ML19106A223
| ML19106A223 | |
| Person / Time | |
|---|---|
| Site: | 07000925 |
| Issue date: | 07/31/1992 |
| From: | Beverly Smith Oak Ridge Associated Universities |
| To: | NRC/RGN-III |
| Shared Package | |
| ML19106A222 | List: |
| References | |
| Download: ML19106A223 (48) | |
Text
Prepared by Oak Ridge Associated Universities Prepared for U.S. Nuclear Regulatory Commission's Region Ill Office Sponsored by Division of Industrial and Medical Nuclear Safety ORISE 92/G-57 CONFIRMATORY RADIOLOGICAL SURVEY FORMER BURIAL GROUND CIMARRON CORPORATION FACILITY CRESCENT,OKLAHOMA B. M. SMITH Environmental Survey and Site Assessment Program Energy/Environment Systems Division FINAL REPORT JULY 1992
NOTICES The opinions expressed herein do not necessarily reflect the opinions of the sponsoring institutions of Oak Ridge Associated Universities.
This report was prepared as an account of work sponsored by the United States Government. Neither the United States Government nor the U.S. Department of Energy, nor any of their employees, makes any warranty, expressed or implied, or assumes any legal liability or responsibility for the accuracy, completeness, or usefulness of any information, apparatus, product, or process disclosed, or represents that its use would not infringe on privately owned rights.
Reference herein to any specific commercial product, process, or service by trade name, mark, manufacturer, or otherwise, does not necessarily constitute or imply its endorsement or recommendation, or favor by the U.S. Government or any agency thereof. The views and opinions of authors expressed herein do not necessarily state or reflect those of the U.S. Government or any agency thereof.
CONFIRMATORY RADIOLOGICAL SURVEY FORMER BURIAL GROUND CIMARRON CORPORATION FACILITY CRESCENT, OKLAHOMA Prepared by B. M. Smith Environmental Survey and Site Assessment Program Energy/Environment Systems Division Oak Ridge Associated Universities Oak Ridge, TN 37831-0117 E. H. Bjelland P. R. Cotten G. R. Foltz Project Staff M. J. Laudeman E. H. Montalvo E. A. Powell Prepared for Division of Industrial and Medical Nuclear Safety U.S. Nuclear Regulatory Commission Region m Office FINAL REPORT JULY 1992 This report is based on work performed under an Interagency Agreement (NRC Fin. No. A-9076) between the U.S. Nuclear Regulatory Commission and the U.S. Department of Energy. Oak Ridge Institute for Science and Education's Energy /Environment Systems Division performs complementary work under contract# DE-AC05-760R00033 between the U.S. Department of Energy and Oak Ridge Associated Universities.
H:\\CLAIBORT\\FILES\\REPORTS\\CIMARRON 1uly 21, 1992
CONFIRMATORY RADIOLOGICAL SURVEY FORMER BURIAL GROUND CIMARRON CORPORATION FACil,ITY CRESCENT, OKLAHOMA Prepued by: J.ii:t!~ ~
Environmental Survey and Site Assessment Program l)ate:~<~,:
Reviewed by: _S:_~
1,1'\\.._H_. s:L
__ 4_,__""-_rf¥---..,...-- l)ate:+/- /-, 1.-
C. F. Weaver, Laboratory Manager{
Environmental Survey and Site Assessment Program Reviewed by:~'
M. R. Landis, Project Manager Date:1/.,) /cp 1
t ~
Environmental Survey and Site Assessment Program
TABLE OF CONTENTS PAGE List of Figures List of Tables In.troduction..... *........................................
Fili.
D ac ty escnption.........................................
Proced.ures......... *....................................
Findings and Results........................................
Comparison of Results with Guidelines.............................
Summary...............................................
References..............................................
Appendices:
Appendix A: Major Sampling and Analytical Equipment Appendix B: Measurement and Analytical Procedures Appendix C: Guidelines for Residual Concentrations of Thorium and Uranium Wastes in Soil ii iii 1
2 3
5 7
8 32 H:\\CLAIBORT\\FILES\\REPORTS\\CIMARRON 1
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LIST OF FIGURES PAGE FIGURE 1: Location of the Cimarron Facility, Crescent, Oklahoma...........
10 FIGURE 2: Plot Plan - Cimarron Facility...........................
11 FIGURE 3: Former Burial Ground Area...........................
12 FIGURE 4: Former Burial Ground Area - Elevated Direct Radiation Location 13 FIGURE 5: Former Burial Ground Area - Surface Soil Sampling Locations at Grid Line Intersections.............................
14 FIGURE 6: Former Burial Ground Area - Surface Soil Sampling Locations from Trench Excavations and Soil Piles.......................
15 FIGURE 7: Former Burial Ground Area - Subsurface Soil Sampling Locations....
16 FIGURE 8: Background Measurement and Sampling Locations..............
17 H:\\CLAJBORT\\FILES\\REPORTS\\CIMARRON ii July 21, 1992
LIST OF TABLES PAGE TABLE 1: Exposure Rate Measurements and Radionuclide Concentrations in Surface Soil Samples...............................
18 TABLE 2: Isotopic Uranium Concentrations in Soil Samples...............
27 TABLE 3: Radionuclide Concentrations in Subsurface Soil Samples...........
28 TABLE 4: Background Exposure Rates and Radionuclide Concentrations in Soil.........................................
31 H:\\CLAIBORT\\FILES\\REPORTS\\CIMARRON iii July 21, 1992
CONFIRMATORY RADIOLOGICAL SURVEY FORMER BURIAL GROUND CIMARRON CORPORATION FACILITY CRESCENT, OKLAHOMA IN1RODUCTION The Kerr-McGee Corporation operated the Cimarron Facility in Crescent, Oklahoma to produce slightly enriched (approximately 3 % ) uranium fuel and mixed oxide (uranium plus plutonium) reactor fuel between 1965 and 1975. These activities were conducted under license SNM-928 with the Atomic Energy Commission, predecessor to the Nuclear Regulatory Commission (NRC).
In 1983, Sequoyah Fuels Corporation (SFC) became the owner of the Cimarron Facility, when Kerr-McGee Nuclear Corporation was divided into SFC and Quivira Mining Corporation.
Later, Cimarron Corporation, a subsidiary of the Kerr-McGee Nuclear Corporation, became responsible for the Cimarron Facility.
Decontamination of the Cimarron Facility began in 1979 with the goal of removing all contaminated equipment and materials so the facility could be released for unrestricted use. The decontamination and decommissioning project was divided into several phases, which involved the Mixed Oxide Plant, the Uranium Plant, the on-site Burial Ground, and the Sanitary Lagoons.
Decontamination and decommissioning activities involving the Mixed Oxide Plant and the Sanitary Lagoons are nearing completion, and the Uranium Plant is in the process of being decontaminated.
Decontamination activities have been completed for the former Burial Ground. The Burial Ground was opened in March 1966 and used for the disposal of low level uranium wastes and thorium contaminated materials, transferred from another Kerr-McGee plant site; its use was discontinued in August 1970. Burial records indicate that 1,303 kg of depleted uranium, 148 kg of enriched uranium, and 5,555 kg of natural thorium were buried at this location.
Excavation and removal of the buried waste and contaminated soil was initiated in 1986 and completed in 1988.
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Initial decontamination activities for the former Burial Ground were completed by Cimarron Corporation in 1988. In August 1988, at the request of the NRC, Oak Ridge Associated Universities (ORAU) conducted a confirmatory survey of the former Burial Ground1* Survey activities consisted of gamma surface scans, exposure rate measurements, surface soil sampling, and subsurface soil and water sampling. Gamma scans identified 30 areas of elevated direct radiation. Clean-up of the areas was initiated immediately after their identification and follow-up surveys indicated that the clean-up was effective at all locations with the exception of Trench
- 1. At the time of the 1988 ORAU survey, contaminated soil meeting Option 2 (on-site burial) disposal concentration limits was stored at the south end of the Burial Ground, inside the fenced area. In April 1991, this material was moved to the yard beside the Uranium Plant. Additional decontamination was performed by Cimarron Corporation by excavation of approximately 14,000 cubic feet of soil, which was removed to the yard beside the Uranium Plant. No additional contaminated soil was identified by the final surveys2 performed by Cimarron Corporation.
At the request of the NRC's Region III Office, the Environmental Survey and Site Assessment Program (ESSAP) of ORA U conducted a confirmatory radiological survey of the former Burial Ground at the Cimarron Corporation Facility. The survey was performed to provide supporting information to confirm the radiological status of the site relative to the applicable NRC guidelines for release of the former Burial Ground for unrestricted use. This report summarizes the procedures and results of the survey.
FACILITY DESCRIPTION The Cimarron Corporation Facility is located on a site of approximately 450 hectares in Logan County, about 8 kilometers south of Crescent, Oklahoma (Figure 1). The site includes the Uranium Plant, the Mixed Oxide Plant, the former Burial Ground, two Sanitary Lagoons, and a Waste Evaporation Pond (Figure 2). The former Burial Ground occupies approximately H:\\CIAIBOR"l'\\FILB\\REPORTS\\CIMARRON 2
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8,600 m2 and is located at the northeast edge of the site. The former Burial Ground includes four trenches within a fenced area (Figure 3) which are approximately 3 meters deep and 1 to 2 meters wide.
PROCEDURES OBJECTIVE The objective of the independent survey was to provide supporting information to confirm that the results of the licensee's decontamination and decommissioning efforts were effective in meeting the NRC guidelines for unrestricted use.
ESSAP also reviewed the supporting documentation, provided by the licensee, to evaluate the accuracy of the information and to assure that a complete description of the radiological status of the former Burial Ground was provided.
DOCUMENT REVIEW As part of the confirmatory activities, ESSAP reviewed the final survey report prepared by Cimarron Corporation for the Burial Ground2* Data and survey results presented in the final report were reviewed to assess the adequacy of the decontamination activities and to compare the licensee's survey results to the established release guidelines.
SURVEY PROCEDURES During the period of December 9 through 12, 1991, ESSAP performed a confirmatory radiological survey of the former Burial Ground at the Cimarron Corporation Facility. The survey was performed in accordance with a plan developed by ESSAP dated November 25, 19913 and submitted to the NRC.
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Reference Grid The 10 m reference grid utilized by the licensee was re-established by ESSAP for referencing measurements and sampling (Figure 3).
Surface Scans Surface scans of the Burial Ground were performed using Nal(Tl) gamma scintillation detectors coupled to ratemeters with audible indicators.
Locations of elevated direct radiation were marked for further investigation (Figure 4).
Exposure Rate Measurement Exposure rate measurements were performed at 1 meter above the surface at all grid line intersections.
Measurements were performed using Nal(Tl) gamma scintillation detectors coupled to ratemeters and cross-calibrated with a pressurized ionization chamber (PIC).
Soil Sampling Surface soil samples (depth 0-15 cm) were collected from grid line intersections, trench walls (approximately 1 meter above the trench floor), four piles of soil stored outside of the fenced area, locations of elevated activity identified by Cimarron Corporation and ORA U during previous surveys, and at locations of elevated direct radiation identified by the surface scans during this survey (Figures 5 and 6).
Subsurface soil samples were collected at approximately 15 to 60 cm intervals from 16 boreholes, which measured in depth from O to 170 cm. Borehole drilling sites were selected from locations of elevated activity identified by Cimarron Corporation and ORAU during previous surveys (Figure 7).
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SAMPLE ANALYSIS AND DATA INTERPRETATION
. Samples and direct measurement data were returned to the ESSAP laboratory in Oak Ridge, TN for analyses and interpretation.
Soil samples were analyzed by gamma spectrometry.
Radionuclides of primary interest were U-235, U-238, and Th-232; however, spectra were also reviewed for other identifiable photopeaks.
Selected soil samples were analyzed by alpha spectrometry for isotopic uranium.
Additional information concerning major instrumentation, sampling equipment, and analytical procedures is provided in Appendices A and B. Results of the independent measurements were compared to the NRC guidelines (Appendix C).
FINDINGS AND RESULTS DOCUMENT REVIEW The documentation provided by Cimarron Corporation was thorough and the radiological data provided in the final report demonstrated that the residual activity levels satisfied the established decommissioning guidelines.
SURVEY RESULTS Surface Scans Gamma scans of the former Burial Ground identified one area of slightly elevated direct radiation at 108N, 53E (Figure 4). This location was noted for further investigation.
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Exposure Rate Measurements Exposure rate measurements are summarized in Table 1. Exposure rates for the Burial Ground ranged from 9 to 14 µR/h.
Radionuclide Concentrations in Soil Samples Twelve samples were analyzed by alpha spectrometry for isotopic uranium. The uranium concentrations for these samples are summarized in Table 2 and indicate slight enrichment above natural isotopic abundances for U-234 and U-235. Isotopic uranium concentrations ranged from 0.5 to 66.2 pCi/g for U-234, from 0.1 to 3.2 pCi/g for U-235, and from 0.4 to 26.2 pCi/g for U-238. The concentrations of total uranium ranged from 0.9 to 95.6 pCi/g. On the basis of alpha spectrometry analysis, the ratio of U-234 to U-235 is approximately 20: 1. This ratio was used to calculate the total uranium concentrations in soil samples analyzed by gamma spectrometry.
Concentrations of radionuclides in surface soil samples are summarized in Table 1.
Concentration ranged from 0.1 to 1.6 pCi/g for U-235 and from < 1.2 to 10.8 pCi/g for U-238.
The concentrations of total uranium in the surface soil samples ranged from < 3.1 to 44 pCi/ g.
The highest concentration was identified at 69N, 62E, which was an area of elevated direct radiation identified during the previous survey.
Thorium concentrations determined for the surface soil samples are summarized in Table 1.
Gamma spectra were reviewed and the thorium-232 series radionuclides were in equilibrium.
Total thorium (Th-232 + Th-228) concentrations ranged from 0.4 to 5.5 pCi/g. The highest concentration was identified at 30N, 50E.
Uranium and thorium concentrations in subsurface soil samples are summarized in Table 3.
Uranium concentrations ranged from 0.1 to 1.2 pCi/g for U-235, from < 1.3 to 10.8 pCi/g for U-238, and from <5.5 to 33 pCi/g for total uranium. The highest concentration was identified H:\\CLAIBORT\\FILES\\REPORTS\\CIMARRON 6
July 21, 1992
at 95N, 50E in the sample taken at a depth of 0-15 cm. Uranium concentrations for samples collected from the boreholes at 70N, 57E; 73N, 66E; 90N, 65E, and 95N, 45E increased with depth. The total thorium concentrations ranged from < 1.5 to 4.9 pCi/g.
COMPARISON OF RESULTS WITH GUIDELINES Background exposure rates were determined during the 1988 ORAU survey {Table 4) and averaged 10 µR/h. Surface scans identified one area of slightly elevated direct radiation at 108N, 53E. This area had a gamma exposure rate of 14 µR/h. Therefore, this area does not exceed the guideline of 10 µR/h above background, as specified in Appendix C, or the 5 µR/h above background guideline, currently in use by the NRC4*
The guidelines for residual concentrations of thorium and uranium wastes in soil are presented in Appendix C. The primary contaminants of concern for this site are enriched uranium, depleted uranium and natural thorium. Applicable soil concentration guidelines are:
Enriched Uranium Depleted Uranium 30 pCi/g 35 pCi/g Natural Thorium*
10 pCi/ g
- With all daughters present and in equilibrium.
Since the residual activity may be a combination of enriched and depleted uranium, and the alpha spectrometry analyses indicate that the uranium is slightly enriched in U-234 and U-235, the more conservative guideline value of 30 pCi/ g was used for comparison with the uranium results.
These guidelines are expressed in terms of concentrations above normal background levels.
Background radionuclide concentrations in soil were determined during the 1988 ORAU survey (Table 4). Total uranium concentrations ranged from < 1.2 to 2.0 pCi/g (1.6 pCi/g average)
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and total thorium concentrations ranged from 0.9 to 2.1 pCi/g (1.4 pCi/g average). Therefore, the sample analysis results indicating that the NRC guidelines have been exceeded are 31.6 pCi/g for total uranium and 11.4 pCi/g for total thorium.
Gamma spectrometry analysis identified 2 surface soil samples with total uranium concentrations which exceeded the guideline value. These samples included the soil samples collected from the previously identified area of elevated activity at 69N, 62E ( 44 pCi/ g), and from the borehole located at 95N, 50E (33 pCi/g, sample depth 0-15 cm). Alpha spectrometry analysis identified 3 surface soil samples which exceeded the guideline value for uranium. These samples included the soil samples collected from a previously identified area of elevated direct radiation at 91N, 42E (33.2 pCi/g), the area of elevated direct radiation identified by this survey at 108N, 53E (95.6 pCi/g) and the borehole at 25N, 70E (43.6 pCi/g, sample depth 0-15 cm).
Total thorium concentrations in all surface and subsurface soil samples were less than the 10 pCi/g above background guideline value.
SUMMARY
At the request of the Nuclear Regulatory Commission Region III Office, the Environmental Survey and Site Assessment Program of Oak Ridge Associated Universities conducted a confirmatory radiological survey of the former Burial Ground at the Cimarron Corporation Facility during December 9 through 12, 1991. The survey included surface scans, exposure rate measurements, and the determination of radionuclide concentrations in soil samples.
Surface scans identified one area of slightly elevated direct radiation; however, the exposure rate measurement was within the guideline value.
Total thorium concentrations in all samples were below the concentration guideline.
Total uranium concentrations in all samples, except five, were below the uranium concentration guideline. Five surface soil samples exceeded the concentration guideline; these samples were H:\\CLAIBORT\\FILES\\REPORTS\\CIMARRON 8
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collected from 69N, 62E; 95N, SOE; 9 lN, 42E; 108N, 53E and 25N, 70E and total uranium concentrations were 44 pCi/g, 33 pCi/g, 33~2 pCi/g, 95.6 pCi/g, and 43.6 pCi/g respectively.
The results of the confirmatory radiological survey indicate that all samples, with 5 exceptions, were below the concentration guidelines for total uranium and total thorium. The locations which exceed the uranium concentration guideline are scattered over the former Burial Ground Area.
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SFC77 OKLAHOMA FIGURE 1: Location of the Cimarron Facility, Crescent, Oklahoma H:\\CLAIBORT\\PILES\\REPORTS\\CIMARRON 10 NOT TO SCALE N
July 21, 1992
SFC1 MIXED OXIDE PLANT
~x~----it-X~--1t-X FENCE FORMER BURIAL GROUND ~
AREA N
NOT TO SCALE FIGURE 2: Plot Plan -
Cimarron Facility H:\\CLAIBORT\\FILES\\REPORTS\\CIMARRON 11 July 21, 1992
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} 2 July 21, 1992
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Elevated Direct Radiation Location H:\\CLAJBORT\\FILES\\REPORTS\\CIMARRON 13 July 21. 1992
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Surface Soil Sampling Locations at Grid Line Intersections H:\\CLAIBORT\\FILBS\\RBPORTS\\CIMARRON 14 July 21, 1992
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Surface Soil Sampling Locations from Trench Excavations and Soil Piles B:\\CLAIBORT\\PILES\\RBPORTS\\CIMARRON 15 July 21, 19~1:'
SFC3e OE SAMPLING LOCATIONS
- BOREHOLE 10E 20E JOE 40E f :.:*.:*:) EXCAVATED AREAS
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Subsurface Soil Sampling Locations H:\\CLAIBORT\\PJLES\\RBPORTS\\CIMARRON 16 July 21, 1992
SFC79 CRESCENT CRESCENT SCHOOL 7
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O KILOMETERS 4 FIGURE 8: Background Measurement and Sampling Locations H:\\CLAIBORT\\FILBS\\REPORTS\\CIMARRON 17 77 July 21. 1992
TABLE 1 EXPOSURE RATE MEASUREMENTS AND RADIONUCLIDE CONCENTRATIONS IN SURFACE SOIL SAMPLES FORMER BURIAL GROUND CIMARRON CORPORATION FACILITY CRESCENT,OKLAHOMA Exposure Rate Radionuclide Concentration (pCi/g)b Location*
(µRib) at 1 m above surface U-235 U-238 Total uc Total Thd Grid Line Cntersections lON, lOE 10 0.2 +/- 0. 4c 1.8 +/- 1.5 6.0
- 1. 7 11N, 20E 10 0.3 +/- 0.1 1.5 +/- 0.6 7.8 1.4 12N, JOE 10 0.3 +/- 0.3 0.9 +/- 1.2 7.2 1.3 14N, 40E 10 0.1 +/- 0.1 3.4 +/- 1.9 5.5 2.1 15N, SOE 10 0.2 +/- 0.1 1.6 +/- 0.8 5.8 1.9 15N, 60E 9
0.3 +/- 0.1 4.2 +/- 1.8 11 2.5 17N, 70E 10 0.7 +/- 0.6 9.1 +/- 2.3 24
- 1. 6 17N, 75E 9
___ t 2.6 20N, lOE 10 0.2 +/- 0.1 1.7 +/- 0.7 5.9 2.2 20N, 20E 9
0.3 +/- 0.1 2.8 +/- 1.3 9.1 0.7 20N, JOE 10 0.1 +/- 0.1 1.3 +/- 0.8 3.4 0.4 20N, 40E 10 0.2 +/- 0.1 1.1 +/- 0.9 7.3 2.0 20N, SOE 10 0.2 +/- 0.1 3.2 +/- 1.1 7.4 1.5 20N, 60E 10 0.1 +/- 0.1 1.4 +/- 0.8 3.5
- 1. 7 20N, 70E 10 0.2 +/- 0.1 2.5 +/- 0.9 6.7
- 1. 6 20N, 75E 10 2.2 JON, lOE 10 0.3 +/- 0.1
<1.5
<7.8 1.9 JON, 20E 9
0.4 +/- 0.3 3.1 +/- 0.9 11 1.5 JON, JOE 10 0.2 +/- 0.1 2.8 +/- 1. 6 7.0 2.2 JON, 40E 10 0.2 +/- 0.1 1.9 +/- 1.1 6.1 1.9 H:\\CLAJBORT\\FILP..S\\REPORTS\\CIMARRON 18 July 21, 1992
Location*
JON, SOE JON, 60E 30N, 70E JON, 74E 40N, lOE 40N, 20E 40N, JOE 40N, 40E 40N, SOE 40N, 60E 40N, 70E 40N, 74E SON, lOE SON, 20E SON, JOE SON, 40E SON, SOE SON, 60E SON, 70E SON, 73E TABLE 1 (Continued)
EXPOSURE RA TE MEASUREMENTS AND RADIONUCLIDE CONCENTRATIONS IN SURFACE SOIL SAMPLES FORMER BURIAL GROUND CIMARRON CORPORATION FACILITY CRESCENT,OKLAHOMA Exposure Rate Radionuclide Concentration (pCi/gt
(µR/h) at 1 m above surface U-235 U-238 Total uc 10 0.4 +/- 0.5 7.4 +/- 1.4 16 10 0.3 +/- 0.1 1.9 +/- 0.8 8.2 10 0.3 +/- 0.1 3.6 +/- 0.8 9.9 9
0.3 +/- 0.1 2.9 +/- 0.9 9.2 9
0.2 +/- 0.1
- 1. 7 +/- 0.6 5.9 9
0.3 +/- 0.1 3.4 +/- 0.9 9.7 10 0.1 +/- 0.2 1.5 +/- 0.6 3.6 10 0.5 +/- 0.3 2.0 +/- 0.7 13 11 0.1 +/- 0.1
- 1. 3 +/- 1.2 3.4 10 0.1 +/- 0.1
<2.0
<4.1 9
0.1 +/- 0.2 0.6 +/- 0.8 2.7 9
0.3 +/- 0.3 3.7 +/- 1.2 10 10 0.1 +/- 0.1 1.4 +/- 1.4 3.5 9
0.2 +/- 0.1 2.0 +/- 0.8 6.2 10 0.2 +/- 0.1 2.4 +/- 1.3 6.6 10 0.1 +/- 0.1 3.5 +/- 1. 7 5.6 11 0.3 +/- 0.1 2.1 +/- 1.0 8.4 10 0.2 +/- 0.1 1.4 +/- 0.5 5.6 10 0.3 +/- 0.1 2.1 +/- 1.0 8.4 9
0.2 +/- 0.1 1.4 +/- 1.3 5.6 H:\\CLAIBORT\\FILP..S\\REPORTS\\CIMAR.R.ON 19 Total Thd 5.5 1.9 1.4 1.5 1.6 1.6 1.4 2.0 1.7 1.8 1.1 2.3 1.5 1.9 1.8 2.3 2.8 2.0 2.3 1.8 July 21, 1992
TABLE 1 (Continued)
EXPOSURE RA TE MEASUREMENTS AND RADIONUCLIDE CONCENTRATIONS IN SURFACE SOIL SAMPLES FORMER BURIAL GROUND CIMARRON CORPORATION FACILITY CRESCENT,OKLAHOMA Exposure Rate Radionuclide Concentration (pCi/ g)b Location*
<,&Rib) at 1 m above surface U-235 U-238 Total uc 60N, lOE 10 0.2 +/- 0.1 2.2 +/- 0.8 6.4 60N, 20E 10 0.1 +/- 0.1 1.4 +/- 0.9 3.5 60N, JOE 10 0.4 +/- 0.5 4.2 +/- 2.1 13 60N, 40E 10 0.2 +/- 0.1
<1.2
<5.4 60N, SOE 11 0.3 +/- 0.1 1.4 +/- 1.1 7.7 60N, 60E 10 0.4 +/- 0.1 2.9 +/- 1.5 11 60N, 70E 9
0.2 +/- 0.1 2.0 +/- 1.2 6.2 60N, 72E 10 0.2 +/- 0.3 1.9 +/- 1.1 6.1 70N, lOE 10 0.1 +/- 0.1
- 1. 2 +/- 1. 0 3.3 70N, 20E 10 0.2 +/- 0.1
- 1. 2 +/- 1.0 5.4 70N, JOE 10 0.9 +/- 0.6 7.9 +/- 1.6 27 70N, 40E 11 0.9 +/- 0.5 10.8 +/- 2.3 30 70N, SOE 11 0.3 +/- 0.1 3.0 +/- 1.1 9.3 70N, 60E 11 0.8 +/- 0.4 6.3 +/- 1.0 23 70N, 70E 10 0.2 +/- 0.1 2.1 +/- 0.8 3
70N, 72E 10 0.4 +/- 0.5 5.6 +/- 1.7 14 SON, lOE 10 0.3 +/- 0.2
<1.4
<7.7 SON, 20E 11 0.2 +/- 0.1 2.4 +/- 1.7 6.6 SON, JOE 11 0.2 +/- 0.1 2.2 +/- 1.1 6.4 SON, 40E 10 0.2 +/- 0.1
- 1. 6 +/- 0.9 5.8 H:\\CLAJBOR.T\\FILP.S\\REPOR.TS\\CIMAR.RON 20 Total Thd 1.5 2.1 2.3 1.6 2.0 2.5 1.9 2.0 1.9 1.8 2.3 2.3 1.7 1.9 2.1 2.9 1.6 2.1 2.0 2.1 July 21, 1992
TABLE 1 (Continued)
EXPOSURE RATE MEASUREMENTS AND RADIONUCLIDE CONCENTRATIONS IN SURFACE SOIL SAMPLES FORMER BURIAL GROUND CIMARRON CORPORATION FACILITY CRESCENT,OKLAHOMA Exposure Rate Radionuclide Concentration (pCi/ g)b Location*
(1&Rlh) at 1 m above surface U-235 U-238 Total uc SON, SOE 11 0.9 +/- 0.5 3.1 +/- 0.9 22 SON, 60E 10 SON, 70E 10 0.3 +/- 0.1 2.3 +/- 1.6 8.6 SON, 71E 9
0.3 +/- 0.4 2.8 +/- 1.0 9.1 90N, lOE 10 0.2 +/- 0.1 1.7 +/- 1.4 5.9 90N, 20E 10 0.2 +/- 0.1 2.1 +/- 0.7 6.3 90N, JOE 10 0.5 +/- 0.3 5.6 +/- 2.0 16 90N, 40E 10 0.2 +/- 0.1 1.1 +/- 0.9 5.3 90N, SOE 10 0.6 +/- 0.4 3.7 +/- 1.4 16 90N, 60E 10 0.3 +/- 0.3 6.5 +/- 1.1 13 90N, 70E 10 0.2 +/- 0.1 3.1 +/- 1.5 7.3 98N, lOE 10 0.5 +/- 0.3
- 1. 7 +/- 0.9 12 lOON, 20E 11 0.1 +/- 0.1 2.0 +/- 1.3 4.1 l.OON, JOE 11 0.6 +/- 0.3 5.8 +/- 1.2 18 lOON, 40E 10 0.2 +/- 0.1 1.9 +/- 1.2 6.1 lOON, SOE 12 0.5 +/- 0.3 5.2 +/- 1. 0 16 lOON, 60E 10 0.6 +/- 0.1 6.1 +/- 1.0 19 lOON, 69E 10 0.3 +/- 0.1 2.3 +/- 0.8 8.6 llON, JOE 11 0.6 +/- 0.4 4.2 +/- 0.7 17 llON, 40E 11 0.5 +/- 0.4 5.6 +/- 1.0 16 H:\\CLAIBORT\\FILBS\\REPORTS\\CIMARRON 21 Total Thd 1.9 1.7 2.5 2.4 1.7 1.7 2.2 2.2 1.2 1.5 1.9 1.6 1.7 2.1
<1.4 1.8 1.8 1.8 2.2 2.2 July 21, 1992
TABLE 1 (Continued)
EXPOSURE RATE MEASUREMENTS AND RADIONUCLIDE CONCENTRATIONS IN SURFACE SOIL SAMPLES FORMER BURIAL GROUND CIMARRON CORPORATION FACILITY CRESCENT,OKLAHOMA Exposure Rate Radionuclide Concentration (pCi/ g)b Location*
(1&Rlh) at 1 m Total Thd above surface U-235 U-238 Total uc llON, SOE 11 0.7 +/- 0.4 6.1 +/- 2.0 21 1.9 llON, 62E 11 0.2 +/- 0.1
- 1. 6 +/- 1.0 5.8 1.4 117N, SOE 10 0.5 +/- 0.4 2.7 +/- 1.1 13 2.1 120N, JOE 11 0.8 +/- 0.4 5.0 +/- 1.4 22 2.6 120N, 40E 10 0.3 +/- 0.1 4.8 +/- 2.0 11 1.5 124N, 40E 10 0.1 +/- 0.1
<1.5
<3.6 2.1 130N, JOE 10 0.3 +/- 0.4 2.7 +/- 1.0 9.0 1.6 Trench 1.1 JON, E Wall 10 0.1 +/- 0.1
<1.9
<4.0 1.5 JON, W Wall 10 0.3 +/- 0.1
<1.9
<8.2 1.9 40N, E Wall 10 0.2 +/- 0.1 1.4 +/- 1.1 5.6
- 1. 7 40N, W Wall 10 0.2 +/- 0.1
<1.1
<5.3
<1.7 SON, E Wall 10 0.1 +/- 0.1
<1.6
<3.7 1.6 SON, W Wall 10
<0.4
<1.7
<10 1.4 60N, E Wall 11 0.1 +/- 0.1
<1.0
<3.1
<1.0 60N, W Wall 10 0.2 +/- 0.1
<1.3
<5.5 1.9 70N, E Wall 10 0.2 +/- 0.1 1.7 +/- 1.3 5.9
- 1. 7 SON, E Wall 10 0.1 +/- 0.1
<1.2
<3.3 2.0 lOON, E Wall 10 0.3 +/- 0.1 3.1 +/- 1.8 9.4 2.2 H:\\CLAIBORT\\FILES\\REPORTS\\CIMARRON 22 July 21, 1992
TABLE 1 (Continued)
EXPOSURE RATE MEASUREMENTS AND RADIONUCLIDE CONCENTRATIONS IN SURFACE SOIL SAMPLES FORMER BURIAL GROUND CIMARRON CORPORATION FACILITY CRESCENT,OKLAHOMA Exposure Rate Radionuclide Concentration (pCi/ g)b Locationa
(µR/h) at 1 m above surface U-235 U-238 Total uc Trench f2 40N, E Wall 10 0.2 +/- 0.1 1.2 +/- 0.7 5.4 40N, W Wall 10
<0.5
<2.0
<13 SON, E Wall 10 0.9 +/- 0.1 3.9 +/- 1.5 23 SON, W Wall 10
<0.5
<1.8
<12 60N, E Wall 11 0.1 +/- 0.1
<1.2
<3.3 60N, W Wall 11
<0.4
<1.9
<10 70N, W Wall 11 0.4 +/- 0.1 3.8 +/- 1.6 12 SON, W Wall 10 0.3 +/- 0.1 1.5 +/- 0.9 7.8 100N, W Wall 10 0.3 +/- 0.1
<2.1
<8.4 Trench f3 70N, E Wall 10 0.2 +/- 0.1
<1.2
<5.4 70N, W Wall 11
<0.5 2.5 +/- 1.2 13 SON, E Wall 11 SON, W Wall 11 0.2 +/- 0.1 1.8 +/- 0.7 6.0 lOON, E Wall 11 0.1 +/- 0.1
<1.8
<3.9 100N, W Wall 11 0.1 +/- 0.1
<1.2
<3.3 Trench f4 SON, E Wall 10 0.1 +/- 0.1
<1.9
<4.0 SON, W Wall 11 0.3 +/- 0.1
<1.2
<7.5 60N, E Wall 10 0.2 +/- 0.1 2.6 +/- 1.3 6.8 60N, W Wall 10 0.2 +/- 0.1
<1.3
<5.5 H:\\CLAIBORT\\FILP.s\\REPORTS\\CIMARRON 23 Total Thd 1.4 2.1 1.4
<1.5 1.8 1.6 1.5 1.5 2.0 1.9 1.9
<1.3 2.3 2.0 1.s
<1.7
<1.7 2.2 1.8 1uly 21, 1992
Location*
70N, E Wall 70N, W Wall SON, E Wall SON, W Wall 90N, W Wall lOON, E Wall lOON, W Wall Pile ;l1 60N, 82E 60N, SSE 70N, SOE 70N, SSE SON, 83E 82N, SOE Pile ;l2 3N, SSE llN, SSE Pile ;l3 lON, 40E lON, SOE lON, 60E lON, 70E.
lON, 75E TABLE 1 (Continued)
EXPOSURE RATE MEASUREMENTS AND RADIONUCLIDE CONCENTRATIONS IN SURFACE SOIL SAMPLES FORMER BURIAL GROUND CIMARRON CORPORATION FACILITY CRESCENT,OKLAHOMA Exposure Rate Radionuclide Concentration (pCi/ g)b
(µRib) at 1 m above surface U-235 U-238 Total uc 11
<0.5
<1.9
<12 11 0.2 +/- 0.1
<1.3
<5.5 10
<0.5
<1.9
<12 10 0.2 +/- 0.1 1.9 +/- 1.0 6.1 10 0.2 +/- 0.1 2.9 +/- 0.9 7.1 10 0.4 +/- 0.2 3.8 +/- 1.7 12 10 0.5 +/- 0.1 3.8 +/- 0.9 14 10 0.3 +/- 0.1 4.7 +/- 1.4 11 10 0.3 +/- 0.1 3.4 +/- 0.9 9.7 10 0.5 +/- 0.3 s.o +/- 1.3 16 10 0.2 +/- 0.1 2.1 +/- 0.8 6.3 10 0.4 +/- 0.4 4.5 +/- 1.8 13 10 11 0.2 +/- 0.2 2.2 +/- 0.9 6.4 10 0.1 +/- 0.1 1.1 +/- 0.6 3.2 10 0.2 +/- 0.1 1.2 +/- 1.0 5.4 10 0.1 +/- 0.1
- 1. 7 +/- 0.7 3.8 10 0.2 +/- 0.1 1.8 +/- 1.6 6.0 10 0.2 +/- 0.1 2.3 +/- 0.7 6.5 10 0.2 +/- 0.1 2.0 +/- 1.3 6.2 H:\\CLAIBORT\\FILP.S\\REPORTS\\CIMARRON 24 Total Thd 2.1 1.6 1.8 1.3
<1.4 2.1 2.2 1.3 1.4 1.8 2.3 1.6 1.2 2.0 1.7 1.8 1.7 1.4 1.6 1.7 July 21, 1992
Location*
Pile fi.4 o, 45E o, SOE o, 60E o, 70E 5S, SOE ss, 60E lOS, SOE lOS, 60E Previousl:x Identified Areas of Elevated Activit:x 57N, 64E 65N, 62E 69N, 62E 70N, 59E 71N, 61E 71N, 65E 75N, 63E 77N, 63E 78N, 63E TABLE 1 {Continued)
EXPOSURE RATE MEASUREMENTS AND RADIONUCLIDE CONCENTRATIONS IN SURFACE SOIL SAMPLES FORMER BURIAL GROUND CIMARRON CORPORATION FACILITY CRESCENT, OKLAHOMA Exposure Rate Radionuclide Concentration {pCi/g)b
(µR/h) at 1 m above surface U-235 U-238 Total uc 10 0.4 +/- 0.2 5.1 +/- 1.0 14 10 0.3 +/- 0.3 7.8 +/- 1.8 14 10 0.2 +/- 0.1 2.0 +/- 0.6 6.2 10 0.2 +/- 0.1 1.1 +/- 0.7 5.3 10 0.3 +/- 0.2 3.3 +/- 0.9 9.6 10 0.2 +/- 0.1 2.0 +/- 1.5 6.2 10 0.6 +/- 0.4 6.6 +/- 2.0 19 10 0.6 +/- 0.3 9.2 +/- 0.8 22 10 0.3 +/- 0.1 3.0 +/- 1.7 9.3 11 0.2 +/- 0.1 1.6 +/- 1.4 5.8 11 1.6 +/- 0.5 9.9 +/- 2.2 44 11 11 0.7 +/- 0.3 7.0 +/- 1.4 22 11 0.2 +/- 0.1 2.7 +/- 0.8 6.9 10 0.3 +/- 0.1 3.5 +/- 1.4 9.8 10 0.4 +/- 0.3 3.8 +/- 1.0 12 10 0.2 +/- 0.3 3.9 +/- 1.8 8.1 H:\\CLAIBORT\\FlLES\\REPORTS\\CIMARRON 25 Total Thd 2.5 1.6 1.6 1.7 2.3 1.7 2.7 2.8 2.8 3.6 1.4 2.2 2.0 3.0 2.0 2.0 2.8 July 21. 1992
TABLE 1 (Continued)
EXPOSURE RATE MEASUREMENTS AND RADIONUCLIDE CONCENTRATIONS IN SURFACE SOIL SAMPLES FORMER BURIAL GROUND CIMARRON CORPORATION FACILITY CRESCENT,OKLAHOMA Exposure Rate Radionuclide Concentration (pCi/g)b Locationa (l'R/h) at 1 m above surface U-235 U-238 83N, 45E 10 0.2 +/- 0.1
- 1. 7 +/- o.8 84N, 65E 10 0.5 +/- 0.1 4.3 +/- 1.3 85N, 45E 10 0.2 +/- 0.1 2.4 +/- 0.8 85N, SOE 10 0.5 +/- 0.4 5.7 +/- 1.8 87N, 65E 10 0.3 +/- 0.4 5.4 +/- 1.6 90N, 66E 10 0.3 +/- 0.3 5.3 +/- 1.0 90N, 68E 9
0.3 +/- 0.3 1.8 +/- 1.0 91N, 42E 10 95N, SOE 11 0.2 +/- 0.1 3.4 +/- 1.7 Area of Elevated Direct Radiation 108N, 53E 14 aRefer to Figures 4-6.
bBased on gamma spectrometry analysis.
ccalculated using a U-234:U-235 activity ratio of 20: 1.
dCalculated by adding concentrations of Th-228 and Th-232.
Total uc 5.9 15 6.6 16 12 12 8.1 7.6
°Uncertainties represent the 95% confidence level, based only on counting statistics.
'--Indicates analysis was performed by alpha spectrometry; see Table 2.
H:\\CLAmOR1'FILBS\\REPORTS\\CIMARRON 26 Total Thd 1.5 2.3
- 1. 7 1.4 1.8 1.9 1.0 1.8
- 1. 7 4.2 July 21. 1992
TABLE 2 ISOTOPIC URANIUM CONCENTRATIONS IN SOIL SAMPLES FORMER BURIAL GROUND CIMARRON CORPORATION FACILITY CRESCENT, OKLAHOMA Uranium Concentration (pCi/g)b Location 8
U-234 U-235 U-238 Gridline Intersections 17N, 75E 17.1 +/- 0. ac 0.9 +/- 0.3 7.6 +/- 0.6 20N, 75E 20.0 +/- 0.9 0.8 +/- 0.2 10.3 +/- 0.6 SON, 60E 10.4 +/- 0.5 0.5 +/- 0.1 7.6 +/- 0.4 Trench #3 SON, E Wall 17.2 +/- 0.7 0.9 +/- 0.2 7.7 +/- 0.4 Pile #1 82N, SOE 14.6 +/- 0.6 0.8 +/- 0.2 6.7 +/- 0.4 Previously Identified Areas of Elevated Activity 70N, 59E 12.6 +/- 0.7 0.5 +/- 0.2 11.6 +/- 0.7 91N, 42E 21.7 +/- 0.9 0.8 +/- 0.2 10.7 +/- 0.6 Areas of Elevated Direct Radiation 108N, 53E 66.2 +/- 1.4 3.2 +/- 0.4 26.2 +/- 0.9 Subsurface 25N, 70E (0-15 cm) 22.2 +/- 0.8 1.4 +/- 0.2 20.0 +/- 0.7 55N, 30E (15-40 cm) 12.0 +/- 0.6 0.7 +/- 0.2 7.0 +/- 0.4 90N, 65E (15-35 cm) 12.8 +/- 0.5 0.6 +/- 0.1 5.3 +/- 0.3 120N, 35E (110-170 cm) 0.5 +/- 0.1 0.1 +/- 0.1 0.4 +/- 0.1 aRefer to Figures 4-7.
bBased on alpha spectrometry analysis.
CUncertainties represent the 95% confidence level, based only on counting statistics.
H:\\CLAIBORT\\PIU!S\\RBPORTS\\CIMARRON 27 Total U 25.6 +/- 1.0 31.0 +/- 1.1 18.5 +/- 0.7 25.8 +/- 0.8 22.1 +/- 0.7 24.7 +/- 1.0 33.2 +/- 1.1 95.6 +/- 1. 7 43.6 +/- 1.1 19.7 +/- 0.7 18.6 +/- 0.6 0.9 +/- 0.2 July 21, 1992
TABLE 3 RADIONUCLIDE CONCENTRATIONS IN SUBSURFACE SOIL SAMPLES FORMER BURIAL GROUND CIMARRON CORPORATION FACILITY CRESCENT,OKLAHOMA Radionuclide Concentration (pCi/ g)b Location*
Depth (cm)
U-235 U-238 Total UC 25N, 70E 0-15
___ c 15-40 0.5 +/- 0. 4f 10.8 +/- 1.3 21 40-80 0.3 +/- 0.3 7.0 +/- 1.9 13 80-130 0.3 +/- 0.1 3.6 +/- 0.9 9.9 130-150 0.2 +/- 0.1 2.6 +/- 1.4 6.8 JON, 35E 0-15 0.2 +/- 0.1 3.4 +/- 1.5 7.6 15-50 0.2 +/- 0.1
<1.3
<5.5 50-75 0.1 +/- 0.1 1.8 +/- 1.2 3.9 75-120 0.1 +/- 0.1 2.0 +/- 0.9 4.1 120-150 0.3 +/- 0.1
- 1. 7 +/- 1.3 8.0 31N, 60E 0-15 0.3 +/- 0.3 2.5 +/- 1.4 8.8 15-40 0.2 +/- 0.1 1.1 +/- 0.6 5.3 40-80 0.2 +/- 0.1 1.3 +/- 1.0 5.6 80-130 0.2 +/- 0.2 2.2 +/- 1.0 6.4 130-150 0.3 +/- 0.3
<1.7
<8.0 45N, 60E 0-15 0.6 +/- 0.4 7.0 +/- 1.2 20 15-50 0.2 +/- 0.3 2.7 +/- 1.0 6.9 50-90 0.2 +/- 0.3 1.1 +/- 0.8 5.3 90-130 0.2 +/- 0.1 1.9 +/- 1.5 6.1 130-150 0.2 +/- 0.2 1.7 +/- 0.7 5.9 SON, 66E 0-15 0.2 +/- 0.1 1.9 +/- 0.7 6.1 15-45 0.2 +/- 0.1 1.6 +/- 1.0 5.8 45-75 0.2 +/- 0.2 0.8 +/- 0.5 5.0 55N, JOE 0-15 0.2 +/- 0.1 2.1 +/- 0.9 6.3 15-40 40-50 0.1 +/- 0.1 0.9 +/- 0.6 3.0 70N, JOE 0-15 0.3 +/- 0.1 2.1 +/- 1.7 8.4 15-40 0.2 +/- 0.1 1.4 +/- 0.8 5.6 40-80 0.4 +/- 0.4 0.4 +/- 0.4 8.8 80-120 0.4 +/- 0.4 2.0 +/- 0.8 10 120-150 0.3 +/- 0.3 2.8 +/- 1.4 9.1 H:\\CLAIBOR.T\\~\\REPOR.TS\\CIMARRON 28 Total Thd 1.6 1.8 1.4 1.1 1.7
<1.5 1.5 1.7 1.4 1.4 2.4 1.5 1.7
- 1. 6 1.2 4.9 2.0 2.0 1.8 2.0 2.0 1.4 1.1 1.6 0.7 1.1 2.0 2.5 2.2 1.7 1.8 July 21. 1992
TABLE 3 (Continued)
RADIONUCLIDE CONCENTRATIONS IN SUBSURFACE SOIL SAMPLES FORMER BURIAL GROUND CIMARRON CORPORATION FACILITY CRESCENT,OKLAHOMA Radionuclide Concentration (pCi/g)b Location*
Depth (cm)
U-235 U-238 Total ue 70N, 57E 0-15 0.2 +/- 0.2 3.6 +/- 0.8 7.8 15-30 0.8 +/- 0.3 10.4 +/- 3.1 27 73N, 66E 0-15 0.3 +/- 0.2 2.7 +/- 0.8 9.0 15-30 o.s +/- 0.4 4.1 +/- 2.1 15 90N, 65E 0-15 0.4 +/- 0.2 4.8 +/- 1.0 13 15-35 35-50 0.8 +/- 0.3 8.6 +/- 1.2 25 91N, 27E 0-15 0.4 +/- 0.1 4.3 +/- 1.4 12 15-40 0.3 +/- 0.1 1.7 +/- 0.5 8.0 40-90 0.2 +/- 0.1
- 1. 7 +/- 1.0 5.9 90-130 0.2 +/- 0.1 1.9 +/- 0.8 6.1 130-150
<0.5
<1.9
<12 95N, 45E 0-15 0.2 +/- 0.1 1.9 +/- 0.8 6.1 15-50 0.2 +/- 0.1
<1.9
<6.1 50-70 0.2 +/- 0.1 2.4 +/- 0.9 6.6 70-130 0.2 +/- 0.1
- 1. 3 +/- 1. 2 5.4 130-150 0.7 +/- 0.3 7.8 +/- 1.1 23 95N, SOE 0-15 1.2 +/- 0.4 7.9 +/- 0.8 33 15-40 0.4 +/- 0.1 4.3 +/- 1. 7 13 40-50 0.4 +/- 0.3 5.4 +/- 1.2 14 lOON, 25E 0-15 0.4 +/- 0.3 4.3 +/- 1.3 13 15-40 0.2 +/- 0.1 3.8 +/- 1.2 6.0 40-70 0.3 +/- 0.3 2.7 +/- 1.0 9.0 70-120 0.2 +/- 0.1 2.4 +/- 1.3 6.6 H:\\CLAIBORT\\FILBS\\REPORTS\\CIMARRON 29 Total Thd 1.6 2.1 1.6 1.7 1.8 1.6 1.8 1.6 1.6 1.9 1.8 1.8 1.7 1.6 1.9 1.5 1.5 2.0 2.4 2.2 2.2 2.5 1.5 1.5 July 21, 1992
TABLE 3 (Continued)
RADIONUCLIDE CONCENTRATIONS IN SUBSURFACE SOIL SAMPLES FORMER BURIAL GROUND CIMARRON CORPORATION FACILITY CRESCENT,OKLAHOMA Radionuclide Concentration (pCi/g)b LocatiOD 8
Depth (cm)
U-235 U-238 105N, 37E 0-15 0.5 +/- 0.1 4.8 +/-
15-50 0.3 +/- 0.2 3.0 +/-
50-80 0.2 +/- 0.1 2.7 +/-
80-130 0.3 +/- 0.1 2.2 +/-
120N, 35E 0-15 0.4 +/- 0.1 5.2 +/-
15-40 0.4 +/- 0.1 5.8 +/-
40-75 0.4 +/- 0.4 4.5 +/-
75-110 0.4 +/- 0.1 4.8 +/-
110-170
- Refer to Figure 7.
bBased on gamma spectrometry analysis.
ccalculated using a U-234:U-235 activity ratio of 20: 1.
dCalculated by adding concentrations of Th-228 + Th-232.
2.2 0.8 1.4 0.9 2.1 1.2 1.5 1.0 Total uc 15 9.3 6.9 8.5 14 14 13 13 ---
0---Indicate analysis was performed by alpha spectrometry analysis; see Table 2.
'Uncertainties represent the 95 % confidence level, based only on counting statistics.
H:\\CLAmORT\\FILES\\REPORTS\\CIMARRON 30 Total Thd 1.2 1.0 1.2 1.7 2.3 2.4 1.5
- 1. 6 1.6 July 21, 1992
TABLE 4 BACKGROUND EXPOSURE RATES AND RADIONUCLIDE CONCENTRATIONS IN SOIL FORMER BURIAL GROUND CIMARRON CORPORATION FACILITY CRESCENT,OKLAHOMA Exposure Rate (µR/h)
Radionuclide Concentration (pCi/ g)b Location*
at 1 m above the surf ace 1
10 2
9 3
9 4
10 5
10 6
10 Average 10
- Refer to Figure 8.
bBased on gamma spectrometry analysis.
ccalculated based on natural activity ratios.
Total uc 1.5 1.3
<1.7 2.0 1.9
<1.2 1.6
~alculated by adding concentrations of Th-228 + Th-232.
H:\\CLAIBORT\\FILES\\REPORTS\\CIMARRON 31 Total Thd 1.2 1.1 0.9 1.4 1.9 2.1 1.4 July 21. 1992
REFERENCES
- 1.
"Interim Report of Confirmatory Survey of Portions of the Sequoyah Fuels Corporation Cimarron Plant, Crescent Oklahoma," ORAU, January 1989.
- 2.
"Cimarron Facility, Contaminated Waste Burial Ground Decontamination and Final Survey Report°, Cimarron Corporation, November 1991.
- 3.
"Confirmatory Radiological Survey Plan for the On-Site Burial Ground of the Cimarron Corporation Facility, Crescent, Oklahoma," ORAU, November 1991.
- 4.
11Policy and Guideline Directive FC91-2, Standard Review Plan:
Evaluating Decommissioning Plans for Licenses Under 10 CFR Parts 30, 40, and 70," U.S. Nuclear Regulatory Commission, August 1991.
H:\\CLAIBORT\\FILES\\RBPORTS\\CIMARRON 32 July 21, 1992
APPENDIX A MAJOR SAMPLING AND ANALYTICAL EQUIPMENT H:\\CLAmORT\\FILES\\REPORTS\\ClMARRON 1uly 21, 1992
APPENDIX A MAJOR SAMPLING AND ANALYTICAL EQUIPMENT The display or description of a specific product is not to be construed as an endorsement of that product or its manufacturer by the authors or their employer.
A.
Direct Radiation Measurements Eberline PRM-6 Portable Ratemeter (Eberline, Santa Fe, NM)
Victoreen Nal Scintillation Detector Model 489-55 (Victoreen, Cleveland, OH)
Reuter-Stokes Pressurized Ionization Chamber Model RSS-111 (Reuter-Stokes, Cleveland, OH)
B.
Laboratory Analytical Equipment High-Purity Germanium Coaxial Well Detector Model GWL-1102010-PWS-S, 23 % efficiency (EG&G ORTEC, Oak Ridge, TN)
Used in conjunction with:
Lead Shield, G-16 (Applied Physical Technology, Atlanta, GA)
Multichannel Analyzer ND-66/Micro Vaxll (Nuclear Data, Schaumburg, IL/Digital Equipment Corp., Maynard, MA)
H:\\CJ.AIBOR.T\\FJLES\\RBPOR.TS\\CIMARRON A-1 July 21. 1992
Alpha Spectrometry System Tennelec Electronics (Tennelec, Oak Ridge, TN)
Solid State Surface Barrier Detectors (EG&G Ortec, Oak Ridge, TN)
(Tennelec, Oak Ridge, TN)
Multichannel Analyzer ND-66 (Nuclear Data, Schaumberg, IL)
H:\\CLAJBORT\\PILES\\REPORTS\\CIMARRON A-2 July 21, 1992
APPENDIX B
- MEASUREMENT AND ANALYTICAL PROCEDURES H:\\CLAmORT\\Fll.ES\\RBPORTS\\CIMARRON 1uly 21, 1992
APPENDIX B MEASUREMENT AND ANALYTICAL PROCEDURES Surface Scans Surface scans were conducted using Nal scintillation detectors with ratemeters. The scans were performed by passing the probes slowly over the surface; the distance between the probe and the surface was maintained nominally at about 1 cm. Identification of elevated levels was based on increases in the audible signal from the recording or indicating instrument.
Gamma Exposure Rate Measurements Measurements of gamma exposure rates were performed using portable ratemeters with gamma scintillation detectors. Count rates were converted to exposure rates (µR/h) by cross-calibrating with a pressurized ion chamber.
Gamma Spectroscopy The samples were placed in an appropriate container chosen to reproduce the calibrated counting geometry. Net weights were determined and the samples counted using high purity intrinsic germanium detectors coupled to a Nuclear Data Model ND-66/Micro V axil pulse height analyzer system. Background and Compton stripping, peak search, peak identification, and concentration calculations were performed using the computer capabilities inherent in the analyzer system.
Energy peaks, used for determination of radionuclides of concern, were:
U-238 U-235 Th-228 Th-232 0.093 MeV from Th-234*
0.143 MeV 0.583 MeV from Tl-208*
0.911 MeV from Ac-228*
- Secular equilibrium assumed.
H:\\CLAIBORT\\FILES\\REPORTS\\CIMARRON B-1 July 21, 1992
Spectra were reviewed for other identifiable photopeaks at concentrations above those normally encountered in environmental media.
Alpha Spectroscopy Soil samples were dried and homogenized, and aliquots were dissolved by pyrosulfate fusion and precipitated by barium sulphate.
The barium sulphate precipitate was redissolved and the uranium was separated by liquid-liquid extraction. The uranium was then precipitated with a cerium fluoride carrier and counted using surface barrier detectors, alpha spectrometers, and a ND-66 multichannel analyzer.
Uncertainties and Detection Limits The uncertainties associated with the analytical data presented in the tables of this report represent the 95 % confidence level for that data. These uncertainties were calculated based on both the gross sample count levels and the associated background count levels. When the net sample count was less than the 95 % statistical deviation of the background count, the sample concentration was reported as less than the detection limit of the measurement procedure.
Because of variations in background levels, measurement efficiencies, and contributions from other radionuclides in samples, the detection limits differ from sample to sample and instrument to instrument. Additional uncertainties of+/- 6 to 10%, associated with laboratory procedures, have not been propagated into the.data presented in this report.
Quality Assurance Analytical and field survey activities were conducted in accordance with procedures from the following documents:
Survey Procedures Manual, Revision 6, February 1991 Quality Assurance Manual, Revision 4, April 1991 Laboratory Procedures Manual, Revision 6, April 1991 H:\\CLAmORT\\FlLES\\REPORTS\\CIMARRON B-2 July 21. 1992
The procedures contained in these manuals were developed to meet the requirements of DOE Order 5700.6B.
Calibration of all field laboratory instrumentation is based on NIST-traceable standards, when such standards are available. In cases where they are not available, standards of an industry recognized organization will be used.
Calibration of pressurized ionization chambers is performed by the manufacturer.
Quality Control procedures include:
Daily instrument background and check-source measurements to confirm that the equipment operation is within acceptable statistical fluctuations Participation in EPA and EML Quality Assurance Programs Training and certification of all individuals performing procedures Periodic internal and external audits H:\\CLAIBORT\\FJLP.s\\RBPORTS\\CIMARRON B-3 July 21, 1992
APPENDIX C GUIDELINES FOR RESIDUAL CONCENTRATIONS OF THORIUM AND URANIUM WASTES IN SOIL H:\\CLAIBORT\\FJLES\\REPORTS\\CIMARRON July 21, 1992
Guidelines for Residual Concentrations of Thorium and Uranium Wastes in Soil On October 23, 1981, the Nuclear Regulatory Commission published in the Federal Register a notice of Branch Technical Position on "Disposal or Onsite Storage of Thorium and Uranium Wastes from Past Operations." This document establishes guidelines for concentrations of uranium and thorium in soil, that will limit maximum radiation received by the public under various conditions of future land usage. These concentrations are as follows:
Material Natural Thorium (Th-232 + Th-228) with daughters present and in equilibrium Natural Uranium (U-238 + U-234) with daughters present and in equilibrium Depleted Uranium:
Soluble Insoluble Enriched Uranium:
Soluble Insoluble Maximum Concentrations (pCi/g) for various options 10 10 35 35 30 30 50 100 300 100 250 40 500 200 1,000 3,000 1,000 2,500
- Based on EPA cleanup standards which bmtt radiation to i mrad/yr to lung and 3 mrad/yr to bone from ingestion and inhalation and 10 µR/h above background from direct external exposure.
bBased on limiting individual dose to 170 mrem/yr.
cBased on limiting equivalent exposure to 0. 02 working level or less.
dBased on limiting individual dose to 500 mrem/yr and in case of natural uranium, limiting exposure to 0.02 working level or less.
H:\\CLAmORT\\FILES\\REPORTS\\CIMARRON C-1 July 21, 1992