14
- 0. 17 0.21 0.33 0.43
- 0. 70 0.57 0.24
- 0. 11 0.10 0.23
- 0. 67
- 0. 92 Total 0.80 2.28 1.74 0.82 0.13 0.01 5.78 Percent of Calms 0.01 Percent of Invalid Hours Percent of Valid Hours
- 0. 00 S. 79 VII-12
Omaha Public Power District Fort Calhoun Nuclear Station JOINT FREQUENCY DISTRIBUTION BY PERCENT SLIGHTLY UNSTABLE (-1.7 < delta T/ delta z <= -1.5)
PERIOD OF RECORD:
JAN 2001 -
DEC 2001 PASQUILL C WIND SPEED (mph) AT 10-m LEVEL Wind 1.0-4.0-8.0-13.0-19.0-Direct 3.9 7.9 12.9 18.9 24.0
+24.0 Total N
0.15 0.39 0.13 0.01 0.00 0.00 0.67 NNE 0.05 0.10 0.02 0.00 0.00 0.00 0.17 NE 0.06 0.07 0.02 0.00 0.00 0.00 0.15 ENE 0.03 0.18 0.03 0.00 0.00 0.00 0.25 E
0.01 0.03 0.11 0.00 0.00 0.00 0.16 ESE 0.05 0.07 0.18 0.01 0.00 0.00 0.31 SE 0.01 0.06 0.11 0.07 0.00 0.00 0.25 SSE 0.05 0.13 0.13 0.16 0.02 0.00 0.48 S
0.00 0.13 0.26 0.14 0.06 0.00 0.58 SSW 0.00 0.11 0.10 0.09 0.02 0.00 0.33 SW 0.01 0.15 0.09 0.03 0.00 0.00 0.29 WSW 0.01 0.07 0.03 0.02 0.00 0.00 0.14 W
0.02 0.07 0.01 0.01 0.00 0.00 0.11 WNW 0.05 0.07 0.13 0.02 0.00 0.00 0.26 NW 0.06 0.21 0.29 0.03 0.00 0.00 0.58 NNW 0.10 0.48 0.38 0.05 0.00 0.00 1.02 Total 0.65 2.31 2.03 0.65 0.10 0.00 5.74 Percent of Calms 0.01 Percent of Invalid Hours 0.00 Percent of Valid Hours 5.75 VII-13
Omaha Public Power District Fort Calhoun Nuclear Station JOINT FREQUENCY DISTRIBUTION BY PERCENT NEUTRAL (-1.5 < delta T/ delta z <= -0.5)
PERIOD OF RECORD:
JAN 2001 -
DEC 2001 PASQUILL D WIND SPEED (mph) AT 10-m LEVEL Wind 1.0-4.0-8.0-13.0-19.0-Direct 3.9 7.9 12.9 18.9 24.0
+24.0 Total N
NNE NE ENE E
WNW NW NNW
- 0. 71 0.51 0.35 0.40 0.40 0.33 0.24 0.24
- 0. 14 0.16 0.32 0.22 0.22 0.30 0.43
- 0. 75 1.28 0.45 0.47
- 0. 72 0.84 1.00 1.16 0.84 0.73 0.78 0.56 0.30 0.24 0.79 2.42 3.11 0.49
- 0. 16
- 0. 11 0.25
- 0. 66 0.89
- 1. 12
- 1. 62
- 1. 74
- 0. 76 0.39 0.06
- 0. 10 0.50
- 1. 61 1.89 0.01 0.01 0.00 0.00 0.02 0.15 0.40 1.27 1.29 0.61 0.27
- 0. 05
- 0. 02 0.15 0.30 0.30 0.00 0.00 0.00 0.00 0.00
- 0. 00
- 0. 07 0.10
- 0. 09 0.11
- 0. 07 0.03 0.01 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.01 0.01 0.00
- 0. 02 0.01 0.00 0.00 0.00 0.00 2.49 1.13 0. 95 1.37
- 1. 94 2.37 2.99 4.09 4.00 2.42
- 1. 63
- 0. 66 0.59
- 1. 74 4.76 6.05 Total___5.72___15.68__12.36___4.84__0.49___
0.06__3__
.16 Total 5.72 15.68 12.36 4.84 0.49 0.06 39.16 Percent of Calms 0.02 Percent of Invalid Hours 0.00 Percent of Valid Hours 39.18 VII-14
Omaha Public Power District Fort Calhoun Nuclear Station JOINT FREQUENCY DISTRIBUTION BY PERCENT SLIGHTLY STABLE (-0.5 < delta T/ delta z <= 1.5)
PERIOD OF RECORD:
JAN 2001 -
DEC 2001 PASQUILL E WIND SPEED (mph) AT 10-m LEVEL Wind 1.0-4.0-8.0-13.0-19.0-Direct 3.9 7.9 12.9 18.9 24.0
+24.0 Total N
NNE NE ENE E
WNW NW NNW
- 0. 61 0.29 0.22 0.37 0.37
- 0. 72 0.51 0.50 0.34 0.33 0.48 0.40
- 0. 64 1.12 0.98 0.91 0.18 0.08 0.07 0. 10 0.33 1.14
- 1. 68 1.24 1.04 0.46 0.23 0.15 0.40 0. 91 1.12 0
. 73 0
. 02 0
. 03 0
. 05 0
. 02 0.06
- 0. 13 0.56
- 1. 72
- 1. 71 0.88 0.41
- 0. 17
- 0. 11
- 0. 14 0.18
- 0. 15
- 0. 02 0.00 0.00 0.01 0.00 0.00 0
. 03 0.25 0.51 0.50 0.38 0. 0 1 0. 0 0 0. 0 0 0. 0 1 0. 03 0. 0 0 0.00 0. 0 0 0. 0 0 0. 00
- 0. 0 0 0.00 0.01 0.05 0.05
- 0. 03 0.00 0.00 0.00 0.00 0.00 0.00 0. 00 0.00 0. 0 0 0. 0 0 0. 0 0 0. 0 0 0. 0 0 0. 0 1 0. 0 1 0. 0 1
- 0. 0 0
- 0. 0 0 0.00 0.00 0.00 0.83 0.40 0.34 0.50 0. 78
- 1. 99 2.80 3. 74 3.68 2.23 1.54 0.76 1.15 2. 19 2.31 1.83 Total____8.78__9.86___6.35___1.77__0.14___0.03___26__93 Total 8.78 9.86 6.35 1.77 0.14 0.03 26.93 Percent of Calms 0.14 Percent of Invalid Hours 0.00 Percent of Valid Hours 27.07 VII-15
Omaha Public Power District Fort Calhoun Nuclear Station JOINT FREQUENCY DISTRIBUTION BY PERCENT MODERATELY STABLE (1.5 < delta'T/ delta z <= 4.0)
PERIOD OF RECORD:
JAN 2001 -
DEC 2001 PASQUILL F WIND SPEED (mph) AT 10-m LEVEL Wind 1.0-4.0-8.0-13.0-19.0-Direct 3.9 7.9 12.9 -
18.9 24.0
+24.0 Total N
NNE NE ENE E
WNW NW NNW 0.21 0.21 0.22 0.25 0.18 0.55 0.56 0.31 0.48 0.35 0.29 0.22 0.54 0.75 0.55 0.40
- 0. 02 0.01 0.03 0.06 0.06 0.31 0.57 0.53 0.30
- 0. 15 0.10
- 0. 05
- 0. 03
- 0. 03 0.07
- 0. 06 0.00 0.00 0.00 0. 00 0.00 0.00
- 0. 11 0.06 0.18 0.23 0.06 0.01 0.02
- 0. 02 0.00 0.00 0.00 0.00 0.00 0.00 0. 0 0
- 0. 01
- 0. 00 0.00 0.01 0.00 0.00 0.00 0.00 0. 0 0 0.00 0.00 0.00 0.00 0.00
- 0. 00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0. 0 0 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
- 0. 00 0.00 0. 00 0.00 0.00 0.00 0.00 0.00 0.00
- 0. 00 0.00 0.34 0.25 0.27 0.33 0.25 0.88 1.28 0. 91 1.00 0.74 0.49 0.3.2 0.64
- 0. 84
- 0. 66 0.48 Total____6.05___2.37___0.70____0.02___0.00___0.00__9.1 Total 6.05 2.37 0.70 0.02 0.00 0.00 9.14 Percent of Calms 0.56 Percent of Invalid Hours Percent of Valid Hours 0.00 9.70 VII-16
I Omaha Public Power District Fort Calhoun Nuclear Station JOINT FREQUENCY DISTRIBUTION BY PERCENT EXTREMELY STABLE (delta T/ delta z > 4.0)
PERIOD OF RECORD:
JAN 2001 -
DEC 2001 PASQUILL G WIND SPEED (mph) AT 10-m LEVEL Wind 1.0-4.0-8.0-13.0-19.0-Direct 3.9 7.9 12.9 18.9 24.0
+24.0 Total N
0.16 0.00 0.00 0.00 0.00 0.00 0.17 NNE 0.23 0.00 0.00 0.00 0.00 0.00 0.26 NE 0.18 0.02 0.00 0.00 0.00 0.00 0.24 ENE 0.25 0.01 0.00 0.00 0.00 0.00 0.32 E
0.17 0.05 0.00 0.00 0.00 0.00 0.25 ESE 0.74 0.07 0.00 0.00 0.00 0.00 0.84 SE 0.70 0.09 0.01 0.00 0.00 0.00 0.89 SSE 0.32 0.02 0.00 0.00 0.00 0.00 0.39 S
0.26 0.11 0.01 0.00 0.00 0.00 0.41 SSW 0.35 0.09 0.01 0.00 0.00 0.00 0.49 SW 0.13 0.03 0.00 0.00 0.00 0.00 0.18 WSW 0.19 0.00 0.00 0.00 0.00 0.00 0.25 W
0.15 0.00 0.00 0.00 0.00 0.00 0.15 WNW 0.18 0.00 0.01 0.00 0.00 0.00 0.22 NW 0.16 0.00 0.00 0.00 0.00 0.00 0.19 NNW 0.13 0.00 0.00 0.00 0.00 0.00 0.14 Total 4.30 0.50 0.05 0.00 0.00 0.00 4.85 Percent of Calms 0.55 Percent of Invalid Hours 0.00 Percent of Valid Hours 5.40 Percent of Hours Accounted For:
100.00 VII-17
Omaha Public Power District t As Fort Calhoun Radiological Environmental Report 2002 I
OMAHA PUBLIC POWER DISTRICT FORT CALHOUN STATION RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT TECHNICAL SPECIFICATION 5.9.4.b January 01, 2002 - December 31, 2002
Annual Radiological Environmental Operating Report This report is submitted in accordance with Section 5.9.4.b of the Technical Specifications of Fort Calhoun Station Unit No. 1, Facility Operating License DPR-40 for the period January 01, 2002 through December 31, 2002.
In addition, this report provides any observations and anomalies that occurred during the monitoring period.
Reviewed by:
Approved by:
S
+/-upervi r-System Chemistry I
.-A' Manager-Chemistry
Annual Radiological Environmental Operating Report In accordance with Technical Specification 5.9.4.b, herein is the Fort Calhoun Station (FCS) Annual Radiological Environmental Operating Report for year 2002.
The data provided is consistent with the objectives as specified in Section 5.2.2 of the Offsite Dose Calculation Manual (ODCM), "Annual Radiological Environmental Operating Report." The report is presented as follows:
- 1)
An introductory discussion of the implementation of the Radiological Environmental Monitoring Program (REMP), including program observations and environmental impact relevant to the operation of FCS.
- 2)
The sample class, sample collection frequency, number of sample locations, and the number of samples collected this reporting period for each parameter is delineated in Table 1.0.
- 3)
A statistical evaluation of REMP data is summarized in Table 2.0, in accordance with Regulatory Guide 4.8, Table 1. For each type of sample media and analysis, Table 2.0 presents data separately for all indicator locations, all control (background) locations, and the location having the highest annual mean result. For each of these classes, Table 2.0 specifies the following:
- a.
The total number of analyses
-b.
The fraction of analyses yielding detectable results (i.e., results above the highest Lower Limit of Detection (LLD) for this period
- c.
The maximum, minimum, and average results
- d.
Locations with the highest mean are specified along with their distance and direction from the center of plant containment
- 4)
Table 3.0 is a listing of missed samples and explanations
- 5)
Table 4.0 is the Environmental Land Use Survey
- 6)
Table 5.0 is the Radiological Environmental Sampling Locations and Media
- 7)
Review of Environmental Inc. Quality Assurance Program
- 8)
Appendix A describes the Interlaboratory Comparison Program
- 9)
Appendix B describes the vendor Data Reporting Conventions utilized
- 10)
Appendix C reports the information required when primary coolant specific activity has exceeded the limits of Technical Specification 2.1.3
- 11)
Appendix D is the Sample Location Map Page 1 of 17
INTRODUCTION Radiological Environmental Monitoring Program (REMP) - 2002 This report gives the results of the Radiological Environmental Monitoring Program (REMP) for the year 2002. The REMP is a requirement of the Fort Calhoun Station (FCS) operating license. It was initiated prior to plant operation in 1973.
The main purpose of the REMP is to ensure public safety by monitoring plant discharges and assessing the effect,-if any, of plant operations, on the environment. Samples are collected that would account for various exposure pathways such as ingestion, inhalation, adsorption and direct exposure.
Samples collected at receptor locations on a regular basis include: air, water, milk, vegetation, fish, sediment and food crops. Direct radiation is measured by thermoluminescent dosimeters (TLDs). These samples and TLDs are sent to an independent vendor laboratory for analysis. The vendor uses analytical methods that are sensitive enough to detect a level of activity far below that which would be considered harmful. Locations for sample collection are based on radiological and meteorological data from the Annual Effluent Release Report and information obtained from the Environmental Land Use Survey.
Most samples, particularly indicator samples, are collected in a circular area within a five-mile radius of plant containment. (However, control locations are usually outside of five miles.) This circle is divided into sixteen equal sectors, each assigned an identification letter "A" through "R" (note: letters "I" and "O" are not used, as they may be mistaken for the numbers "1" and "0"). Sector "A" is centered on North or zero degrees. Sectors are also given directional labels such as 'West-Southwest" ('WSW"). Sample locations are listed by number along with their respective distances and direction from plant containment, in the Offsite Dose Calculation Manual (ODCM).
When assessing sample results, data from indicator locations (those most likely to be effected by plant operations) are compared to those from control locations (those least or not likely to be effected). Results from an indicator location which were significantly higher than those from a control location, could indicate a plant attributable effect, and could require additional investigation. In the year 2002, only one plant attributable result was seen.
The results of the sample analyses, as required by the FCS Offsite Dose Calculation Manual (ODCM), are presented in the attached statistical tables in accordance with Table I of Regulatory Guide 4.8, "Environmental Technical Specifications for Nuclear Power Plants." Sample collection was conducted by plant chemistry/environmental staff. A contract vendor (Environmental Inc.,
Northbrook, Illinois) performed sample analyses, preparation of monthly reports and the statistical evaluation of sample results. All vendor analysis techniques met the sensitivity requirements as stated in the ODCM.
Page 2 of 17
Results for 2002 were generally within expected ranges and compared closely with historical results. The following is a review of specific sample results.
- 1)
Ambient Gamma Radiation Ambient gamma radiation is measured by thermoluminescent dosimeters (TLDs) provided by the vendor laboratory. These TLDs contain calcium sulfate phosphors, and are processed quarterly. They are located at thirteen indicator locations and two control/shielded locations as per the ODCM. Three of these indicator locations were added at the new air sampler locations in September 2002 per NRC Branch Technical Position requirements to co-locate a TLD with each air sampler. There were no lost or damaged TLDs for the year. Results for 2002 were within the same range as historical results. Indicator locations showed the same range of results as the control and shielded TLDs. The results indicate no plant-related effects on the environment, therefore, no changes or modifications to plant systems or operation are required.
- 2)
Milk kNe-etation Milk samples are required to be collected every two weeks, from May through September. The indicator location for milk samples is approximately 0.7 miles from plant in Sector K (SSW). The source of this milk was from a small goat herd. The control location for milk samples was approximately 9.9 miles from the plant, in Sector J (S), at a large, commercial dairy. The indicator sample was unavailable on July 25, 2002, so vegetation was collected as a substitute as per surveillance requirements. This occurrence did not reduce the overall effectiveness of the REMP. All results for lodine-131, Cesium and other gammas, were
<LLD for both the control and indicator samples, as well as the substitute vegetation sample. The results indicate no plant-related effects on the environment, therefore, no changes or modifications to plant systems or operation are required.
- 3)
Fish Several species of fish, chosen to represent the aquatic food chain, are collected at both a downstream indicator location (River Mile 644-646),
and an upstream control location (River Mile 665-667). Results from both locations were <LLD for all gamma isotopes. The results indicate no plant-related effects on the environment, therefore, no changes or modifications to plant systems or operation are required.
- 4)
Food Crops Garden vegetables were collected at the offsite indicator location calculated to have the highest potential exposure pathway. This location is approximately 0.94 from plant containment in Sector H (SSE). Control Page 3 of 17
samples were collected at the same dairy farm which serves as the control location for milk samples. Results were within historical ranges and <LLD for all samples. The results indicate no plant-related effects on the environment, therefore, no changes or modifications to plant systems or operation are required.
- 5)
Sediment River sediment samples are collected twice a year at upstream control locations and downstream indicator locations. For the year 2002, all results from both up-and downstream were <LLD. The results indicate no plant-related effects on the environment, therefore, no changes or modifications to plant systems or operation are required.
- 6)
Air Monitoring Three new sample locations were added in the third quarter, 2002. They are at locations 29, 36 and 37. These receptor locations were added to the REMP because they were calculated to be the highest annual average ground level D/Q, consistent with the requirements of the NRC Branch Technical Position. All original location results are within historical ranges and new locations show the same range of results. Indicator location results were within the same range as the Control location, indicating no plant-related effects. However, several Condition Reports (CRs) were written during the year.
- a.
On April 3, part of the LCD on the elapsed time display was burned out at location OAP-A (CR200200804). Actual Time On/Time Off as recorded by the technician was used to calculate the amount of air flow for the sample. The air pump was returned to the shop for repair. This occurrence was unforeseeable and had no impact on results.
- b.
On September 17, the tygon tubing used to exhaust air from the air pump at location OAP-H was found to have come loose from the back of the pump (CR200203276). The tubing was replaced. There was no impact on results.
- c.
On September 18, one filter paper was collected (at location OAP-I) with a short, hairline tear along its perimeter by the hold down ring (CR200203283). Upon investigation, it appeared that the mesh filter support was not quite level and could have abraded the filter paper.
A review of the sample results did not show any discernable effect.
- d.
On October 2, a severe storm caused a power outage in the Fort Calhoun area, for approximately four hours. Affected sample locations were: OAP-A, OAP-B, OAP-G, OAP-H and OAP-I. All elapsed time displays on the air pumps reflected this outage. No Page 4 of 17
samples were lost or damaged and total sample volume was based on actual run time.
- e.
Several timer problems were noted during the year, when the elapsed timer display did not agree with the Time On/Time Off as recorded by the technician. Procedure CH-ST-RV-0008, "Environmental Sample Collection - Air Monitoring," allowed for sample time to be calculated using the Time On/Time Off information as written down by the technician. However, it did not state when this methodology should be used. Additional guidance was inserted into the procedure to clarify this. In all cases, the most conservative method for determining run-time will be used. Additionally, all sample locations now have a secondary, back-up timer installed.
A review of all air sample results for the year 2002 did not show any unusual results or any indication of a plant-related effect on air quality, therefore no changes or modifications to plant systems or operation are required.
- 7)
Water Samples A detectable tritium result occurred in the first quarter of 2002. Location OSW-B, 0.5 miles downstream showed 894 +/-118 pCi/L. These results are below the ODCM reporting level of 2000 pCi/L and well below the Federal drinking water standard of 20,000 pCi/L. The quarterly composite sample was reanalyzed with a result of 958 +/-120 pCi/L. Also, the individual monthly samples (composites of weekly samples) were analyzed with the following results: January, 806 +/-115; February, <165; March, 1579 +/-139 pCi/L. Plant staff conducted a chemistry evaluation of effluent release data and it was determined that environmental water samples were collected during monitor tank releases during January and March. Tritium concentration at site discharge during the releases was calculated using the low mixing value listed in the ODCM for low river flows. The tritium concentration for tank release 2002003 was 3646 pCi/L and for tank release 2002020 was 1448 pCi/L. Creating a composite for January and March using these calculated values and sample volumes obtained from environmental samples during periods of no release would result in composite values consistent with the Environmental Inc.'s findings. The dose estimated represents 0.3% of the annual limit of 3 mrem which does not significantly impact the environment. Future monitor tank releases and dose estimates will continue to be tracked and trended to insure minimal impact on the environment. No tritium was detected in samples at the nearest downstream drinking water intake during the year 2002. The results indicate no plant-related effects on the environment, therefore, no changes or modifications to plant systems or operation are required.
Page 5 of 17
Table 1.0 Sample collection program.
Number of Number of Samples Collection Sample Collected Sample Class Frequency Locations This Period Background Radiation (TLDs)
Quarterly 15 54 Air Particulates Weekly 8
311 Airborne Iodine Weekly 8
311 Milk Bi-weekly 2
21 Pasture Grass (milk substitute) 2 1
Water Monthly 3
36 Fish Annually 2
5 Sediment Semiannually 2
4 Food Crops Annually 3
7 TOTAL 750 Page 6 of 17
Table 2.0 Radiological Environmental Monitonng Program Summary Reporting Peniod January-December, 2002 Name of Facility Location of Facility Fort Calhoun Nuclear Power Station - Unit 1 Washington, Nebraska
( County, State )
Docket No 50-285
Background
Gamma 54 0 5 1 5 (46/46)
OTD-I-(I), NW of Plant 1 6 (8/8) 1 4 (8/8) 0 Radiation (1 1-1 9) 0 7 mi @ 305°/NW (1.4-1 8)
(1 2-1 8)
(TLD)
OTD-E-(C). EOF (mRlweek) 14 9 mi @ 153°/SSE Airbome GB 311 0 005 0 029 (2591259)
OAP-A-(I), l1Om Tower 0 031 (52/52) 0 029 (52152) 0 Particulates (0 009-0 066) 0 5 mi @ 293'1WNW (0 013-0 066)
(0 012-0 052)
(pCL/m3)
GS 26 Cs-134 0 001
< LLD
< LLD 0
Cs-137 0 001
< LLD
< LLD 0
Other Gammas 0 001
< LLD
< LLD 0
Airbome 1-131 311 0 07
< LLD
< LLD 0
Iodine (pClm3)
Milk 1-131 21 0 5
< LLD
< LLD 0
(pCYL)
GS 21 K-40 150 1663 (10110)
OFM-F-(I), Bansen, 1663 (10/10) 1362 (11/11) 0 (1523-1814) 0 7 mi @ 207°/SSW (1523-1814)
(1244-1489)
Cs-134 15
< LLD
< LLD 0
Cs-137 15
< LLD
< LLD 0
Other Gammas 15
< LLD
< LLD 0
Pasture Grass (milk substitute) pCilg wet GS 1
Mn-54 Co-58 Co-60 Fe-59 Zn-65 Zr-Nb-95 1-131 Cs-134 Cs-1 37 Ba-La-140 0 025 0 020 0019 0 045 0 062 0.010 0 021 0021 0031 0011
< LLD
< LLD
< LLD
< LLD
<LLD
< LLD
< LLD
< LLD
< LLD
< LLD
< LLD
< LLD
< LLD
< LLD
< LLD
< LLD
< LLD
< LLD
< LLD
< LLD 0
0 0
0 0
0 0
0 0
0 Water GS 36 (pCI/L)
Cs-134 15
< LLD
< LLD
< LLD Other Gammas 15
< LLD
< LLD H3 12 300 894 (118)
OSW-B-(I), Downstream 894 (1/4)
< LLD 0 5 mi. @ 108°/ESE Page 7 of 17
Table 2 0 Radidogical Environmental Monitonng Program Summary Reporting Peniod January-December, 2002 Name of Facility Location of Facility Fort Calhoun Nuclear Power Station - Unit 1 Washington, Nebraska Docket No 50-285
( County, State )
Fish GS 5
(pCi/g wet)
Mn-54 0 015
< LLD
< LLD 0
Fe-59 0.030
< LLD
< LLD 0
Co-58 0 012
< LLD
< LLD 0
Co-60 0 014
< LLD
< LLD 0
Zn-65 0 025
< LLD
< LLD 0
Cs-134 0 017
< LLD
< LLD 0
Cs-137 0 015
< LLD
< LLD 0
Sediment GS 4
pClg dry Mn-54 0 026
< LLD
< LLD 0
Fe-59 0 031
< LLD
< LLD 0
Co-58 0 026
< LLD
< LLD 0
Co-60 0 070
< LLD
< LLD 0
Zn-65 0 055
< LD
< LLD 0
Cs-134 0 032
< LLD
< LLD 0
Cs-137 0.023
< LLD
< LD 0
Food Crops GS 7
(pCig wet)
Mn-54 0 009
< LLD
< LLD 0
Fe-59 0 027
< LLD
< LLD 0
Co-58 0 011
< LD
< LID 0
Co-60 0.012
< LLD
< LLD 0
Zn-65 0 020
< LLD
< LLD 0
Zr-Nb-95 0 014
< LLD
< LLD 0
Cs-134 0 011
< LLD
< LLD 0
Cs-137 0 010
< LLD
< LLD 0
Ba-La-140 0 026
< LLD
< LLD 0
a GB = gross beta, GS = gamma scan b LLD = nominal lower limit of detection based on a 95% confidence level c Mean and range are based on detectable measurements only (i.e. >LLD) Fraction of detectable measurements at specified locations is indicated in parentheses (F) d Locations are specified (1) by code, (2) by name, and (3) by distance and direction relative to the Reactor Containment Building 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 the typical pre-operational value for the medium or location Page 8 of 17
Table 3.0 Listing of missed samples (samples scheduled but not collected)
Sample Type Date Location Reason All required samples for the REMP were collected as scheduled for 2002.
Note: A typographical error was discovered in the 2001 Annual Radiological Environmental Operating Report, Table 3.0. The statement should read as follows:
"All required samples for the REMP were collected as scheduled for 2001."
Page 9 of 17
C( ( C ( ( (
CC C ( C C C
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Table 4.0 Environmental Land Use Survey To-u (a
(D 0
-I Sector Type of Use Owner's Name (miles/degrees)
Counting Technique Males/Age(')
Females/Age(')
Remarks Nearest Residence F. Smith 4.57 / 349 Interview 1 Adult 1 Adult None Milk Animal None None None None None None Meat Animal None None None None None None Vegetable Garden None None None None None None Nearest Residence J. Rand 1.93 / 12 Questionnaire 1 Adult 1 Adult None Milk Animal None None None None None None Meat Animal D. Dugdale 4.72 / 29 Interview 1 Adult, 1 Child 1 Adult, 1 Teen None Vegetable Garden None None None None None None Nearest Residence Riverside Farms 1.52 / 42 Interview 1 Adult 1 Adult None Milk Animal None None None None None None Meat Animal None None None None None None Vegetable Garden C. Salter 3.29 / 43 Questionnaire 1 Adult 1 Adult None Nearest Residence G. Meade 4.79 / 63 Questionnaire 1 Adult 1 Adult None Milk Animal None None None None None None Meat Animal None None None None None None Vegetable Garden None None None None None None (1) Approximate age categories in receptor deck for evaluating dose commitment:
Infant 0-1 Yr.
Child 1-11 Yrs.
Teen 12-17 Yrs.
Adult Over 17 Yrs.
C ( ( (
C
( (
(
C C C C C ( ( C C C C C C C C C C C C C (
(
C C C ( C C C C ( C C C C Table 4.0 Environmental Land Use Survey (continued)
T (a
CD 0
-4 Sector Type of Use Owner's Name
(
oiles/degrees)
Counting Technique Males/Age(')
Females/Age(')
Remarks Nearest Residence B. Herman 4.67 / 89 Interview 1 Adult 1 Adult None Milk Animal None None None None None None E
Meat Animal D. Brothers 4.91 /90 Interview 1 Adult 1 Adult None Vegetable Garden B. Herman 4.67 /89 Interview 1 Adult 1 Adult None Nearest Residence Wilson Island 4.22 121 Questionnaire 1 Adult 1 Adult None Milk Animal None None None None None None F
Meat Animal None None None None None None Vegetable Garden None None None None None None Nearest Residence T. Carter 1.67/ 145 Questionnaire 1 Adult 1 Adult None Milk Animal None None None None None None Meat Animal J. Pane 4.59/ 146 Interview 1 Adult, 1 Teen 1 Adult None Vegetable Garden W. Kalin 1.74 / 145 Interview 1 Adult 1 Adult None Nearest Residence A. Pechnik 0.94 /163 Interview 1 Adult 1 Adult None Milk Animal None None None None None None H
Meat Animal R. Hineline 1.82/ 148 Questionnaire 2 Adults 1 Adult None Vegetable Garden A. Pechnik 0.94 /163 Interview 1 Adult 1 Adult None (1) Approximate age categories in receptor deck for evaluating dose commitment:
Infant 0-1 Yr.
Child 1-11 Yrs.
Teen 12-17 Yrs.
Adult Over 17 Yrs.
CIC C ((
C CCC (C(
C C
C C C
C C C C C CC C( C (C ( (
Table 4.0 Environmental Land Use Survey (continued)
-D ID D_
0
-4 Sector Type of Use Owner's Name (miles/degrees)
Counting Technique Males/Age(1)
Females/Age~"
Remarks Nearest Residence J. Ellis 0.74/ 182 Interview 2 Adults 1 Adult None Milk Animal None None None None None None Meat Animal L. Dickes 2.60 / 170 Questionnaire 2 Adults 1 Adult None Vegetable Garden J. Ellis 0.74 / 182 Interview 2 Adults 1 Adult None Nearest Residence T. Bansen 0.65 / 203 Interview I Adult; 2 Child 1 Adult; 1 Child None Milk Animal T. Bansen 0.65 / 203 Interview 1 Adult; 2 Child 1 Adult; 1 Child None K
Meat Animal T. Bansen 0.65 / 203 Interview 1 Adult, 2 Child 1 Adult, 1 Child None Vegetable Garden T. Bansen 0.65 / 203 Interview 1 Adult; 2 Child,1 Adult; 1 Child None Nearest Residence D. Robertson 0.73 / 224 Interview 1 Adult, 1 Teen 1 Adult, 1 Teen None Milk Animal None None None None None None Meat Animal D. Robertson 0.73 / 224 Interview 1 Adult, 1 Teen 1 Adult, 1 Teen None Vegetable Garden K. Fredericksen 1.31 / 233 Questionnaire 1 Adult 1 Adult None Nearest Residence M. Bensen 1.06 / 257 City Register 1 Adult 1 Adult None Milk Animal None None None None None None Meat Animal B. Wrich 2.42 / 250 Interview 1 Adult 1 Adult; I Child None Vegetable Garden D. Russell 1.21 /246 City Register 1 Adult I Adult None (1) Approximate age categories in receptor deck for evaluating dose commitment:
Infant 0-1 Yr.
Child 1-11 Yrs.
Teen 12-17 Yrs.
Adult Over 17 Yrs.
( ( ( ( (- C
( c C c( (
c C C c c ( ( ( ( c
( C C C( ( ( ( (C ( ( ( ( c(
( ( ( ( C (
Table 4.0 Environmental Land Use Survey (continued)
(D (AD 0
-4.
Sector Type of Use Owner's Name Coordinates Counting Technique Males/Age(')
Females/Age(')
Remarks I__
(m ile s /d e g re e s )
Nearest Residence D. Nielsen 1.20 / 263 Questionnaire 1 Adult 1 Adult None Milk Animal None None None None None None Meat Animal J. Anderson 3.25 / 281 Interview 1 Adult None None Vegetable Garden D. Nielsen 1.20 / 263 Questionnaire 1 Adult 1 Adult None Nearest Residence G. Wachter 2.27 / 302 City Register 1 Adult 1 Adult None Milk Animal None None None None None None Meat Animal R. Wrich 2.74 / 283 Questionnaire 1 Adult, 1 Child 1 Adult; 1 Child None Vegetable Garden E. Epperson 2.97 / 284 Questionnaire None 1 Adult None Nearest Residence T. Petersen 2.40 / 318 Interview 1 Adult None None Milk Animal None None None None None None Meat Animal None None None None None None Vegetable Garden T. Petersen 2.40 / 318 Interview 1 Adult None None Nearest Residence K. Kelley 2.08 / 330 Interview None 1 Adult None Milk Animal None None None None None None Meat Animal None None None None None None
_-Vegetable Garden S. Sorensen 4.01 / 329 City Register 1 Adult 1 Adult; 1 Child None (1) Approximate age categories in receptor deck for evaluating dose commitment:
Infant 0-1 Yr.
Child 1-11 Yrs.
Teen 12-17 Yrs.
Adult Over 17 Yrs.
b
(
C
( (
Ra gca EC n
CiC CaC
( C CaC Cn
(
C C C C
(
(t ( C C
( C C
(
(
Table 5.0 Radiological Environmental Sampling Locations and Media
-U (D
0
-.4 Approximate Approximate Sample Ap t
Distance from Direction Air Monitoring Vegetables Station Colecronite Center of (degrees Sector TLD Water Milk Sediment Fish and Food No.
Collection Sites Containment from true Airborne Airborne Products (miles) north)
Particulate Iodine Onsite Station, 1
11 0-meter weather 0.53 293 01WNW P
X X
X tower Onsite Station, 2
adjacent to old plant 0.59 207 "/SSW K
X X
X access road Offsite Station, 3
Intersection of Hwy.
0.94 1 45"/SE G
X X
X 75 and farm access road 4
Blair OPPD office 2.86 305 0/NW Q
X X
X
_=_
5 EOF Building, North14953/S H
Omaha Power Station 14.9 153 0155E H
X 6
Fort Calhoun, NE City 5.18 150 0/SSE H
X Hall Fence around intake 7
gate, Desoto Wildlife 2.07 1020/ESE F
X Refuge Onsite Station, 8
entrance to Plant Site 0.55 191 °/S J
X from Hwy. 75 Onsite Station, NW of 0.68 305°/NW Q
X Plant
C(
( (
( (
(
(
(
E
(((C
((((
C C ( ( (CC ( ( ( ( ( (
( ( ( ( ( (
C
( (
Table 5.0 Radiological Environmental Sampling Locations and Media (continued)
D)
CD Cu
-4
--1 Approximate Approximate Sample Distance from Direction Air Monitoring Vegetables Station Approximate Center of (degrees Sector TLD Water Milk Sediment Fish and Food No.
Collecton Sites Containment from true Airborne Airborne Products (miles) north)
Particulate Iodine 10 Onsite Station, WSW 0.61 242°/WSW M
X of Plant Offsite Station, SE of 1.07 139 0/SE G
x P la n t Metropolitan Utilities 12 Dist. Florence 14.3 1540/SSE H
X Treatment Plant North Omaha, NE West bank Missouri 13 River, downstream 0.45 1080/ESE F
X X
from Plant discharge Upstream from Intake 14 Bldg, west bank of 0.09 4°/N A
X X
river 151 20 Mohr Dairy 9.86 1860/S J
=
=
X 2
=
X 2 1 '
II__
22 Fish Sampling Area, 0.08 6°lN A
X Missouri River (R.M. 645.0) 1__
C ( C C ( C ( C ( c E c C C C c C C C c C C e
(
c C
C C
( (
C
( ( (
C ( (
C
(
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Table 5.0 Radiological Environmental Sampling Locations and Media (continued)
-El 0
co ID 0o Approximate Approximate Sample Distance from Direction Air Monitoring Vegetables Station Approximate Center of (degrees Sector TLD Water Milk Sediment Fish and Food No.
Collection Stes Containment from true Airborne Airborne Products (miles) north)
Particulate Iodine Fish Sampling Area, 17.9 358 0/N A
23 Missouri River (R.M. 666.0)
______ A X
241 2 5 1 261 271
=
=
=
=
283 Alvin Pechnik Farm 0.94 1630/SSE H
X X
X X
29'
=
=
_
30' 311 32 Valley Substation #902 19.6 221 O/SW L
X X
X 333 Bansen Farm 0.7 2030/SSW K
X2 341
=
=
=
=
=
35 Onsite Farm Field 0.52 118°IESE F
X Offsite Station 363 Intersection 0.75 227 °/SW L
X X
X Hwy 75/Co.Rd. P37 373 Offsite Station Desoto 1.57 1440/SE G
X X
X Township_
NOTES:
(1) Location Is currently discontinued and Is documented in the table for historical reference only.
(2) When a milk sample is not available at a location, a broad leaf (pasture grass) vegetation sample will be collected at that location as a substitute.
(3) Locations represent highest potential exposure pathways as determined by the biennial Land Use Survey, performed in accordance with Part 1, Section 6.3.2, and are monitored as such.
Review of Environmental Inc., Quality Assurance Program Fort Calhoun Station contracts with Environmental Inc., Midwest Laboratory (vendor) to perform radioanalysis of environmental samples. Environmental Inc.
participates in interlaboratory comparison (crosscheck) programs, as part of its quality control program. These programs are operated by agencies such as the Department of Energy which supply blind-spike environmental type samples such as milk or water containing concentrations of radionuclides unknown to the testing laboratory. This type of program provides an independent check of the testing laboratory's procedures and processes, and provides indication of possible weaknesses. In addition, Environmental Inc. has its own in-house QA program of blind-spike and duplicate analyses.
Environmental staff reviewed results of the vendor's in-house quality assurance program for pass/fail criteria, and made the following observations:
- One Cesium-134 sample failed in the Interlaboratory Comparison Program.
Due to high percent of failures among all participants, the provided sample was deemed suspect. This would not have affected FCS sample analysis.
- One failed TLD result was due to the TLD holder being improperly positioned on the irradiator. This would not impact FCS TLD results.
- One milk sample showed a trace of Strontium-90 (Sr-90) slightly above LLD, which is not unheard of as there are trace amounts of Sr-90 in the environment.
- One spiked water sample had a known activity less than the laboratory's LLD. The sample was recounted for 2000 minutes with results within limits.
This would not affect FCS sample results.
- One water and one soil sample yielded false positives which would have no result on FCS results. FCS does not collect soil samples.
- Additionally, there were a few reporting or conversion errors which were corrected.
All of the above were documented in Condition Reports.
Page 17 of 17
N-Environmental, Inc.
Mdwvest Laboratory a] Plbhen Techoldoges Co 7OOLmdhdsWoaSd.thblmck.IL 600B22 (847) 5640700 lf (847) 58-4"517 APPENDIX A INTERLABORATORY COMPARISON PROGRAM RESULTS NOTE:
Environmental Inc., Midwest Laboratory participates in intercomparison studies administered by Environmental Resources Associates, and serves as a replacement for studies conducted previously by the U.S. EPA Environmental Monitoring Systems Laboratory, Las Vegas, Nevada. Results are reported in Appendix A. TLD Intercomparison results, in-house spikes, blanks, duplicates and mixed analyte performance evaluation program results are also reported. Appendix A is updated four times a year, the complete Appendix is included in March, June, September and December monthly progress reports only.
January, 2002 through December, 2002
Appendix A Interlaboratorv Comparison Program Results Environmental, Inc., Midwest Laboratory, formerly Teledyne Brown Engineering Environmental Services Midwest Laboratory has participated in interlaboratory comparison (crosscheck) programs since the formulation of it's quality control program in December 1971. These programs are operated by agencies which supply environmental type samples (e.g., milk or water) containing concentrations of radionuclides known to the issuing agency but not to participant laboratories. The purpose of such a program is to provide an independent check on a laboratory's analytical procedures and to alert it of any possible problems.
Participant laboratories measure the concentration of specified radionuclides and report them to the issuing agency. Several months later, the agency reports the known values to the participant laboratories and specifies control limits. Results consistently higher or lower than the known values or outside the control limits indicate a need to check the instruments or procedures used.
Results in Table A-1 were obtained through participation in the environmental sample crosscheck program administered by Environmental Resources Associates, serving as a replacement for studies conducted previously by the U.S. EPA Environmental Monitoring Systems Laboratory, Las Vegas, Nevada.
The results in Table A-2 were obtained for Thermoluminescent Dosimeters (TLDs), via Intemational Intercomparison of Environmental Dosimeters under the sponsorships listed in Table A-2. Results of internal laboratory testing is also listed Table A-3 lists results of the analyses on in-house 'spiked' samples for the past twelve months. All samples are prepared using NIST traceable sources. Data for previous years available upon request.
Table A-4 lists results of the analyses on in-house 'blank' samples for the past twelve months. Data for previous years available upon request. request.
Table A-5 list results of the in-house 'duplicate" program for the past twelve months. Acceptance is based on the difference of the results being less than the sum of the errors. Data for previous years available upon request.
The results in Table A-6 were obtained through participation in the Mixed Analyte Performance Evaluation Program.
The results in Table A-7 were obtained through participation in the Environmental Measurement Laboratory Quality Assessment Program.
Attachment A lists acceptance criteria for'spiked" samples.
Out-of-limit results are explained directly below the result.
Al
LABORATORY PREC Analysis Gamma Emitters Strontium-89b Strontium_90b Potassium-40 Gross alpha Gross beta Tritium Radium-226,-228 Plutonium Iodine-131, Iodine-12 9b Uranium-238, Nickel-63b Technetium_99b Iron-55b Attachment A ACCEPTANCE CRITERIA FOR 'SPIKED' SAMPLES ISION: ONE STANDARD DEVIATION VALUES FOR VARIOUS ANALYSESa One standard deviation Level for single determination 5 to 100 pCi/liter or kg 5.0 pCi/liter
> 100 pCi/liter or kg 5% of known value 5 to 50 pCi/liter or kg 5.0 pCi/liter
> 50 pCi/liter or kg 10% of known value 2 to 30 pCi/liter or kg 5.0 pCi/liter
> 30 pCi/liter or kg 10% of known value
> 0.1 gAiter or kg 5% of known value 20 pCi/liter 5.0 pCi/liter
> 20 pCi/liter 25% of known value 100 pCi/liter 5.0 pCi/liter
> 100 pCi/liter 5% of known value 4,000 pCi/liter 1 s = (pCi/liter) =
169.85 x (known) 0,033
> 4,000 pCi/liter 10% of known value 0.1 pCi/liter 15% of known value 0.1 pCi/liter, gram, or sample 10% of known value 55 pCi/liter 6.0 pCi/liter
> 55 pCi/liter 10% of known value 35 pCi/liter 6.0 pCi/liter
> 35 pCi/liter 15% of known value 50 to 100 pCi/liter
> 100 pCiliter 10 pCi/liter 10% of known value Othersb 20% of known value a From EPA publication, Environmental Radioactivity Laboratory Intercompanson Studies Program, Fiscal Year, 1981-1982, EPA-600/4-81-004.
b Laboratory limit.
A2
TABLE A-1. Interlaboratory Comparison Crosscheck program, Environmental Resource Associates (ERA)a.
Concentration (pCi/L)
Lab Code Date Analysis Laboratory ERA Control Resultb Result' Limits STW-940 STW-940 STW-942 STW-942 STW-944 STW-944 STW-944 STW-944 STW-944 STW-944 STW-944 STW-944 STW-951 STW-951 STW-951 STW-951 STW-952 STW-952 STW-952 STW-952 STW-952 STW-952 STW-953 d STW-954 STW-965 STW-965 STW-965 STW-965 STW-965 STW-965 STW-965 STW-965 STW-965 STW-965 STW-965 STW-965 STW-966 STW-966 STW-967 STW-968 STW-968 STW-968 STW-969 02120102 02120/02 02/20102 02/20102 02/20102 02/20/02 02/20102 02/20102 02/20102 02/20/02 02/20/02 02/20102 05/22/02 05/22/02 05/22/02 05/22/02 05122/02 05/22/02 05/22/02 05/22102 05122/02 05/22/02 05/22/02 05122102 08121102 08/21/02 08/21/02 08/21/02 08/21/02 08/21/02 08/21/02 08121/02 08/21/02 08/21/02 08/21/02 08/21/02 11/20/02 11/20/02 11/20/02 11/20/02 11/20/02 11/20/02 11/20/02 Sr-89 Sr-90 Gr. Alpha Gr. Beta Ba-1 33 Co-60 Cs-134 Cs-1 37 Ra-226 Ra-228 Uranium Zn-65 Gr. Alpha Ra-226 Ra-228 Uranium Co-60 Cs-134 Cs-1 37 Gr. Beta Sr-89 Sr-90 H-3 1-131 Ba-133 Co-60 Cs-134' Cs-137 Gr. Alpha Gr. Beta Ra-226 Ra-228 Sr-89 Sr-90 Uranium Zn-65 Gr. Alpha Gr. Beta H-3 Ra-226 Ra-228 Uranium 1-131 53.0 +/- 2.5 16.6 i 0.5 6.5 + 0.6 45.7 +/- 3.1 25.8 +/- 1.5 76.9 +/- 2.7 38.7 +/- 1.6 92.9 +/- 2.7 15.3 +/- 0.7 17.5 +/-0.4 23.8 +/- 1.1 361.0 +/- 9.2 23.9 +/- 2.5 5.9 +/- 0.5 5.6 +/- 0.9 7.6 +/- 0.2 37.9 +/- 0.7 14.5 +/- 0.8 50.0 +/- 2.0 171.0 +/-2.5 28.4 +/-4.8 32.4 +/- 3.1 13900.0 +/- 100.0 14.6 +/- 0.3 71.9 +/- 2.1 23.8 +/- 1.0 62.9 +/- 1.2 219.3 +/- 10.7 74.4 +/- 0.6 26.7 +/- 0.4 5.0 +/- 0.5 6.0 +/- 0.7 28.4 +/- 1.5 36.5 i 1.1 4.1 i0.1 92.4 +/- 2.2 9.3 +/-0.4 44.7 +/- 1.0 10100.0 +/- 38.7 11.6 +/-0.1 16.0 +/- 1.4 15.5 +/- 0.5 6.0 +/- 0.4 55.3 +/- 5.0 15.9 i5.0 8.0 +/-5.0 48.3 i 5.0 28.9 i 5.0 73.4 +/- 5.0 42.1 +/- 5.0 88.8 +/- 5.0 14.3 +/-2.2 16.9 +/-4.2 28.3 +/- 3.0 359.0 +/- 35.9 22.8 +/- 5.7 6.1 +/-0.9 4.5 +/- 1.1 9.3 +/- 3.0 39.1 +/- 5.0 17.1 +/-5.0 52.1 +/-5.0 189.0 +/- 28.4 31.7 +/- 5.0 28.3 +/- 5.0 17400.0 +/- 1740.0 14.7 +/- 2.0 80.0 +/- 8.0 23.3 +/- 5.0 71.7 +/- 5.0 214.0 i 10.7 58.8 + 14.7 21.9 +/- 2.2 5.0 +/- 0.8 4.7 +/- 1.2 29.0 +/- 5.0 36.4 +/- 5.0 5.0 +/- 3.0 95.7 +/- 9.6 12.2 +/- 5.0 47.0 +/- 5.0 10200.0 +/- 1020.0 12.1 +/-1.8 15.1 +/-3.8 19.2 +/- 3.0 6.8 +/- 2.0 46.6 - 64.0 7.2 - 24.6 0.0 -16.7 39.6 - 57.0 20.2 - 37.6 64.7 - 82.1 33.4 - 50.8 80.1 - 97.5 10.6 - 18.0 9.6 - 24.2 23.1 - 33.5 298.0 - 420.0 13.0 - 32.6 4.5 - 7.7 2.6 - 6.5 4.1 - 14.5 30.4 - 47.8 8.4 - 25.8 43.4 - 60.8 140.0 - 238.0 23.0 -40.4 19.6 - 37.0 14400.0 - 20400.0 11.2 - 18.2 66.4 - 93.6 14.6 - 32.0 63.0 - 80.4 195.0 - 233.0 33.5 - 84.1 13.2 - 30.6 3.7 -6.3 2.7 - 6.7 20.3 - 37.7 27.7 - 45.1 0.0 - 10.2 79.4 - 112.0 3.5 - 20.9 38.3 - 55.7 8440.0 - 12000.0 9.0 - 15.2 8.6 - 21.6 14.0 - 24.4 3.3 - 10.2 Al-1
TABLE A-1. Interlaboratory Companson Crosscheck program, Environmental Resource Associates (ERA)a.
Concentration (pCUL)
Lab Code Date Analysis Laboratory ERA Control Resultb Resultc Limits STW-970 11/20/02 Co-60 104.0 +/- 7.1 104.0 +/- 5.2 95.0 - 113.0 STW-970 11/20/02 Cs-134 48.2 +/-2.3 55.5 +/-5.0 46.8 -64.2 STW-970 11/20/02 Cs-1 37 109.0 +/- 12.6 117.0 +/- 5.9 107.0 - 127.0 STW-970 11/20102 Gr. Beta 252.0 +/-26.8 288.0 +/- 49.5 244.0 -416.0 STW-970 11/20/02 Sr-89 43.2 +/- 0.7 47.6 +/- 5.0 38.9 - 56.3 STW-970 11/20/02 Sr-90 7.5 +/- 0.2 7.6 +/- 5.0 0.0 - 16.2 STW-971 11/20/02 Gr. Alpha 74.9 +/- 1.5 103.0 +/- 25.8 58.4 - 148.0 STW-971 11/20102 Ra-226 8.9 +/-0.0 9.1 +/- 1.4 6.7 -11.5 STW-971 11/20/02 Ra-228 15.3 +/-0.1 17.8 +/-4.5 10.1 -25.5 STW-971 11/20/02 Uranium 51.7 +/- 1.6 61.7 +/- 6.2 51.0 - 72.4 a Results obtained by Environmental, Inc., Midwest Laboratory as a participant in the environmental samples crosscheck program operated by Environmental Resources Associates (ERA).
b Unless otherwise indicated, the laboratory result is given as the mean +/- standard deviation for three determinations.
c Results are presented as the known values, expected laboratory precision (1 sigma, 1 determination) and control limits as provided by ERA.
d Analysis was repeated; result of reanalysis: 16114+/-487 pCi/L.
° ERA acknowledged an unacceptably high percentage of failure for Cs-1 34 and questioned its own control limits.
No problems were identified in the analysis.
A1-2
TABLE A-2. Crosscheck program results; Thermoluminescent Dosimetry, (TLDs).
mR Lab Code TLD Type Date Measurement Known Lab Result Control Value
+/- 2 sigma Limits Environmental. Inc.
2001-1 2001-1 2001-1 2001-1 2001-1 2001-1 2001-1 2001-1 CaSO4: Dy Cards CaSO4: Dy Cards CaSO4: Dy Cards CaSO4: Dy Cards CaSO4: Dy Cards CaSO4: Dy Cards CaSO4: Dy Cards CaSO4: Dy Cards 1212412001 12124/2001 12/24/2001 12/2412001 12/24/2001 12/24/2001 12/24/2001 12/24/2001 Reader Reader Reader Reader Reader Reader Reader Reader 1, #1 1,#1 1, #2 1, #2 1, #3 1, #3 1.#4 1.#4 3.98 3.98 7.07 7.07 15.9 15.9 63.61 63.61 3.71 +/- 0.12 3.38 +/- 0.09 7.89 +/- 0.18 7.64 +/- 0.25 18.62 +/- 0.40 19.58 +/- 0.12 78.24 +/- 1.23 79.89 +/- 2.47 2.79 - 5.17 2.79 - 5.17 4.95 - 9.19 4.95 - 9.19 11.13 - 20.67 11.13 -20.67 44.53 - 82.69 44.53 - 82.69 Environmental. Inc.
2002-1 CaSO4: Dy Cards 2002-1 CaSO4: Dy Cards 2002-1 CaSO4: Dy Cards 2002-1 CaSO4: Dy Cards 2002-1 CaSO4: Dy Cards 2002-1 CaSO4: Dy Cards 2002-1 CaSO4: Dy Cards 2002-1 CaSO4: Dy Cards 5128/2002 5/28/2002 5128/2002 5128/2002 5/28/2002 5/28/2002 5/28/2002 5/28/2002 Reader 1, #1 Reader 1, #1 Reader 1, #2 Reader 1. #2 Reader 1, #3 Reader 1, #3 Reader 1, #4 Reader 1, #4 4.84 4.84 8.60 8.60 19.34 19.34 77.36 77.36 4.44 +/- 0.16 4.37 +/- 0.20 9.08 +/- 0.14 8.76 +/- 0.16 22.14 +/- 0.27 24.03 +/- 0.30 92.77 +/- 0.58 85.25 +/- 0.37 3.39 3.39 6.02 6.02
- 6.29
-6.29
- 11.18
- 11.18 13.54 - 25.14 13.54 - 25.14 54.15 - 100.57 54.15 - 100.57 Environmental. Inc.
2002-2 CaSO4: Dy Cards 2002-2 CaSO4: Dy Cards 12/13/2002 Reader 1, 30 12113/2002 Reader 1,45a 56.73 25.21 71.61 +/- 1.79 33.49 +/- 1.38 39.71 - 73.75 17.65 - 32.77 a Precision of the distance (cm) measurement can significantly increase the error. The placement of the card holder 2002-2002-2002-2002-2002-2002-on the table could account for the higher error.
-2 CaSO4: Dy Cards 12113/2002 Rea(
-2 CaSO4: Dy Cards 12/13/2002 Rea(
.2 CaSO4: Dy Cards 12/13/2002 Rea(
.2 CaSO4: Dy Cards 12113/2002 Rea(
-2 CaSO4: Dy Cards 12113/2002 Rea(
.2 CaSO4: Dy Cards 12113/2002 Rea der 1, 60 der 1, 75 der 1, 90 Jer 1, 120 Jer 1, 135 Jer 1, 150 14.18 9.08 6.30 3.55 2.80 2.28 17.37 +/- 1.24 10.65 +/- 1.02 6.37 +/- 0.54 4.60 +/- 0.41 2.51 +/- 0.23 2.22 +/- 0.28 9.93 - 18.43 6.36 - 11.80 4.41 - 8.19 2.49 - 4.62 1.96 - 3.64 1.60 - 2.96 c Control limits are based on Attachment A, Page A2 of this report.
A2-1
TABLE A-3. In-House 'Spike" Samples Concentration (pCi/L)a Lab Code Sample Date Analysis Laboratory results Known Control Type 2s, n=1b Activity Limitsc SPW-1 1552 SPW-11552 SPMI-595 SPMI-595 SPMI-597 SPMI-597 SPMI-597 SPAP-594 SPW-599 SPMI-1446 SPW-1446 SPW-1446 SPMI-1448 SPVE-1444 SPAP-2078 SPW-2080 SPF-2082 SPF-2082 SPMI-2084 SPMI-2084 SPMI-2084 SPMI-2084 SPMI-2084 SPW-2115 SPW-2116 SPW-2116 SPW-2116 SPW-2116 SPW-2116 SPW-2019 SPW-2019 SPCH-3064 SPW-4682 SPAP-4685 W-71702S W-71702S W-71702S SPVE-491 0 W-72302S W-80102S W-80102S W-80202S SPW-7188 SPW-7190 Water Water Milk Milk Milk Milk Milk Air Filter Water Milk Water Water Milk Vegetation Air Filter Water Fish Fish Milk Milk Milk Milk Milk Water Water Water Water Water Water Water Water Charcoal Water Air Filter Water Water Water Vegetation Water Water Water Water Water Water 1/7/2002 1/7/2002 1/31/2002 1/31/2002 1/31/2002 1/31/2002 1/31/2002 2/6/2002 2/19/2002 3/8/2002 3/8/2002 3/8/2002 3/8/2002 3/11/2002 4/8/2002 4/5/2002 4/5/2002 4/5/2002 4/8/2002 4/8/2002 4/8/2002 4/8/2002 4/8/2002 4/8/2002 4/8/2002 4/8/2002 4/8/2002 4/8/2002 4/8/2002 5/3/2002 5/3/2002 5/11/2002 7/17/2002 7/17/2002 7/17/2002 07/17/02 07/17/02 07/22/02 07/23/02 08/01/02 08/01/02 08/02/02 10/25/02 10/25/02 Gr. Alpha Gr. Beta Cs-134 Cs-1 37 Co-60 Cs-1 34 Cs-1 37 Gr. Beta H-3 1-131 (G) 1-131 1-131 (G) 1-131 1-131 (G)
Gr. Beta H-3 Cs-134 Cs-137 Cs-134 Cs-137 1-131 1-131 (G)
Sr-90 1-131 Co-60 Cs-1 34 Cs-137 1-131 (G)
Sr-90 Gr. Alpha Gr. Beta 1-131 (G)
H-3 Gr. Beta Fe-55 H-3 Ni-63 Sr-90 Sr-90 Gr. Alpha Gr. Beta Tc-99 Fe-55 Ni-63 35.33 +/- 1.83 112.62 +/- 2.44 29.63 +/- 4.98 51.31 +/- 7.55 44.18 +/- 7.76 20.15 +/- 5.08 54.88 +/- 8.32 1.58 +/- 0.02 47607 +/- 595 87.84 +/- 11.47 82.98 +/- 1.20 92.75 +/- 12.87 88.00 +/- 1.13 0.39 +/- 0 04 1.43 +/- 0.01 49121 +/-608 0.83 +/- 0.04 1.29 +/- 0.07 20.93 +/- 5.82 51.83 +/- 10.23 87.72 +/- 1.28 84.08 +/- 10.75 62.81 +/- 1.99 82.42 +/- 1.27 32 47 +/- 5.78 30.80 +/- 3.60 53.85 +/- 7.07 79.09 +/- 7.58 70.35 +/- 2.32 25.89 +/- 1.71 101.19 +/-2.37 0.74 +/- 0.04 40856 +/- 548 1.58 +/- 0.02 10463.00 +/- 126.00 45779 +/- 583 17.02 +/- 1.50 10.22 +/- 0.80 21.43 +/- 0.97 41.25 +/- 4.58 113.66 +/- 5.30 16.39 +/- 0.72 20396 +/- 265 227.18 +/- 11.60 34.57 107.70 27.10 50.89 41.36 22.59 50.89 1.55 50189 85 20 85.20 85.20 85.20 0.42 1.55 46912 0.83 1.35 24.69 50.56 88.37 88.37 66 85 88 37 33.09 28.80 50.56 88 37 66.85 34.57 107.70 0.85 46179 1.55 12200.60 46179 17.10 9.04 26.55 34.45 107.70 14.13 22778 170.80 17.29 - 51.86 96.93 - 118.47 17.10 - 37.10 40.89 - 60.89 31.36 - 51.36 12.59 - 32.59 40 89 - 60.89 0.00 - 11.55 40151 -60227 75 20 - 95.20 68.16 - 102.24 75.20 - 95.20 68.16 - 102.24 0.25 - 0.58 0 00 - 11.55 37530 - 56294 0.50 - 1.16 0.81 - 1.89 14.69 - 34.69 40.56 - 60.56 70.70 - 106.04 78.37 - 98.37 53 48 - 80.22 70.70 - 106.04 23.09 - 43.09 18.80 - 38.80 40.56 - 60.56 78.37 - 98.37 53.48 - 80.22 17.29 - 51.86 96.93 - 118.47 0.51 - 1.18 36943 -55415 0.00 - 11.55 9760.48 - 14640.72 36943 - 55415 10.26 - 23.94 0.00 - 19.04 16.55 - 36.55 17.23 - 51.68 96.93 - 118 47 2.13 - 26.13 18222 -27334 102.48 - 239.12 A3-1
TABLE A-3. In-House "Spike" Samples Concentration (pCi/L)
Lab Code Sample Date Analysis Laboratory results Known Control Type 2s, n=1 b Activity Limitsc SPW-7192 Water 10125102 H-3 96310 +/- 871 90963 72770 -109156 SPW-7194 Water 10125/02 C-14 42938 +/- 167 49661 29796 - 69525 SPAP-7198 Air Filter 10125/02 Gr. Beta 1.65 +/- 0.02 1.53 0.00 - 11.53 SPW-7335 Water 10/30/02 Co-60 39.67 +/- 7.38 37.05 27.05 -47.05 SPW-7335 Water 10/30/02 Cs-134 33.09 +/- 5.96 34.11 24.11 -44.11 SPW-7335 Water 10/30/02 Cs-1 37 46.80 +/- 10.39 49.90 39.90 - 59.90 SPMI-7336 Milk 10/30/02 Cs-134 34.40 +/- 4.99 34.11 24.11 -44.11 SPMI-7336 Milk 10/30/02 Cs-1 37 46.52 +/- 8.52 49.91 39.91 - 59.91 SPF-7340 Fish 10/30/02 Cs-134 0.66 +/- 0.03 0.68 0.41 - 0.95 SPF-7340 Fish 10/30/02 Cs-137 1.35 +/- 0.05 1.33 0.80 - 1.86 SPS-8102 Sediment 11/01/02 Sr-90 14.69 +/- 0.67 13.45 3.45 -23.45 a Results are reported in units of pCi/L, except for air filters (pCi/Filter), food products, vegetation, soil, sediment (pCi/g).
b Results are based on single determinations.
c Control limits are based on Attachment A, Page A2 of this report NOTE. For fish, Jello is used for the Spike matrix. For Vegetation, cabbage is used for the Spike matrix.
A3-2
TABLE A-4. In-House "Blank" Samples Concentration (pCi/L)a Lab Code Sample Date Analysis Laboratory results (4.66a)
Acceptance Type LLD Activityb Criteria (4.66 ca)
SPW-1 1551 SPW-11551 SPAP-590 SPAP-590 SPAP-590 SPAP-590 SPMI-596 SPMI-596 SPMI-596 SPMI-596 SPW-598 SPW-598 SPW-598 SPW-600 SPMI-1447 SPVE-1443 SPW-1445 SPW-1445 SPW-1445 SPW-1445 SPW-1445 SPMI-1447 SPAP-2077 SPW-2079 SPF-2081 SPF-2081 SPMI-2083 SPMI-2083 SPMI-2083 SPMI-2083 SPW-2115 SPW-2115 SPW-2115 SPW-2115 SPW-2115 SPW-2115 SPW-2018 SPW-2018 SPch-3063 SPW-4683 W-71702 W-71702 W-71802B W-71802B water water Air Filter Air Filter Air Filter Air Filter Milk Milk Milk Milk water water water water Milk Vegetation water water water water water Milk Air Filter water Fish Fish Milk Milk Milk Milkc water water water water water water water water Charcoal water water water water water 1/72002 11712002 1/31/2002 1/31/2002 1/31/2002 1/31/2002 1/31/2002 1/31/2002 1/31/2002 1/31/2002 1/31/2002 1131/2002 1/31/2002 1/31/2002 3/7/2002 3/8/2002 31812002 3/8/2002 3/8/2002 3/8/2002 3/8/2002 3/8/2002 4/812002 4/512002 415/2002 41512002 4/8/2002 418/2002 4/812002 4/8/2002 4/8/2002 4/8/2002 41812002 418/2002 41812002 4/8/2002 4/22/2002 4/22/2002 5/11/2002 7/17/2002 7/17/2002 7/17/2002 7/18/2002 7/18/2002 Gr. Alpha Gr. Beta Co-60 Cs-1 34 Cs-1 37 Gr. Beta Co-60 Cs-1 34 Cs-1 37 K-40 Co-60 Cs-1 34 Cs-1 37 H-3 1-131 (G) 1-131 (G)
Co-60 Cs-1 34 Cs-1 37 1-131 1-131(G) 1-131 Gr. Beta H-3 Cs-1 34 Cs-1 37 Cs-134 Cs-137 1-131 Sr-90 Co-60 Cs-134 Cs-137 1-131 1-131 (G)
Sr-90 Gr. Alpha Gr. Beta 1-131 (G)
H-3 Fe-55 Ni-63 Gr. Alpha Gr. Beta 0.47 1.37 1.78 3.42 2.33 0.74 3.54 3.24 3.89 2.30 3.74 3.23 138.80 7.63 0.02 2.76 2.87 4.34 0.45 6.50 0.31 0.32 134.17 7.67 9.54 2.90 3.03 0.52 0.48 1.49 2.09 3.78 0.50 3.30 0.66 0.56 1.38 8.27 129.00 33.61 2.56 0.48 1.33 0.45 i 0.39 0.55 +/- 1.03
-0.096 +/- 0.38 1472.1 +/- 101.50
-96.5 +/- 63.40 0.17 +/- 0.31 0.15 +/- 0.22
-0.055 +/- 0.19 16.13 +/- 67.39
-0.38 +/- 0.34 1.29 +/- 0.36
-0.16 +/- 0.33 0.10 +/- 0.32
-0.24 +/- 0.38 3.19 +/- 1.03
-62.8 +/- 60.30
-1.72 +/- 15.63 0.71 +/- 1.37 0.31 +/- 0.36 0.9 +/- 0.95 1
3.2 100 100 100 3.2 10 10 10 0
10 10 10 200 20 20 10 10 10 0.5 20 0.5 3.2 200 100 100 10 10 0.5 1
10 10 10 0.5 20 1
1 3.2 9.6 200 1000 20 1
3.2 A4-1
TABLE A-4. In-House "Blank" Samples Concentration (pCi/L)a Lab Code Sample Date Analysis Laboratory results (4.66a)
Acceptance Type LLD Activityb Criteria (4.66 or)
W-72302 water 7/23/2002 Sr-90 0.27 0.027 +/- 0.13 1
W-80202 water 8/2/2002 Tc-99 0.34
-0.051 +/- 0.16 10 SPW-7189 water 10/25/2002 Fe-55 978.21 21.77 + 595.33 1000 SPW-7191 water 10/25/2002 Ni-63 11.74 4.47 +/- 7.24 20 SPW-7193 water 10/25/2002 H-3 146.00
-92 +/- 65.00 200 SPAP-7199 Air Filter 10/25/2002 Gr. Beta 0.00
-0.0024 +/- 0.00 3.2 SPMI-7333 Milk 10/30/2002 Cs-134 5.30 10 SPMI-7333 Milk 10130/2002 Cs-137 4.80 10 SPW-7334 water 10/30/2002 Co-60 3.69 10 SPW-7334 water 1013012002 Cs-1 34 5.37 10 SPW-7334 water 10/30/2002 Cs-137 3.90 10 SPF-7339 Fish 10/30/2002 Cs-134 4.69 100 SPF-7339 Fish 10/30/2002 Cs-137 11.18 100 a Uquid sample results are reported in pCVUter, air filters( pCi/filter), charcoal (pCi/charcoal canister), and solid samples (pCi/kg).
b The activity reported is the net activity result.
c Low levels of Sr-90 are still detected in the environment A concentration of (1-5 pCiIL) in milk is not unusual.
A4-2
TABLE A-5. In-House "Duplicate" Samples Concentration (pCUL)a Averaged Lab Code Date Analysis First Result Second Result Result CF-20,21 CF-20, 21 CF-20,21 CF-20,21 AP-11804, 11805 AP-11825,11826 AP-11846,11847 WW-150,151 MI-124,125 W-172,173 SW-11698. 11699 SW-11698,11699 U-275,276 LW-356, 357 LW-377,378 SW-525,526 SW-525,526 DW-504.505 MI-649,650 DW-697, 698 DW-927, 928 W-973,974 W-1673,1674 SWT-1395,1396 MI-1268,1269 Ml-1268,1269 MI-1332,1333 MI-1332,1333 MI-1458,1459 DW-10100, 10101 DW-10111, 10112 Ml-1521.1522 MI-1521,1522 Ml-1541,1542 MI-1541,1542 LW-1651,1652 DW-10134,10135 WW-1694,1695 SO-1715,1716 SO-1715,1716 DW-10302,10303 W-1758,1759 W-1758,1759 1/2/2002 1/2/2002 1/212002 1/2/2002 1/2/2002 1/212002 1/2/2002 1/7/2002 1/8/2002 1/8/2002 1/8/2002 1/8/2002 1/1012002 1/16/2002 1/16/2002 1130/2002 1/30/2002 1/31/2002 2/5/2002 2/612002 21812002 2/18/2002 2/25/2002 2126/2002 2127/2002 2/27/2002 3/5/2002 315/2002 3/6/2002 3/9/2002 3/9/2002 3/11/2002 3/11/2002 3/11/2002 3/11/2002 3114/2002 3/16/2002 3118/2002 3/19/2002 3/19/2002 3/2012002 3/25/2002 3/25/2002 Be-7 Gr. Beta K-40 Sr-90 Be-7 Be-7 Be-7 Gr. Beta K-40 H-3 Gr. Alpha Gr. Beta Gr. Alpha Gr. Beta Gr. Beta Gr. Alpha Gr. Beta Gr. Alpha K-40 Gr. Beta Sr-90 Fe-55 H-3 Gr. Beta K40 Sr-90 K-40 Sr-90 K-40 Gr. Alpha Gr. Alpha K-40 Sr-90 K-40 Sr-90 Gr. Beta Gr. Alpha Gr. Beta Cs-137 Gr. Beta Gr. Alpha Gr. Alpha Gr. Beta 0.47 +/- 0.25 7.82 +/- 0.20 6.65 +/- 0.55 0.01 +/-0.01 0.054 +/- 0.011 0.053 +/- 0.013 0.054 +/-0.018 1.26 +/- 0.50 1332.30 +/- 158.90 153.00 +/- 68.00 2.51 +/- 1.36 7.68 +/- 1.33 1.40 +/- 1.00 3A7 +/- 0.65 2.75 +/- 0.68 0.56 +/- 0.35 2.29 +/- 0.41 2.30 +/- 1.70 1319A0 +/- 176.70 5.10 +/- 1.20 0.69 +/- 0.29 7.29 +/- 0.97 2640.00 +/- 155.00 2.96 +/- 0.59 1460.50 +/- 162.50 0.77 +/- 0.36 1503.00 +/- 164.00 1.35 +/- 0.38 1411.70 +/- 166.70 4.10 +/- 1.70 7.10 +/- 2.00 1270.80 +/- 103.30 1.69 +/- 0.46 1562.20 +/- 122.80 0.85 +/- 0.57 2.90 +/- 0.57 5.60 +/- 1.90 1.79 +/- 0.59 0.03 +/- 0.01 18.50 +/- 1.70 2.30 +/- 1.40 2.50 +/- 0.70 4.10 +/- 1.20 0.37 +/- 0.12 7.95 +/- 0.21 6.53 +/- 0.36 0.01 +/- 0.01 0.049 +/- 0.019 0.043 +/- 0.013 0.048 +/- 0.016 1.04 1271.70 148.00 3.71 8.49 1.10
+/- 0.46
+/- 151.50
+/- 68.00
+/- 1.80
+/- 1.43
+/-1.20 2.94 +/- 0.61 2.84 +/- 0.61 0.24 +/- 0.35 2.58 +/- 0.39 3.90 +/- 1.40 1210.80 +/- 118.20 4.70 +/- 1.20 0.71 +/-0.29 6.86 +/- 0.94 2908.00 +/- 161.00 2.29 +/- 0.53 1573.00 +/- 168.00 0.95 +/- 0.40 1305.00 +/- 168.00 1.07 +/-0.40 1390.00 i 172.30 1.80 +/-*1.60 8.30 +/- 2.30 1369.10 +/- 121.60 2.46 +/- 0.49 1529.30 +/- 126.10 1.48 +/- 0.43 2.57 +/- 0.56 5.40 +/- 1.60 1.53 +/- 0.50 0.02 +/- 0.01 19.10 +/- 1.70 3.30 +/- 1.60 2.30 +/- 0.60 2.50 +/- 1.10 0.42 +/- 0.14 7.89 +/- 0.14 6.59 +/- 0.33 0.01 +/- 0.00 0.052 +/- 0.011 0.048 +/- 0.009 0.051 +/- 0.012 1.15 +/-0.34 1302.00 +/- 109.77 150.50 +/- 48.08 3.11 +/- 1.13 8.09 +/- 0.98 1.25 +/- 0.78 3.21 +/- 0.45 2.79 +/- 0.46 0.40 +/- 0.25 2.43 +/- 0.28 3.10 +/- 1.10 1265.10 +/- 106.29 4.90 +/- 0.85 0.70 +/- 0.21 7.08 +/- 0.68 2774.00 +/- 111.74 2.63 +/- 0.40 1516.75 +/- 116.87 0.86 +/- 0.27 1404.00 +/- 117.39 1.21 +/- 0.28 1400.85 +/- 119.87 2.95 +/- 1.17 7.70 +/- 1.52 1319.95 +/- 79.78 2.07 +/- 0.34 1545.75 +/- 88.01 1.16 +/- 0.36 2.74 +/- 0.40 5.50 +/- 1.24 1.66 +/- 0.39 0.03 +/- 0.01 18.80 +/- 1.20 2.80 +/- 1.06 2.40 i 0.46 3.30 i 0.81 A5-1
TABLE A-5. In-House "Duplicate" Samples Concentration (pCUL)a Averaged Lab Code Date Analysis First Result Second Result Result MI-1926, 1927 MI-1926,1927 SWU-2010, 2011 DW-10376, 10377 AP-2479, 2480 DW-10395, 10396 LW-2181, 2182 LW-2181, 2182 CW-2437, 2438 CW-2437. 2438 MI-1947, 1948 AP-2458, 2459 DW-10409,10410 MI-2052, 2053 MI-2052, 2053 AP-2711, 2712 W-938, 939 SS-2202, 2203 SS-2202, 2203 F-2307, 2308 DW-10476,10477 W-2244, 2245 DW-10509, 10510 SW-2690, 2691 SO-2903, 2904 SO-2903, 2904 SO-2903. 2904 DW-10562, 10563 DW-10578, 10579 SO-2861, 2862 SO-2861, 2862 SL-2819, 2820 SL-2819, 2820 SL-2819, 2820 SL-2840, 2841 SL-2840, 2841 SL-2840, 2841 MI-2971, 2972 MI-2971, 2972 DW-10603, 10604 SS-3037. 3038 MI-3124, 3125 MI-3208, 3209 LW-3250, 3251 3/26/2002 3/26/2002 3/2612002 3/27/2002 3/28/2002 312912002 3131/2002 313112002 313112002 3t3112002 4/112002 4/11/2002 411/2002 4/3/2002 4/3/2002 4/3/2002 4/9/2002 4/9/2002 4/9/2002 4/10/2002 4/12/2002 4/15/2002 4/17/2002 4/24/2002 4/24/2002 4/2412002 4/24/2002 4/24/2002 4/29/2002 4/30/2002 4/30/2002 5/1/2002 5/112002 5/112002 5/1t2002 5/11/2002 5/1/2002 5/5/2002 5/512002 516/2002 5/9/2002 5/13/2002 5/14/2002 5/15/2002 K-40 Sr-90 Gr. Beta Gr. Beta Be-7 Gr. Alpha Gr. Beta H-3 Gr. Beta H-3 K-40 Be-7 Gr. Alpha K-40 Sr-90 Be-7 Ni-63 Gr. Beta K-40 K-40 Gr. Alpha Gr. Beta Gr. Alpha Gr. Beta Be-7 Cs-137 K-40 Gr. Alpha Gr. Alpha Cs-137 K-40 Be-7 Gr. Beta K-40 Be-7 Gr. Beta K-40 K-40 Sr-90 Gr. Alpha K-40 K-40 K-40 Gr. Beta 1414.00 +/- 115.00 2.30 +/- 0.70 2.90 +/- 0.60 10.50 +/- 1.30 0.064 +/- 0.023 10.20 +/-2.10 2.98 +/- 0.68 2694.43 +/- 156.53 1.09 +/- 0.61 6456.70 +/- 229.20 1421.40 +/- 130.90 0.077 +/- 0.011 39.30 +/- 4.00 1283.70 +/- 103.20 0.81 +/- 0.36 0.071 +/- 0.01 1.73 +/- 0.10 5.83 +/- 1.16 5.75 +/- 0.48 2.75 +/- 0.27 5.10 +/- 1.30 1.70 +/- 1.10 6.00 +/- 2.00 2.25 +/- 0.68 1.22 +/- 0.57 0.13 +/- 0.05 21.06 +/- 1.48 2.17 +/- 1.13 8.20 +/- 2.20 236.40 +/- 46.00 10191.00 +/-784.60 805.70 +/- 301.50 5566.00 +/- 124.00 5524.00 +/- 632.90 1010.00 +/- 352.10 4399.00 +/- 221.80 2422.80 +/- 352.10 1338.90 +/- 83.44 0.83 +/- 0.47 6.30 +/- 1.70 11585.00 +/- 749.00 1329.50 +/- 103.80 1494.60 +/- 158.40 3.14 +/- 0.55 1316.00 +/- 128.00 2 40
- 0.70 2.20 +/- 0.50 10.10 +/- 1.50 0.068 +/- 0.014 14.60 +/- 2.40 1.99 +/- 0.70 2688.84 +/- 156.40 1.14 +/- 0.58 6292.80 +/- 226.52 1256.80 +/- 104.20 0.081 +/- 0.010 35.30 +/- 3.60 1434.80 +/- 147.90 0.75 +/- 0.35 0.07 +/- 0.01 1.82 +/- 0.10 5.52 +/- 1.19 6.11 +/-0.51 2A9 +/- 0.32 3.90 +/- 1.60 1.60 +/- 1.00 7.30 +/- 1.80 2.15 +/- 0.59 0.78 i 0.43 0.09 i 0.05 19.91 +/- 1.16 3.25 i 1.54 7AO +/- 2.00 200.70 i 52.60 11025.00 i 941.30 860.73 +/- 164.80 5359.00 +/- 122.00 5277.50 +/-431.40 872.95 +/- 181.70 4593.00 +/- 276.00 2254.10 i371.40 1345.80 i 100.90 1.65 i OA6 5.50 +/- 1.60 11612.00 i787.00 1373.00 i 107.40 1462.60 i 182.50 3.28 i 0.63 1365.00 +/- 86.04 2.35 +/- 0.49 2.55 +/- 0.39 10.30 +/- 0.99 0.066 +/- 0.013 12.40 +/- 1.59 2.48 +/- 0.49 2691.64 +/- 110.64 1.11 +/- 0.42 6374.75 i 161.12 1339.10 +/- 83.65 0.079 i 0.008 37.30 +/- 2.69 1359.25 +/- 90.17 0.78 +/- 0.25 0.07 +/- 0.01 1.78 +/- 0.07 5.67 +/- 0.83 5.93 i 0.35 2.62 i 0.21 4.50 +/- 1.03 1.65 +/- 0.74 6.65 +/- 1.35 2.20 +/- 0.45 1.00 +/- 0.36 0.11 +/- 0.04 20.48 +/- 0.94 2.71 +/- 0.96 7.80 +/- 1.49 218.55 +/- 34.94 10608.00 +/- 612.71 833.22 +/- 171.80 5462.50 +/- 86.98 5400.75 +/- 382.97 941.48 +/- 198.11 4496.00 +/- 177.04 2338.45 +/- 255.89 1342.35 i 65.47 1.24 i 0.33 5.90 +/- 1.17 11598.50 i 543.22 1351.25 i 74.68 1478.60 +/- 120.83 3.21 +/-0.42 A5-2
TABLE A-5. In-House 'Duplicate" Samples Concentration (pCVIL)a Averaged Lab Code Date Analysis First Result Second Result Result CF-3292, 3293 MI-3376,3377 MI-3418,3419 SWT-3461, 3462 S0-3503,3504 S0-3503,3504 S0-3503,3504 SL-3545, 3546 SL-3545, 3546 DW-10754,10755 SW-3777, 3778 SW-3777, 3778 MI-3798, 3799 LW-3924, 3925 MI-3966, 3967 MI-3966, 3967 MI-3987, 3988 MI-4095,4096 SWU-4221,4222 LW-4179,4180 G-4329,4330 G-4329,4330 G-4329, 4330 SL-4337,4338 SL-4337,4338 SL-4337,4338 SL-4337,4338 AP-4864,4865 MI-4359,4360 AP-4569,4570 AP-4843,4844 AP-4789,4790 SWU-4810,4811 MI-4548,4549 DW-4737,4738 MI-4632,4633 MI-5054, 5055 G-5075,5076 SWU-5124, 5125 G-5151, 5152 G-5151, 5152 MI-5103, 5104 LW-5434,5435 MI-5215, 5216 5/2012002 5126/2002 5128/2002 5/2812002 5/2912002 5/2912002 5/29/2002 61312002 61312002 6/6/2002 6/111/2002 6/1112002 611112002 6/1312002 6/1812002 6/1812002 6119/2002 6/2512002 6/2512002 6/27/2002 7/1/2002 7/1/2002 7/1/2002 7/1/2002 7/1/2002 7/1/2002 7/11/2002 7/1/2002 7/2/2002 7/212002 7/212002 7/3/2002 7/3/2002 7/912002 7/12/2002 7/1512002 7/3012002 7/30/2002 7/3012002 7/3112002 7/31/2002 8/2/2002 8/5/2002 8/7/2002 K-40 K-40 K-40 Gr. Beta Cs-137 Gr. Beta K-40 Gr. Beta K-40 Sr-90 Gr. Alpha Gr. Beta K-40 Gr. Beta K-40 Sr-90 Sr-90 K-40 Gr. Beta Gr. Beta Be-7 Gr. Beta K-40 Be-7 Cs-1 37 Gr. Beta K-40 Be-7 K-40 Be-7 Be-7 Be-7 Gr. Beta K-40 1-131 K-40 K-40 Gr. Beta Gr. Beta Be-7 K-40 K-40 Gr. Beta K-40 1.33 i 0.99 1333.30 i 159.40 1423.70 +/- 121.30 2.65 +/- 0.54 0.17 +/- 0.04 27.72 +/- 2.26 20.24 +/- 1.19 4436.00 +/- 90.00 4684.20 +/- 734.40 0.50 +/- 0.30 4.42 +/- 1.50 7.57 +/- 1.22 1433.40 +/- 124.20 3.05 +/- 0.59 1245.20 +/- 109.20 2.38 +/- 0.51 0.98 +/- 0.35 1256.10 +/- 138.20 6.89 +/- 1.97 2.37 +/- 0.58 1394.80 +/- 538.40 8.10 +/- 0.27 7758.20 +/- 1100.00 1480.90 +/- 223.80 32.30 +/- 14.70 5262.40 +/- 522.10 2249.00 +/- 381.90 0.085 +/- 0.009 1390.10 +/- 168.30 0.068 +/- 0.016 0.077 +/- 0.016 0.080 +/- 0.013 2.40 +/- 0.84 1511.80 +/- 127.00 0.52 +/- 0.20 1198.40 +/- 114.10 1428.80 i 105.60 7.11 +/-0.07 1.75 i 0.84 1.82 +/- 0.30 5.13 +/- 0.66 1415.90 +/- 70.57 2.77 +/- 0.35 1361.10 +/- 111.90 1.14 +/- 0.91 1090.70 +/- 143.40 1443.30 +/- 164.30 3.28 +/- 0.60 0.18 +/- 0.05 25.45 +/- 2.03 20.54 +/- 1.24 4281.00 +/- 89.00 5242.50 +/- 884.50 0.60 +/- 0.30 2.97 +/- 1.40 6.83 +/- 1.16 1401.20 +/- 96.96 3.38 +/- 0.72 1340.20 +/- 121.90 2.63 +/- 0.52 0.97 +/- 0.35 1199.00 +/- 128.30 5.38 +/- 1.93 2.00 +/- 0.62 1098.10 +/- 437.40 8.00 +/- 0.25 8399.80 +/- 929.30 1726.40 +/- 552.60 50.97 +/- 27.10 5432.40 +/- 540.00 2989.90 +/- 509.60 0.085 +/- 0.006 1567.40 +/- 194.30 0.086 +/- 0.018 0.090 +/- 0.020 0.078 +/- 0.015 2.47 +/- 0.88 1446.80 +/- 101.80 0.49 +/- 0.29 1371.30 +/- 146.90 1344.30 +/- 106.40 6.99 +/- 0.07 1.90 +/- 0.78 2.05 +/- 0.32 5.72 +/- 0.70 1423.80 +/- 129.20 2.26 +/- 0.35 1358.30 +/- 115.80 1.23 +/- 0.67 1212.00 +/- 107.21 1433.50 + 102.11 2.97 +/- 0.40 0.18 +/- 0.03 26.58 +/- 1.52 20.39 +/- 0.86 4358.50 +/- 63.29 4963.35 +/- 574.82 0.55 +/- 0.21 3.70 +/- 1.02 7.20 +/- 0.84 1417.30 +/- 78.78 3.21 +/-O.46 1292.70 +/- 81.83 2.51 +/- 0.36 0.98 +/- 0.25 1227.55 +/- 94.29 6.13 +/- 1.38 2.19 +/- 0.42 1246.45 +/- 346.84 8.05 +/- 0.18 8079.00 +/- 720.00 1603.65 +/- 298.10 41.64 +/- 15.42 5347.40 +/- 375.56 2619.45 +/- 318.41 0.085 +/- 0.006 1478.75 +/- 128.53 0.077 +/- 0.012 0.084 +/- 0.013 0.079 +/- 0.010 2.43 +/- 0.61 1479.30 +/- 81.38 0.51 +/- 0.18 1284.85 +/- 93.00 1386.55 +/- 74.95 7.05 +/- 0.05 1.82 +/- 0.57 1.93 +/- 0.22 5.42 +/- 0.48 1419.85 +/- 73.61 2.52 +/- 0.25 1359.70 +/- 80.52 A5-3
TABLE A-5. In-House "Duplicate" Samples Concentration (pCUL)a Averaged Lab Code Date Analysis First Result Second Result Result MI-5355, 5356 F-5413, 5414 F-5413, 5414 MI-5603, 5604 MI-5603, 5604 MI-5578, 5579 VE-5682, 5683 VE-5682, 5683 VE-5682, 5683 WW-6188, 6189 SL-5724, 5725 SL-5724, 5725 SL-5724, 5725 MI-5877, 5878 Ml-6157, 6158 MI-6258, 6259 LW-6278, 6279 MI-6385, 6386 BS-6453, 6454 BS-6453, 6454 S0-6478, 6479 SO-6478, 6479 SO-6478, 6479 SO-6478, 6479 SO-6478, 6479 AP-6641, 6642 MI-6544, 6545 AP-6857, 6858 AP-6857, 6858 AP-6857, 6858 BS-6620, 6621 BS-6620, 6621 BS-6620, 6621 MI-6651, 6652 G-6760. 6761 G-6760, 6761 SWU-7054, 7055 U-7126, 7127 XW-7768, 7769 XW-7768, 7769 F-7148, 7149 BS-7337, 7338 BS-7337, 7338 BS-7337. 7338 SO-7407, 7408 S0-7407, 7408 SO-7407, 7408 8/13/2002 8/15/2002 8/1512002 812612002 8/2612002 8/27/2002 8/28/2002 8128/2002 8/28/2002 8/31/2002 9/3/2002 913/2002 9/3/2002 9/912002 9/19/2002 9/24/2002 9/3012002 10/1/2002 10/1/2002 10/1/2002 10/1/2002 10/1/2002 10/1/2002 10/1/2002 1011/2002 10/1/2002 10/2/2002 10/3/2002 101312002 1013/2002 101712002 1017/2002 101/2002 10/812002 10/912002 10/9/2002 1011012002 10/11/2002 1011412002 10/14/2002 10/15/2002 10123/2002 10123/2002 10/23/2002 10/29/2002 1012912002 10/29/2002 K-40 Gr. Beta K-40 1-131 K-40 K-40 Be-7 Gr. Beta K-40 Gr. Beta Be-7 Cs-137 K-40 K-40 K-40 K-40 Gr. Beta K-40 Cs-137 K-40 Cs-137 Gr. Alpha Gr. Beta K-40 Sr-90 Be-7 K-40 Be-7 Be-7 Be-7 Co-60 Cs-137 K-40 K-40 Be-7 K-40 Gr. Beta Gr. Beta Cs-I 37 H-3 K-40 Co-60 Cs-1 37 Gr. Beta Cs-137 Gr. Beta K-40 1405.00 +/- 165.80 2.37 +/- 0.10 1.47 +/- 0.32 0.64 +/- 0.34 1353.60 +/- 83.13 1301.50 +/- 161.70 0.29 +/- 0.10 3.79 +/- 0.08 3.06 +/- 0.29 2.70 +/- 0.57 0.92 +/- 0.19 0.05 +/- 0.02 2.09 +/- 0.31 1340.70 +/- 165.00 1372.10 +/- 115.10 1328.60 +/- 201.00 2.15 +/- 0.51 1297.10 +/- 168.90 0.43 +/- 0.03 16.50 +/- 0.51 0.074 +/- 0.016 8.01 +/- 4.36 30A1 +/-4.07 19.82 +/- 0.53 0.087 +/- 0.017 0.070 +/- 0.016 1331.60 +/- 125.20 0.062 +/- 0.015 0.062 +/-0.015 0.062 +/- 0.015 0.090 +/- 0.020 0.62 +/- 0.04 11.38 +/-0.48 1565.50 +/- 141.00 2.17 +/- 0.49 6.24 +/- 1.00 3.09 +/- 0.57 2.61 +/- 1.24 2.25 i 0.25 2.63 +/- 0.10 2.57 i 0.28 0.083 +/- 0.025 0.082 +/- 0.019 12.54 +/-2.34 0.14 +/- 0.03 16.73 +/- 2.21 12.05 +/- 0.61 1549.30 +/- 114.40 2.55 +/- 0.10 1.73 +/- 0.43 0.52 +/- 0.36 1261.40 +/- 117.80 1381.60 +/- 111.20 0.25 +/- 0.11 3.80 +/- 0.08 3.31 +/- 0.42 2.30 +/- 0.57 1.04 +/- 0.23 0.05 +/- 0.02 2.28 +/- 0.48 1168.50 +/- 172.50 1136.50 +/- 222.70 1312.60 +/- 118.60 1.70 +/- 0.50 1310.10 i 128.30 0.44 +/- 0.03 16.80 +/- 0.61 0.070 +/- 0.016 7.55 +/- 4.57 33.04 +/-4.28 20.39 +/- 0.58 0.094 +/- 0.020 0.080 i 0.015 1326.50 +/- 171.60 0.071 +/-0.015 0.071 +/- 0.015 0.071 i0.015 0.11 i0.02 0.63 i 0.03 10.78 +/- 0.52 1640.60 i 189.20 2.31 i0.34 6.61 i 0.60 2.06 +/- 0.52 2.61 i 1.08 2.09 i 0.18 2.64 0.10 2.98 +/- 0.44 0.073 +/- 0.031 0.11 +/-0.04 12.99 i2.22 0.15 +/- 0.03 16.62 +/- 2.27 12.27 +/- 0.81 1477.15 +/- 100.72 2.46 +/- 0.07 1.60 +/- 0.27 0.58 +/- 0.25 1307.50 +/- 72.09 1341.55 +/- 98.12 0.27 +/- 0.08 3.79 +/- 0.06 3.18 +/- 0.25 2.50 +/- 0.41 0.98 +/- 0.15 0.05 +/- 0.01 2.19 +/- 0.29 1254.60 +/-119.35 1254.30 +/- 125.34 1320.60 +/-116.69 1.93 +/- 0.36 1303.60 +/- 106.05 0.44 +/- 0.02 16.65 +/-O.40 0.072 i0.011 7.78 i 3.16 31.73 +/- 2.95 20.10 +/- 0.39 0.091 +/- 0.013 0.075 +/- 0.011 1329.05 +/- 106.21 0.066 +/- 0.010 0.066 +/- 0.010 0.066 +/- 0.010 0.10 +/- 0.01 0.62 +/- 0.02 11.08 +/- 0.35 1603.05 +/- 117.98 2.24 +/- 0.30 6.42 +/- 0.58 2.57 +/- 0.39 2.61 +/- 0.82 2.17 +/- 0.15 2.64 +/- 0.07 2.77 +/- 0.26 0.078 +/- 0.020 0.10 +/- 0.02 12.77 +/- 1.61 0.15 +/- 0.02 16.67 +/- 1.58 12.16 +/- 0.51 A5-4
TABLE A-5. In-House "Duplicate Samples Concentration (pC/L)a Averaged Lab Code Date Analysis First Result Second Result Result MI-7428, 7429 10/2912002 K-40 1542.60 +/- 213.00 1355.80 +/- 185.70 1449.20 +/- 141.29 pw-7621, 7622 10/30/2002 Gr. Beta 2.22 +/- 0.92 2.08 +/- 0.83 2.15 +/- 0.62 TD-7653,7654 10/3112002 H-3 11122.00 +/- 387.00 11259.00 +/- 390.00 11190.50 +/- 274.71 SW-7569, 7570 1115/2002 Gr. Beta 15.90 +/- 1.25 16.24 +/- 1.27 16.07 +/- 0.89 SW-7569, 7570 11/5/2002 K-40 14.79 +/- 1.48 14.79 +/- 1.48 14.79 +/- 1.05 SO-8010,8011 11/7/2002 Cs-137 0.11 +/- 0.02 0.11 +/- 0.03 0.11 + 0.02 SO-8010, 8011 11/7/2002 K-40 6.91 +/- 0.54 7.21 +/- 0.54 7.06 +/- 0.38 VE-7747, 7748 11,1112002 Gr. Beta 3.59 +/- 0.05 3.25 +/- 0.05 3.42 +/- 0.03 VE-7747,7748 11/11/2002 K-40 3.17 +/- 0.36 3.26 t 0.46 3.22 +/-0.29 MI-7789, 7790 11113/2002 K-40 1319.30 +/- 167.60 1301.20 +/- 140.70 1310.25 +/- 109.41 DW-8082,8083 11t29/2002 1-131 0.83 +/- 0.24 0.98 +/- 0.22 0.90 +/- 0.16 SW-8054. 8055 1212/2002 Gr. Beta 2.60 +/- 0.46 2.21 +/- 0.39 2.41 +/- 0.30 SW-8054, 8055 121212002 K-40 1.44 +/- 0.14 1.43 +/- 0.14 1.44 +/- 0.10 MI-8105, 8106 121412002 K-40 1300.60 +/- 111.30 1315.40 +/- 108.90 1308.00 +/- 77.86 TD-8298, 8299 12/5/2002 H-3 355.00 +/- 94.00 469.00 +/- 99.00 412.00 +/- 68.26 MI-8396, 8397 12117/2002 K-40 1409.20 +/- 117.30 1449.60 +/- 108.60 1429.40 +/- 79.93 SWT-8654,8655 12t30/2002 Gr. Beta 1.63 +/- 0.50 1.40 +/- OA7 1.51 +/- 0.34 AP-8783, 8784 12/31/2002 Be-7 0.044 +/- 0.009 0.042 +/- 0.008 0.043 +/- 0.006 Note: Duplicate analyses are performed on every twentieth sample received in-house. Results are not listed for those analyses with activities that measure below the LLD.
a Results are reported in units of pCi/L, except for air filters (pCi/Filter), food products, vegetation, soil, sediment (pCi/g).
A5-5
TABLE A-6. Department of Energy's Mixed Analyte Performance Evaluation Program (MAPEP)a.
Concentrationb Known Control Lab Code Type Date Analysis Laboratory result Activity Limitsc STW-939 water 12/01/01 Am-241 1.25 +/- 0.0 1.19 +/- 0.0 0.83 - 1.6 STW-939 water 12101/01 Co-57 138.9 +/- 0.5 143 +/- 14.3 100.1 - 185.9 STW-939 water 12/01/01 Co-60 139.1 +/- 0.5 141 +/- 14.1 98.7 - 183.3 STW-939 water 12/01101 Cs-134 25.16 +/- 0.2 28.5 +/- 0.3 19.95 -37.1 STW-939 water 12/01/01 Cs-137 279.96 +/- 0.9 286 +/- 28.6 200.2 - 371.8 STW-939d water 12/01/01 Fe-55 19.68 +/- 23.2 9.2 +/- 0.9 6.44 - 12.0 STW-939 water 12/01/01 Mn-54 253.64 +/- 0.9 246 +/- 0.2 172.2 - 319.8 STW-939 water 12/01/01 Ni-63 65.88 +/- 1.9 88.3 +/- 8.8 61.81 - 114.8 STW-939e water 12/01/01 Pu-238 0.060 +/- 0.01 0.0 +/- 0.0 STW-939 water 12/01/01 Pu-239/40 2.79 +/- 0.0 2.99 +/- 0.3 2.09 - 3.9 STW-939 water 12/01/01 Sr-90 4.88 +/- 0.3 4.8 +/- 0.5 3.36 - 6.2 STW-939 water 12/01/01 U-23314 0.89 +/- 0.0 0.98 +/- 0.1 0.69 - 1.3 STW-939 water 12/01/01 U-238 6.75 +/- 0.0 7.8 +/- 0.8 5.46 - 10.1 STW-939 water 12/01/01 Zn-65 70.6 +/- 1.1 67.3 +/- 6.7 47.11 - 87.5 STSO-955 soil 10/16102 Am-241 40.54 +/-2.7 43.5 +/-4.4 30.45 -56.6 STSO-955 soil 10/16/02 Co-57 210.58 +/- 2.0 246 +/- 24.6 172.2 - 319.8 STSO-955 soil 10116/02 Co-60 84.38 +/-0.9 87.5 +/-8.8 61.25-113.8 STSO-955 soil 10/16102 Cs-1 34 692.6 +/- 2.1 862 +/- 86.0 603.4 - 1120.6 STSO-955 soil 10/16/02 Cs-137 96.98 +/- 1.7 111 +/- 11.1 77.7 - 144.3 STSO-955 soil 10/16102 Fe-55 1714.6 +/- 299.6 1870 +/- 187.0 1309 - 2431.0 STSO-955 soil 10/16/02 Mn-54 509.74 +/- 3.4 546 +/- 54.6 382.2 -709.8 STSO-955 soil 10/16/02 Ni-63 890.6 +/- 22.4 1180 +/- 118.0 826 - 1534.0 STSO-955 soil 10/16/02 Pu-238 34.04 +/- 6.0 33.3 +/- 3.3 23.31 -43.3 STSO-955 soil 10/16/02 Pu-239/40 68.7 +/- 3.7 72.9 +/- 7.3 51.03 -94.8 STSO-955e soil 10/16/02 Sr-90 1.5 +/- 3.0 0.0 +/- 0.0 STSO-955 soil 10/16/02 U-233/4 166.33 +/-3.8 229 +/- 22.9 160.3 -297.7 STSO-955 soil 10/16/02 U-238 169.76 +/- 3.8 220 +/- 22.0 154 -286.0 STSO-955 soil 10/16/02 Zn-65 783.59 +/- 6.4 809 +/- 80.9 566.3 - 1051.7 a Results obtained by Environmental, Inc. Midwest Laboratory as a participant in the Department of Energy's Mixed Analyte Performance Evaluation Program, Idaho Operations office, Idaho Falls, Idaho b All results are in Bq/kg or Bq/L as requested by the Department of Energy.
c MAPEP results are presented as the known values and expected laboratory precision (1 sigma, 1 determination) and control limits as defined by the MAPEP.
d Known activity below the laboratory LLD. The sample was recounted for 2000 minutes; result:11.52 +/- 5.55 Bq /L
' Included in the testing series as a "false positive". No activity expected.
A6-1
TABLE A-7. Environmental Measurements Laboratory Quality Assessment Program (EML)
Concentration" Lab Code Type Date STW-945 Water 03/01/02 STW-945 Water 03/01/02 STW-945 Water 03/01/02 STW-945 Water 03/01/02 STW-945 Water 03/01102 STW-945 Water 03/01/02 STW-945 Water 03/01102 STW-945 Water 03/01/02 STW-946 Water 03/01/02 STW-946 Water 03101102 STW-946 Water 03/01/02 STSO-947 Soil 03/01/02 STSO-947 Soil 03/01/02 STSO-947 Soil 03/01102 STSO-947 Soil 03/01/02 STSO-947 Soil 03/01/02 STSO-947 Soil 03101/02 STSO-947 Soil 03/01/02 STSO-947 Soil 03/01/02 STSO-947 Soil 03/01/02 STSO-947 Soil 03/01/02 STSO-947 Soil 03/01/02 STSO-947 Soil 03/01/02 STVE-948 Vegetation 03/01/02 STVE-948 Vegetation 03/01/02 STVE-948 Vegetation 03/01/02 STVE-948 Vegetation 03101/02 STVE-948 Vegetation 03101/02 STVE-948' Vegetation 03/01102 STVE-948 Vegetation 03/01/02 STAP-949 Air Filter 03101/02 STAP-949 Air Filter 03/01/02 STAP-949 Air Filter 03101/02 STAP-949 Air Filter 03/01102 STAP-949 Air Filter 03/01102 STAP-949 Air Filter 03/01/02 STAP-949 Air Filter 03/01102 STAP-949 Air Filter 03/01/02 STAP-950 Air Filter 03/01/02 STAP-950 Air Filter 03/01102 STW-959 Water 09101/02 STW-959 Water 09/01/02 STW-959 Water 09101102 STW-959 Water 09/01/02 STW-959 Water 09/01/02 STW-959 Water 09/01/02 Analysis Am-241 Co-60 Cs-134 Cs-137 Pu-238 Pu-239/40 Sr-90 Uranium Gr. Alpha Gr. Beta H-3 Ac-228 Arn-241 Bi-212 Bi-214 Cs-137 K-40 Pb-212 Pb-214 Pu-239140 Sr-90 Th-234 Uranium Am-241 Cm-244 Co-60 Cs-I 37 K-40 Pu-239/40 Sr-90 Am-241 Co-60 Cs-1 37 Mn-54 Pu-238 Pu-239/40 Sr-90 Uranium Gr. Alpha Gr. Beta Am-241 Co-60 Cs-134 Cs-1 37 Cs-137 Am-241 Laboratory results 1.68 +/- 0.14 349.20 +/- 2.60 3.40 +/- 0.60 57.20 +/- 1.70 0.45 +/- 0.11 4.47 +/- 0.28 7.40 +/- 1.30 3.27 +/- 0.43 265.40 +/- 7.70 930.60 +/- 12.00 226.30 +/- 32.70 55.00 +/- 5.50 8.30 +/- 3.30 49.20 +/- 12.40 46.60 +/- 3.10 1401.60 +/- 9.10 613.10 +/- 28.10 51.60 +/- 2.60 52.00 +/- 3.60 14.70 +/- 3.50 52.10 +/- 6.30 122.40 +/- 6.30 143.40 +/- 9.40 3.10 +/-2.20 0.90 +/- 0.80 13.50 +/- 2.10 350.40 +/- 6.30 940.80 +/- 45.60 16.90 +/- 0.70 543.40 +/- 24.90 0.09 +/- 0.05 30.10 +/- 0.30 29.90 +/- 0.30 40.40 +/- OAO 0.05 +/- 0.02 0.15 +/- 0.02 3.40 +/- 0.40 0.80 +/- 0.20 0.43 +/- 0.04 1.34 +/- 0.05 3.00 +/- 0.10 258.40 +/- 2.30 50.80 +/- 3.30 80.10 +/- 0.30 80.10 +/- 0.30 3.00 +/- 0.10 EML ResulP 1.47 347.33 3.36 56.07 0.49 4.22 7.58 2.84 375.00 1030.00 283.70 51.17 10.93 53.43 53.93 1326.67 621.67 51.10 54.37 19.10 53.76 89.30 194.77 2.23 1.32 11.23 313.67 864.33 3.54 586.28 0.09 30.52 28.23 38.53 0.06 0.19 4.83 0.61 0.53 1.30 3.04 268.67 60.20 81.43 81.43 3.04 Control Limitsc 0.79 - 1.41 0.80 - 1.20 0.80 - 1.30 0.80 - 1.22 0.74 - 1.20 0.79 - 1.20 0.69 - 1.34 0.75 - 1.33 0.58 - 1.29 0.61 - 1.43 0.78 - 2.45 0.80 - 1.38 0.65 - 2.28 0.50 - 1.34 0.78 - 1.42 0.80 - 1.25 0.80 - 1.32 0.78 - 1.32 0.76 - 1 A6 0.71 - 1.30 0.67 - 2.90 0.63 - 2.35 0.71 - 1.32 0.73 - 2.02 0.61 - 1.59 0.80 - 1.44 0.80 - 1.31 0.79 - 1.39 0.69 - 1.31 0.55 - 1.21 0.70 - 2.34 0.80 - 1.26 0.80 - 1.32 0.80 - 1.35 0.67 - 1.33 0.73 - 1.26 0.53 - 1.84 0.79 - 2.10 0.73 - 1.43 0.76 - 1.36 0.79 - 1.41 0.80 - 1.20 0.80 - 1.30 0.80 - 1.22 0.80 - 1.22 0.79 - 1.41 A7-1
TABLE A-7. Environmental Measurements Laboratory Quality Assessment Program (EML)a.
Concentratbonb EML Lab Code Type Date Analysis Laboratory results Result' Control Limits" STW-959 Water 09/01102 Am-241 3.00 +/- 0.10 3.04 0.79 - 1.41 STW-959 Water 09/01/02 Co-60 258.40 i 2.30 268.67 0.80 - 1.20 STW-959 Water 09/01/02 Cs-134 50.80 +/- 3.30 60.20 0.80 - 1.30 STW-959 Water 09/01/02 Cs-137 80.10 +/- 0.30 81.43 0.80- 1.22 STW-959 Water 09/01/02 H-3 271.90 +/- 20.90 227.30 0.78 -2.45 STW-959 Water 09/01/02 Pu-238 4.40 +/- 0.20 4.33 0.74 - 1.20 STW-959 Water 09/01/02 Pu-239/40 2.10 +/- 0.10 2.07 0.79 - 1.20 STW-959 Water 09/01/02 Sr-90 9.70 +/- 0.20 8.69 0.69 - 1.34 STW-959 Water 09/01/02 Uranium 5.60 +/- 0.10 6.84 0.75 - 1.33 STW-960 Water 09/01/02 Gr. Alpha 204.90 +/- 3.20 210.00 0.58 - 1.29 STW-960 Water 09/01/02 Gr. Beta 852.00 +/- 26.50 900.00 0.61 - 1.A3 STSO-961 Soil 09/01/02 Ac-228 47.60 +/- 1.90 42.30 0.80 - 1.38 STSO-961 Soil 09/01/02 Am-241 7.80 +/- 1.40 6.77 0.65 -2.28 STSO-961 Soil 09/01/02 Bi-212 45.60 +/- 1.70 45.93 0.50 - 1.34 STSO-961e Soil 09/01/02 Bi-214 48.80 +/- 4.90 33.63 0.78 - 1.42 STSO-961 Soil 09/01/02 Cs-137 819.60 +/- 16.60 829.33 0.80 - 1.25 STSO-961 Soil 09/01/02 K-40 705.30 +/- 31.40 637.67 0.80 - 1.32 STSO-961 Soil 09/01/02 Pb-212 48.60 +/- 3.40 43.43 0.78 - 1.32 STSO-961 Soil 09/01/02 Pb-214 51.10 +/- 5.10 35.20 0.76 - 1.46 STSO-961' Soil 09/01/02 Pu-239/40 20.20 +/- 0.80 12.90 0.71 - 1.30 STSO-961 Soil 09/01/02 Sr-90 38.50 +/- 0.10 41.16 0.67 - 2.90 STSO-961 Soil 09/01/02 Uranium 58.90 +/- 0.70 87.21 0.71 - 1.32 STVE-962 Vegetation 09/01/02 Am-241 2.10 +/- 0.30 2.25 0.73 - 2.02 STVE-962 Vegetation 09/01/02 Cm-244 1.00 +/- 0.30 1.25 0.61 - 1.59 STVE-962 Vegetation 09/01/02 Co-60 11.80 +/- 1.50 9.66 0.80 - 1.44 STVE-962 Vegetation 09/01/02 Cs-137 340.30 +/- 16.80 300.67 0.80 - 1.31 STVE-962 Vegetation 09/01/02 K-40 1646.00 +/- 74A0 1480.00 0.79 - 1.39 STVE-962 Vegetation 09/01/02 Pu-239/40 3.00 +/- 0.30 3.43 0.69 - 1.31 STVE-962 Vegetation 09/01/02 Sr-90 345.60 +/- 97.80 476.26 0.55 - 1.21 STAP-9639 Air Filter 09/01/02 Am-241 0.20 +/- 0.01 0.19 0.70 -2.34 STAP-963 Air Filter 09/01/02 Co-60 24.90 +/- 0.60 23.00 0.80 - 1.26 STAP-963 Air Filter 09/01/02 Cs-137 38.00 +/- 1.30 32.50 0.80 - 1.32 STAP-963 Air Filter 09/01/02 Mn-54 60.80 +/- 1.90 52.20 0.80 - 1.35 STAP-9639 Air Filter 09/01/02 Pu-238 0.11 +/- 0.02 0.12 0.67 - 1.33 STAP-9639 Air Filter 09/01/02 Pu-239140 0.21 +/- 0.01 0.21 0.73 - 1.26 STAP-963 Air Filter 09/01/02 Sr-90 5.20 +/- 0.20 5.56 0.53 - 1.84 STAP-9639 Air Filter 09/01/02 Uranium 0.41 +/- 0.04 0.47 0.79 - 2.10 STAP-964 Air Filter 09/01/02 Gr. Alpha 0.40 +/- 0.10 0.29 0.73 - 1.43 STAP-964 Air Filter 09/01/02 Gr. Beta 0.80 +/- 0.10 0.87 0.76 - 1.36
' Results are reported in Bq/L with the following exceptions: Air Filters (Bq/Filter). Soil and Vegetation (Bqlkg).
b The EML result listed is the mean of replicate determinabons for each nuclide +/- the standard error of the mean.
c Control limits are reported by EML as the ratio of Reported Value / EML value.
d An error was found In the conversion from pCug to Bq/g. Corrected result: 2.84 +/- 0.59 Bq/g.
e Naturally-occurring radium daughters are present in the shield background, and a probable cause of the higher bias seen for isotopes of lead and bismuth.
' Reporting error.The average result of the triplicate analyses was 14.1+/- 5 7 Bq/kg.
9 STAP-963, Calculations for the transuranics analyses (Am-241. Uranium, Pu-238, -239/40) were not converted to Sq/total filter.
The data listed is the result of recalculation.
A7-2
APPENDIX B DATA REPORTING CONVENTIONS B-1
Data Reporting Conventions 1.0. All activities, except gross alpha and gross beta, are decay corrected to collection time or the end of the collection period.
2.0. Single Measurements Each single measurement is reported as follows:
x + s where:
x = value of the measurement; s = 2s counting uncertainty (corresponding to the 95% confidence level).
In cases where the activity is less than the lower limit of detection L, it is reported as: <L, where L = the lower limit of detection based on 4.66s uncertainty for a background sample.
3.0. Duplicate analyses 3.1 Individual results: For two analysis results; xi +/- st and x2 + S2 Reported result:
x +/- s; where x = (1/2) (xI + x2) and s = (1/2)
S2 3.2.
Individual results:
<L,, <L2 Reported result: <L, where L = lower of LI and L2 3.3.
Individual results:
x +/- s, <L Reported result:
x +/- s if x > L; <L otherwise.
4.0. Computation of Averages and Standard Deviations 4.1 Averages and standard deviations listed in the tables are computed from all of the individual measurements over the period averaged; for example, an annual standard deviation would not be the average of quarterly standard deviations. The average x and standard deviation s of a set of n numbers xl, x2... xn are defined as follows:
x =
X
=
n
\\1 n-I 4.2 Values below the highest lower limit of detection are not included in the average.
4.3 If all values in the averaging group are less than the highest LLD, the highest LLD is reported.
4.4 If all but one of the values are less than the highest LLD, the single value x and associated two sigma error is reported.
4.5 In rounding off, the following rules are followed:
4.5.1. If the figure following those to be retained is less than 5, the figure is dropped, and the retained figures are kept unchanged. As an example, 11.443 is rounded off to 11.44.
4.5.2. If the figure following those to be retained is equal to or greater than 5, the figure is dropped and the last retained figure is raised by 1. As an example, 11.445 is rounded off to 11.45.
4.6 Composite samples which overlap the next month or year are reported for the month or year in which most of the sample is collected.
B-2
APPENDIX C TECHNICAL SPECIFICATION 2.1.3 REACTOR COOLANT DOSE EQUIVALENT IODINE ABOVE TECHNICAL SPECIFICATION LIMIT C-1
The following information is provided per Technical Specification 2.1.3.4. On 5/4/2002 DEI was
> 1.0 uCi.gm for approximately 22 hours2.546296e-4 days <br />0.00611 hours <br />3.637566e-5 weeks <br />8.371e-6 months <br /> 1-131 and 1-133 when DEI >1.0 3
2.5 2
I E
An 3
1.5
/A
\\ IN I
l DEI 1-131
-l-1-133 1
0.5 n
i 5/1/2002 5/2/2002 5/3/2002 5/4/2002 5/5/2002 5/6/2002 Date I
C-2
Rx Power/ Letdown Flow 120 100 E
a)
L.0
-0 80 60 40 7
I 7 I I H U 0
I i
-4 RX Power Letdown flow I 20 0
5/1/02 5/2/02 5/3/02 5/4/02 5/5/02 date/time 5/6/02 Date/time 5/1/02 7:10 PM 5/2/02 8:16 PM 5/3/02 8:25 PM 5/4/02 12:26 AM 5/4/02 4:30 AM 5/4/02 8:36 AM 5/4/02 12:38 PM 5/4/02 4:32 PM 5/4/02 8:25 PM 5/4/02 10:35 PM 5/5/02 2:38 AM Rx power 30 30 14 0
0 0
0 0
0 0
0 Letdown flow 72 71.8 71.7 0
76 73 75 36 20 40 108 DEI 0.0207 0.016 0.225 1.31 2.56 1.67 1.43 1.19 1.02 0.775 0.413 NUCLIDE 1-131 0.011 0.00708 0.196 1.17 2.32 1.53 1.33 1.11 0.965 0.736 0.395 1-133 0.0177 0.0154 0.0759 0.419 0.736 0.435 0.34 0.248 0.19 0.138 0.0642 C-3
APPENDIX D SAMPLE LOCATION MAP D-1
True N
Site N
r, I
I i
I L.
i I
9 1
L. -
I 10 35 I
\\ I II 0
1/2 1
II I
SCALE IN MILES SITE BOUNDARY/OWNER CONTROL AREA D-2
- 20 Locations currently discontinued are not illustrated.
D-3