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Category:CORRESPONDENCE-LETTERS
MONTHYEARML20155H9301998-11-0404 November 1998 Forwards Listed Canceled Financial Assurance Documents Re Decommissioning of Cintichem Facility in Tuxedo,Ny.Without Encls ML20154H6341998-10-0505 October 1998 Responds to Requesting That Order on Consent for Case D200059005 Be Terminated.Released from All Requirements Set in Order,Effective 981005 ML20237C4981998-08-19019 August 1998 Informs That Commission Has Issued Encl Order Terminating FOL R-81 for Cintichem 5 Megawatt Open Pool Nuclear Research Reactor IAW 901019 Application.Copies of Amend 16 to Idemnity Agreement B-14 Encl for Signature.Se & EA Encl ML20237C5491998-08-19019 August 1998 Informs That NRC Completed Review of Info Submitted by Cintichem,Inc to Support Decommissioning of Tuxedo,Ny Facility.No Further Remediation or Actions W/Respect to NRC Regulated Matl Required,Based on Conclusions ML20197C7691998-07-28028 July 1998 Responds to Requesting Amend to Order on Consent Case D200059005.Amend 10 Which Requires That Sampling of 001 Outfall & Retention Pond Continue Encl ML20236L7321998-06-0808 June 1998 Informs of Completed Review of Final Status Survey Rept for Decommissioning of Bldg 4.Facility May Be Released from Radiological Control.License Termination,Encl ML20236S0211998-06-0202 June 1998 Forwards Confirmatory Surveys of Bldgs & Areas of Cintichem Facility Located in Tuxedo,Ny.Radionuclide Concentration in Bedrock Soil Samples & Orise Resrad Calculation,Encl ML20248D6681998-05-27027 May 1998 Requests That Process for Terminating Licenses R-81 & SNM-639 Be Resumed Due to All Radioactive Matl Having Been Removed as Final Condition for Termination Subject Licenses ML20216C5311998-04-15015 April 1998 Forwards Results of NRC TLD Direct Radiation Monitoring Around Cintichem Facility for Fourth Quarter of 1997.Final Rept Due to Termination of Program ML20217Q6411998-02-10010 February 1998 Responds to Requesting Mod to Ref Order on Consent.Amend 9 to Order,Authorizing Most Changes Requested Enclosed ML20202A8051998-02-0202 February 1998 Forwards Amend 10 to License SNM-639,in Resonse to 971204 Request to Amend Decommissioning Plan for Tuxedo,Ny Facility to Reduce off-site Environ Monitoring Program ML20202E1941998-01-28028 January 1998 Forwards Amended Table Which Includes Sr-90 Data Re Final Survey of Soils at 001 Outfall.Conclusion That Survey Results Meet Soils Acceptance Criteria Has Not Changed ML20202E1841998-01-28028 January 1998 Forwards Revised Tables Including Sr-90 Analytical Results. Five Individual Samples from Adjacent Locations Consolidated Into One Sample for Sr-90 Analysis ML20202E4781998-01-19019 January 1998 Forwards Cintichem Final Status Survey Plan & Rept,Per Section 7 of Licensee Radiopharmaceutical Facilities Decommissioning Plan.W/O Encl ML20199C2511998-01-0202 January 1998 Responds to Concerning Status of mixed-waste at Cintichem Site.Attached Table Presents Overview of Radioactively Contaminated Waste That Remains to Be Disposed of from Decommissioning Project ML20198C8521997-12-23023 December 1997 Forwards Result of NRC TLD Direct Radiation Monitoring Around Cintichem Facility, for Third Quarter of 1997 ML20199B6091997-10-22022 October 1997 Forwards Characterization Rept for Union Carbide Spoils Area Tuxedo,Ny.Area Meets Criteria for Unrestricted Use ML20217G2501997-10-0808 October 1997 Forwards Response to 970819 RAI Re Survey Repts of Hot Laboratory Support Bldgs & Outdoor Areas Inside & Outside of RCA ML20199B6151997-10-0303 October 1997 Responds to 971002 Request for Mod to Order on Consent Case D200059005.Amend to Order on Consent Authorizing Changes Encl ML20199B6601997-10-0202 October 1997 Requests That Order on Consent D200059005 Be Amended to Allow for Delay in Analysis of Water Samples from S-12 for Gamma Emitting Radionuclides,As Currently Done W/Analysis for Sr-90 ML20211C5501997-09-22022 September 1997 Forwards Bedrock Dose Assessment Rept, Which Completes Final Survey Process.W/One Oversize Drawing ML20210R8271997-08-22022 August 1997 Forwards Results of NRC TLD Direct Radiation Monitoring for Second Quarter of 1997 ML20210Q6631997-08-19019 August 1997 Requests That Listed Info Be Submitted in Order to Complete Preliminary Review of Sections 11-18 of Cintichem Final Plant & Rept Submitted by 970606,27,0703,25 & 30 Ltrs ML20210L8541997-08-0505 August 1997 Informs That Responsibility for Non-Power Reactor Insp Program Has Been Transferred from Regional Ofc to Nrr.All Activities Re Non-Power Reactors Including Licensing,Insp & Operator Licensing Will Be Responsibility of NRR ML20149G7981997-07-0303 July 1997 Forwards Chapters 15 & 16 of Final Survey Repts for Cintichem Outdoor Areas Outside Former RCA, Which Describes Cintichem'S Approach to Conducting Final Survey for Areas of Property ML20149G9111997-06-27027 June 1997 Forwards Chapters 13 & 14 Final Survey Repts for Cintichem Outdoor Areas Inside of Former Rca. Chapter 14 Presents Results of Survey ML20140H0591997-04-24024 April 1997 Informs of Completion of All Remediation Work & Final Surveys Per Cintichem Decommissioning Plan.Will Submit Last Sections of Final Survey Rept for Review & Approval in May ML20137W1391997-04-0303 April 1997 Discusses Radiological Characterization Plan for Union Carbide Spoils Area ML20135D1601997-02-21021 February 1997 Forwards Results of TLD Direct Radiation Environ Monitoring Around Facility for Fourth Quarter of 1996 ML20133A4641996-12-20020 December 1996 Forwards Results of NRC TLD Direct Radiation Monitoring Around Cintichem Facility ML20133N0281996-12-19019 December 1996 Informs of Agreement to Extension of Deadlines for Weekly & Monthly Repts in Response to 961206 Request Re Reporting Requirements in Order of Consent Case D200059005 ML20132B6591996-12-0606 December 1996 Informs That License SNM-639 Will Remain in Effect Until Completion of Decommissioning Operations ML20134K7041996-11-14014 November 1996 Advises That SNM-639 License Expires on 961215,per Amend 7 Issued 950118.Request License Remain Effective Through June 1997,allowing Sufficient Time for Completing Work Outlined ML20134F7571996-10-29029 October 1996 Submits Response to Re Radiological Status of Bedrock at Tuxedo,Ny Facility ML20134F7611996-09-25025 September 1996 Provides Comments Re Ground Water Issues Raised at Cintichem Inc Decommissioning Project ML20078N4221995-02-0202 February 1995 Submits Comments Re Cintichem,Inc Decommissioning Proposed Bedrock Criteria ML20078K4791995-02-0101 February 1995 Confirms Discussions Had Yesterday & Morning Re Strontium-90 Analyses of Water Discharged Through 001 Outfall at Cintichem Site ML20059K1891994-01-14014 January 1994 Forwards Insp Repts 50-054/93-03 & 70-0687/93-03 on 931116- 18.No Violations Noted ML20058C9821993-11-22022 November 1993 Provides Results of NRC TLD Direct Radiation Monitoring Around Cintichem Facility for Third Quarter of 1993 ML20057C7521993-09-24024 September 1993 Expresses Appreciation for J Mcgovern Addressing Town Board & Public Re Decommissioning of Cintichem ML20057B7701993-09-14014 September 1993 Forwards FRN Discussing 930726 Final Rule on Decommissioning Recordkeeping & Documentation.W/O Encl ML20056H4001993-09-0101 September 1993 Responds to Re Towns Request for Status Rept on Licensees Decommissioning Project.Advises That Town Board Meeting Will Commence on 930922 & Outline of Planned Presentation Will Be Issued ML20057A5751993-08-31031 August 1993 Forwards Results of TLD Direct Radiation Monitoring at Facility for Second Quarter 1993 ML20056H1131993-08-27027 August 1993 Provides Clarification Re 930715 Exemption Request from Requirements of Revised 10CFR20 ML20056H4061993-05-25025 May 1993 Suggests That Meeting Date Be Set Up for Sept to Hold Discussions on Closing of Cintichem Reactor Facilities ML20128L3931993-02-11011 February 1993 Forwards Potential Effects of Cintichem-Proposed Residual Soil Criteria on Water Quality of Indian Kill Reservoir ML20128F2901993-02-0303 February 1993 Provides Clarification Re Use of Proposed Subsurface Soil Criteria ML20128B8781993-01-28028 January 1993 Confirms Meeting Arrangement W/Cintichem on 930201 in Tuxedo,Ny to Discuss Unrestricted Release Criteria for Soil at Ny Facility ML20127C1521993-01-0707 January 1993 Requests Assistance in Obtaining Info Re Residual Radiation Exposure Criteria for Decontamination & Decommissioning of Licensed Sites.Author Employed by DOE to Provide Assistance ML20127J5791993-01-0404 January 1993 Forwards Listed Proprietary Procedures for Soil from Teledyne,Per .Procedures Withheld 1998-08-19
[Table view] Category:INCOMING CORRESPONDENCE
MONTHYEARML20236S0211998-06-0202 June 1998 Forwards Confirmatory Surveys of Bldgs & Areas of Cintichem Facility Located in Tuxedo,Ny.Radionuclide Concentration in Bedrock Soil Samples & Orise Resrad Calculation,Encl ML20248D6681998-05-27027 May 1998 Requests That Process for Terminating Licenses R-81 & SNM-639 Be Resumed Due to All Radioactive Matl Having Been Removed as Final Condition for Termination Subject Licenses ML20202E1841998-01-28028 January 1998 Forwards Revised Tables Including Sr-90 Analytical Results. Five Individual Samples from Adjacent Locations Consolidated Into One Sample for Sr-90 Analysis ML20199B6091997-10-22022 October 1997 Forwards Characterization Rept for Union Carbide Spoils Area Tuxedo,Ny.Area Meets Criteria for Unrestricted Use ML20217G2501997-10-0808 October 1997 Forwards Response to 970819 RAI Re Survey Repts of Hot Laboratory Support Bldgs & Outdoor Areas Inside & Outside of RCA ML20211C5501997-09-22022 September 1997 Forwards Bedrock Dose Assessment Rept, Which Completes Final Survey Process.W/One Oversize Drawing ML20149G7981997-07-0303 July 1997 Forwards Chapters 15 & 16 of Final Survey Repts for Cintichem Outdoor Areas Outside Former RCA, Which Describes Cintichem'S Approach to Conducting Final Survey for Areas of Property ML20149G9111997-06-27027 June 1997 Forwards Chapters 13 & 14 Final Survey Repts for Cintichem Outdoor Areas Inside of Former Rca. Chapter 14 Presents Results of Survey ML20134K7041996-11-14014 November 1996 Advises That SNM-639 License Expires on 961215,per Amend 7 Issued 950118.Request License Remain Effective Through June 1997,allowing Sufficient Time for Completing Work Outlined ML20134F7611996-09-25025 September 1996 Provides Comments Re Ground Water Issues Raised at Cintichem Inc Decommissioning Project ML20078N4221995-02-0202 February 1995 Submits Comments Re Cintichem,Inc Decommissioning Proposed Bedrock Criteria ML20056H1131993-08-27027 August 1993 Provides Clarification Re 930715 Exemption Request from Requirements of Revised 10CFR20 ML20128L3931993-02-11011 February 1993 Forwards Potential Effects of Cintichem-Proposed Residual Soil Criteria on Water Quality of Indian Kill Reservoir ML20127C1521993-01-0707 January 1993 Requests Assistance in Obtaining Info Re Residual Radiation Exposure Criteria for Decontamination & Decommissioning of Licensed Sites.Author Employed by DOE to Provide Assistance ML20127J5791993-01-0404 January 1993 Forwards Listed Proprietary Procedures for Soil from Teledyne,Per .Procedures Withheld ML20126A6191992-12-15015 December 1992 Forwards Addl Info Requested in in Support of Proposed Residual Soil Contamination Acceptance Criteria Included in Initial Submittal & Recently Modified in Submission ML20115C6591992-10-13013 October 1992 Informs That T Mach License (SOP-10461-1) Should Be Terminated Since Individual No Longer Employed by Vendor ML20092H4071992-02-10010 February 1992 Advises That Licensee Will Carry Out Full Decommissioning Project as Directed in NRC Order to Decommission ML20076N0701991-03-13013 March 1991 Withdraws 910214 Request for Hearing & Petition to Intervene in Proceeding Re Proposed Issuance of NRC Orders Authorizing Cintichem,Inc to Dismantle Reactor Facility & Dispose of Termination of License R-81.W/Certificate of Svc ML20029A5271991-02-19019 February 1991 Submits Addl &/Or Clarifying Info Re Decommissioning Plan, Per 910213 Ltr ML20029B5621991-02-19019 February 1991 Confirms 910214 Telcon Informing of Inability to Utilize Telegram Notification as Specified in 910114 Fr Notice (56FR1422) Because Datagram Identification 3737 Inactive. Telegram Notice Requirement Waived ML20029B6331991-02-14014 February 1991 Forwards Ny State Dept of Environ Conservation Request for Hearing & Petition to Intervene ML20028H8231991-01-21021 January 1991 Forwards Proposed Task Lists for Discussion on 910211 at NRC Headquarters ML20065S0991990-12-10010 December 1990 Identifies Two Tech Spec Required Items Difficult or Impossible to Perform Due to Transitional Period Between Normal Operations & Decommissioning ML20059N5771990-10-0303 October 1990 Advises That Repairs to Canal & Gamma Pit Sections of Reactor Primary Water Sys Completed,Per Order Modifying License.Licensee Decided to Operate at Level of 10 Ft of Water.Radiation Measurements Will Be Conducted ML20055J1721990-07-19019 July 1990 Requests Notification as Soon as Notice of Decommissioning Appears in Fr.Notice Will Enable Town to Go Forward W/ Petition for Public Hearing ML20042G5631990-05-0303 May 1990 Requests That NRC Requested Changes to Licensee Physical Security Plan Ref in NRC 900205 Ltr Be Rescinded Due to Vendor Decision to Decommission Facility ML20042F1031990-03-29029 March 1990 Forwards 900321 Ltr from C Monaco,Cortland County Low Level Radwaste Coordinator Requesting Licenses of All New York State Power Plants & Any Amends Extending Operating Lives of Plants ML20246B9721989-06-0707 June 1989 Provides Status Rept of Listed Open NRC Insp Items,Per EC Wenzinger 890518 Request,Including Inadequate Training or Procedures to Assure Uniform Plant Operations ML20246M9541989-05-0808 May 1989 Responds to NRC Ltr Re Violations Noted in Insps 50-054/89-02 & 70-0687/89-02 on 890328-31.Corrective Actions:Refresher Training Performed Re Contamination Control Aspects of Operation & Handbook Prepared ML20245L3891989-04-28028 April 1989 Responds to NRC Re Violations Noted in Insp Rept 50-054/88-03.Corrective Actions:Policy Manual on Contamination Control Prepared & Will Be Distributed to Employees Routinely Working in Controlled Areas ML20245D3421989-03-20020 March 1989 Forwards Listed Endorsements,Including Endorsements 14,163, 144,94,75,39 & 31 to Nelia Policies NF-295,NF-100,MAELU Policy MF-29,NELIA Policy NF-182,MAELU Policy MF-61,NELIA Policy NF-281 & Maelu Policy MF-112,respectively ML20236D0211989-02-20020 February 1989 Requests Meeting Re Issue W/Potential Impact on All Test,Research & Training Reactor Members.Integrity of Rulemaking Comment Process Questioned ML20235F8421989-02-15015 February 1989 Forwards to NRR Re Proposal to Meet Requirements of 10CFR50.64b for Conversion of Research Reactors from High to Low Enriched U ML20151W1171988-08-12012 August 1988 Responds to NRC Ltr Re Violations Noted in Insp Repts 50-054/88-01 & 70-0687/88-04 on 880713.Corrective Actions: Hot Cell Emergency Ventilation Sys Use Terminated Until Proper Effluent Monitoring Equipment Installed ML20148K1111988-03-22022 March 1988 Forwards Listed Endorsements to Listed Policies,Including Endorsement 102 to Maelu Policy MF-26,Endorsement 123 to Nelia Policy NF-76,Endorsement 71 to Maelu Policy MF-56 & Endorsement 89 to Nelia Policy NF-189 ML20151R3851988-03-14014 March 1988 Elicits NRC Comments on Proposed Procedure by Which Licensee Would Apply for Exemption from Current NRC Requirement to Convert Research Reactors Using High Enriched U Fuel to Low Enriched U Fuel ML20196K1621987-07-0909 July 1987 Partially Deleted Ltr Submitting Addl Info in Response to NRC 861230 & 870211 Requests Re 860918 Application for Exemption from Requirement to Convert from High Enriched U to Low Enriched U for Reactor Fuel,Per Generic Ltr 86-12 ML20238B1301987-07-0909 July 1987 Advises of Recent Organizational Changes & Updates Re Action Taken to Strengthen Radiation Safety Program.Dj Gallaher Replaced Ww Rudley as President on 870415.T Vaughn Replaced C Konnerth as Operations Manager on 870511 ML20235J7041987-07-0909 July 1987 Submits Addl Info in Response to NRC 861230 & 870211 Requests Re 860918 Application for Exemption from Requirement to Convert from High Enriched U to Low Enriched U for Reactor Fuel.Proprietary Response Encl ML20209E3411987-04-27027 April 1987 Supports Exemption from 10CFR50 Requirements Re Conversion from High Enriched to Low Enriched U Fuel for Cintichem,Inc. Cintichem Produces Over 50% of Mo-99 in Us & Is Only Domestic Supplier of Several Vital Radioactive Drugs ML20213G2881987-04-0202 April 1987 Forwards Comments on Reactor Operator & Senior Reactor Operator Exams Administered on 870327 ML20205Q2081987-03-25025 March 1987 Advises That Listed Officers & Directors Mentioned in 841228 Application for Amend to License R-81 Should Be Deleted,Per Director & Shareholder 870120 Resolutions ML20204H2751987-02-0404 February 1987 Responds to Insp Repts 50-054/86-04 & 70-0687/86-05. Procedure Revised So That Each Unlabeled Drum Will Be Labeled at Time Waste First Placed in Container ML20207N0871986-12-31031 December 1986 Forwards Endorsement 6 to Nelia Policy NF-295 ML20214Q4751986-09-18018 September 1986 Requests Exemption from Conversion from Use of Highly Enriched U,Per 10CFR50.64 & Listed Generic Ltr 86-12 Purposes.Justification Provided ML20206T0191986-05-29029 May 1986 Responds to Violation Noted in Insp Rept 70-0687/86-02. Corrective Actions:Technician Counseled Re Posting of Correct Amount of U-235 Stored in Feed Cabinet 4 ML20198D0651986-05-13013 May 1986 Responds to NRC Re Violation Noted in Insp Repts 50-054/86-01 & 70-0687/86-02.Corrective Actions:Procedure Changed to Require That Waste Drums Be tamper-safed Prior to Analysis ML20210L2431986-03-20020 March 1986 Forwards Endorsement 5 to Nelia Policy NF-295 ML20137N7141985-11-22022 November 1985 Responds to Violations Noted in Insp Repts 50-054/85-04 & 70-0687/85-07 on 850819-23.Corrective Actions:Waste Drums Placed in Waste Storage Bldg & Sign Posted by I-125 Loop Glovebox 1998-06-02
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CIN71 CHEM, INC.
P.O. BUX B10 TUXEDO NEW YOFT< 10907 [914]351-2131 October 22,1997 Ms. Barbara Youngberg NYS Dept of Environmental Conservation 50 Wolf Road Albany, NY 12233
Subject:
Characterization Report for Union Carbide Spoils Area in Tuxedo, NY Dcar Ms. Youngberg:
Enclosed plosse find the referenced report. Based on our findings, this area now meets the criteria for unrestricted use.
If you have any comments or questions, please contact me at (914) 351-2236, or Mr. James McGovern at.(914) 3512131.
Very truly yours, oseph J. 2 er Manager, HSEA Enclosure, as stated cc: T. Dragoun, NRC C. Warren E. Abelquist, ORISE L. Feigenbaum R. Aldrich, NYS J. McGovern bggD T. Michaels, NRC J. Adler D. Orlando, NRC L. Glander >
Document Control Desk, NRC )
bec: F.C. Kentz, III t K. Magar 9711190040 971022 11pf PDR ADOCK t)5000054 P PDR
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e Characterization and Dose Assessment:
Union Carbide Spoils Area Page 1 of 10 CINTICIIEM CIIARACTERIZATION AND DOSE ASSESSMENT REPORT:
UNION CARBIDE SPOILS AREA
- 1. INTHODUCTION This report presents the final results of the sampling program that was performed in the vicinity of the " Union Carbide Spoils Area" (UCSA) located on the Cintichem site in Tuxedo, NY, Field sampling activities were conducted during the spring and summer of 1997. The data obtained was then used to assess the potential for exposure, if any, that could result from residual ra(ioactivity (uranium ore residues) that are contained in this area.
The following two sections present the results of the UCSA characterization and dose assessment program. The characterization data indicates that the UCSA met the radiological criteria for unrestricted use in all areas except the "flot Spot" area that had been identified previously. This liot Spot has since been remediated to background levels. No radiation exposures in excess of natural background c e expected to result from the UCSA.
- 2. UCSA CIIARACTERIZATION PROGRAM RESULTS Potentially affected soil within and around the suspect area of the UCSA was characterized by a sampling program conducted during the spring and summer of 1997 The characterization was performed in accordance with and as described by a sampling plan spproved by the New York State Department of Environmental Conservation '.
A total of 25 boreholes were drilled in or around the ncrthem section of the UCSA, Additionally, a background borehole was installed 86 raeters east-southeast of the known UCSA liot Spot. The locations of these boreholes are shown in Figure 1. Three of the borholes placed within the UCSA hit obstructions after a few feet. The other 22 boreholes were drilled completely Grough the expected thickness of the fill layer to the refusal on the original surface's boulder layer, The fill lyer appeared to have a maximum thickness of 12 feet. Five of the UCSA boreholes plus the background borehole were sampled by split-spoon.
This yielded 36 soil samples from the UCSA and one six-foot composite sample from the backgrotmd borehole.
Nineteen composite samples of the soil cuttings were obtained from 19 of the 20 other boreholes that were installed. All 26 boreholes were gamma-logged at one-foot intervals with
, a sodium-iodide scintillation detector, yielding 155 gamma spectra. The soil sampling results from the five boreholes that were split-spoon sampled are presented in Table 1, A through E.
I " Radiological Characterization Plar) for Union Carbide Spoils Area," issued by Cintichem, Inc.,
dated January 22,1997 l
- Characterization and Dose Assessment: Page 2 of 10 Union Carbide Spoils Area The soil sampling results from the 19 boreholes from which composite samples were obtained are presented in Table 2. The soil sample result from the background borehole is presented in Table 3.
The soil concentrations of the principal long-lived radionuclides originally found within the known Hot Spot (i.e., Ra ??6, U 238, U-235, and Th-232) were all found to be within the range of natural background found in the background borehole. The background concentrations (in pCi/gm) were found to be 3.75 for Ra 226,5.13 for U-238, <0.22 for U-235,1.78 for Th-232, and <0.047 for Cs-137 (a fallout background radionuclide). The maximum soil concentrations found within the five split-spoon sampled boreholes were 6.76 for Ra-226,12.15 for U-238,0.15 for U-235,1.7 for Th-232, and 0.88 for Cs-137. The mean concentrations for the 36 soil samples were found to be 3.3 for Ra-226,3.1 for U-238,0.11 for U-235,0.85 for Th-232, and 0.157 for Cs-137. These results are essentially no different than natural background, with the possible exception of the sample from Borehole No. 2 at the 720 to 719 foot elevation from which the maximum results for Ra-226, U-238, and Cs-137 were obtained.
Borchole No. 2 bordered the known llot Spot on its northern side. The excavation and removal of this llot Spot also inicuded the soil layer surrounding this borehole. As such, the resulting maximums would now be 4.54 for Ra-226,5.58 for U-238,0.15 for U-235,1.7 for Th 232, and 0.166 for Cs 137.
The soil concentration results for the 19 boreholes from which composite samples were obtained are also indistinguishable from that of the background borehole. The maximum
! concentrations found were (in pCi/gm) 4.17 for Ra-226,6.18 for U-238, <0.14 for U-235,1.7 for Th-232, and 0.039 for Cs-137. The mean concentrations for this group of samples were l found to be 2.39 for Ra 226,3.51 for U-238, < 0.107 for U-235,1.09 for Th-232, and 0.13 for Cs-137 Q gamma logging results for the 155 one-foot intervals were also found to be indistinguisnable from those obtained in the background borehole.
L This data indicates that there are no deposits of uranium ore residue present in the UCSA other than that of the initial llot Spot that was subsequently removed. Radionuclides of interest have only been found at levels similar to those of natural background. This is additionally supported by the degree of U-238 decay chain equilibrium (i.e., Ra-226 to U-238 ratio) that was found.
As can be seen from Table 4, the soil samples from the UCSA boreholes had mean ta-226 :
U-238 ratios of about 0.73. This is that same ratio found in the background borehole.
Samples of soil from the known Ilot Spot and uranium ore residues from Building No. 3 both had mean Ra-226 : U-238 ratios of about 1.33. This indicates that the radionuclides fo the boreholes do not originat from the uranium ore that was processed on site.
Soil from the known llot Spot was completely excavated and removed. This resulted in a hole 10 to 12 feet in diameter and approximately 4 to 5 feet deep. This excavation was then surveyed and sampled. The bottom and sides of the excavation were scanned with a sodium-
.- c
(
Characterization and Dose Assessment:
Union Carbide Spoils Area Page 3 of 10 iodide scintillation detector and a beta / alpha contamination frisker to locate any potentially elevated areas. None were found. The excavation was then soil sampled and surveyed for gamma exposure rate, with locations shown on Figure 2. _Results are presented in Table 5.
The soil cor.centrations found were consistent with those encountered for the remainder of th:
UCSA and background boreholes with mean concentrations (in pCi/gm) of 3.28 for Ra-226, 3.32 for U 238,0.13 for U-235,0.79 for Th-232, and 0.29 for Cs-137. Gross gamma exposure rates (background inclusive) were found to range from 8 to 13 pRem/hr at one meter above the surface, with a mean of 9.9 pRem/hr.
4
- 3. CONCLUSIONS The UCSA, with the Ilot Spot remediated, has been found to be at natural background levels for uranium ore residues. As such, no radiatio , exposures in excess of natural background are expected. This area meets the criteria for unrestncted use.
I l
l l
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Characterization and Dose Assessment:-
Uulon Carbide Spoils Area Page 4 of 10 4
TABLE 1 UCSA BOREHOLE SOIL SAMPLE DATA Section I-A Ground Level Elevation: 724 ft Borehole No. 2 Grid Coordinate: 395N, 72.5W.
Depth interval Soil Coriceritrets oCVgm
( feet ) Ra-226 U-238 U-235 Th-232 - Cs 137 724 723 1.71 2.04 < 0.10 < 0.25 0.14 723 722 0.83 1.50 < 0.08 0.69 < 0.113 722-721 2.52 4.75 < 0.id 1.03 0.097 721 720 4.07 6.01 < 0. 6 6 < 0.77 0.23 NSR = No sample 720-719 6.76 12.15 < 0.29 <1.12 0.88 recoveed 719-718 NSR NSR NSR NSR NSR 718 717 1.32 <1.46 < 0.08 0.81 < 0.08 R = Refusal on bedrock 717 716 NSR NSR NSR NSR NSR or boulder 716-715 2.56 2.57 < 0.12 1.10 0.021 715 714 NSR NSR NSR NSR NSR 714 713 NSR NSR NSR NSR NSR 713 712 2.32 2.13 < 0.03 1.40 < 0.21 712 R R R R R Moan 2.76 4.08 0.12 0.896 0.244 S.D. 1.89 3.65 0.08 0.348 0.26 Section 1-B Ground Level Elevation: 722 ft Borchole No. 4 Grid Coordinate: 402N, Jaw Depth Interval Soil Concentration. oCUgm
! ( feet ) Ra-226 U-238 U-235 Th-232 Cs-137 722 721 1.71 3.56 < 0.11 1.31 < 0.08 721 720 2.35 3.94 < 0.11 0.79 < 0.08 720-719 2.61 2.84 < 0.11 <0.42 < 0.025 719 718 1.62 <1.69 < 0.04 0.64 < 0.088 NSR = No sample _ 718-717 1.65 2.17 < 0.10 0.89 0.14 recovered 717 716 NSR NSR NSR NSR NSR 716-715 2.0 2.49 < 0.08 0.83 0.10 R = Refusal on bedrock 715-714 NSR NSR NSR NSR NSR or boulder 714-713 NSR NSR NSR NSR NSR 713-712 NSR NSR NSR NSR NSR l 712 711 NSR NSR NSR NSR NSR 711 710 4.54 6.19 < 0.19 < 0.58 < 0.09 l 710 R R R R R i Mean 2.35 3.27 0.11 0.78 0.086 L
S.D. 1.03 1.50 0.045 0.284 0.034
- 4 .
4 - 1 Characterization and Dose Asseasment:
Union Carbide Spoils Ares -
e, Page 5 of 10 TABLE 1 Continued
. Section 1-C Ground Level Elevation: 723 ft llorehole No. 6 Grid Coordinate: 400N, 87W Depth Interval Soil Corswi;rtucci. pCilgm
( feet ) Ra-226 U-238 U 235 Th 232 Cs 137 723-722 2.10- 2.88 < 0.11 1.35 < 0.078 722-721 1.65' 1.54 < 0.08 0.81 0.18 721 720 2.70 4.19 < 0.11 0 83 < 0.10 720 719 <1.22 <1.89 < 0.11 1.08 0.19 -
719 718 2.75 5.58 < 0.14 1.11 < 0.14
- R = Refusal on bedrock 718-717 1.2 1.78 < 0.08 0.54 0.17 or boutier 717 716 ' 2.22 3.06 < 0.11 < 0.29 < 0.09 116 R R R R R Mean 1.98 2.99 0.11 0.86 0.135 S.D. 0.643 1.47 0.02 0.36 0.046 Section 1.D Gidund Level Elevation: 724 ft llorehole No. 8 Grid Coordinate: 394N,85W Depth Interval Soil Concentration. DCl/9m
( feet ) Ra-226 U-238 U 235 Th-232 Cs-137 l 724 723 0.89 1.13 <0.07 < 0.17 0.135 723 722 1.01 2.01 < 0.07 - 0.96 < 0.063 722 721 2.10 5.02 < 0.12 1.06 0.17 721 720 0.96 1.43 < 0.04 0.73 < 0.076 720 719 0.93 1 43 < 0.08 0.57 0.087 719-718 1.33 2.27 < 029 0.89 < 0065
!' R = Refusal on bedrock 718-717 1.05 1.83 < 0.07 < 0.28 < 0.033 or bovider 717 716 1.48 2.19 < 0.07 0.68 < 0.08 l
716-715 1,98 2.39 < 0 *.1 0.91 < 0.07 715 714 1.35 1.68 < 0.09 0.67 0 01 714 R R R R R Mean 1.31 2.14 0.08 0.692 0.08 S.D. 0.435 1.09 0.023 0.29 0.046
Characterization and Dose Assessment:
Union Carbide Spoils Area - Page 6 of 10 TABLE 1 Continued Section 1-E Ground Level Elevation: 726 ft Borehole No.15 Grid Coordinate: 387.5N, 92.5W
' Depth Interval Soil Concentrabon. DCilam
( feet ) Ra-226 U-238 U 235 - Th-232 Cs-137 726-725 3.03 2.91 - < 0.11 1.07 0.48 725-724 2.22 3.25 < 0.12 < 0.05 0.66 R = Refusal on bedrock 724-723 3.91 2.58 < 0.16 1.70 0.095 or boulder 72377' 4.16 4.95 0.15 1.59 0.134 72l R R R R R Mean 3.33 3.42 0.135 1.22 0.34 S D. 0.885 1.05 0.024 0.55 0.27
+.
- Characterization and Dose Assessment:
Union Carbide Spoils Area Page 7 of 10 TABLE 2 UCSA BOREHOLE COMPOSITE SOIL SAMPLE RESULTS Borehole Grid Ground Bottom DCilgm ID No. Location Elevation (ft) Elevation (ft) Ra-226 U-238 U-235 Th-232 Cs 137 1 394N, 75W 724. 712 1.57 <1.76 < 0.086 1.58 < 0.04 3 398N, 76W 721 714 3.27 4.91 < 0.14 1.7 0.27 5 (no sample recovered) 7 397.5N, 90W 724 712 2.08 3.34 < 0.13 0.76 < 0.14 9 392.5N, 88W 724 716 2.64 5.48 < 0.11 1.3 < 0.06 10 395N, 83W 725 721 2.11 3.64 < 0.11 < 0.33 < 0.078 11 396N, 78W 724 715 3.52 6.18 < 0.13 0.58 0.19 12 392N, 78W 724 716 2.33 1.71 < 0.09 1.26 < 0. 05 13 392N, 82W 724 717 1.80 2.84 < 0.12 1.35 0.17 14 392.5N, 92.5W 726 720 2.19 5.38 < 0.12 1.42 0.18 16 385N, 93Y' 726 720 1.73 3.02 < 0.08 1.45 < 0.08 17 384N, 89W 724 718 2.70 5.00 < 0.12 1.35 < 0.065 18 396.5N, 89W 724 721 1.20 1.68 < 0.065 0.53 0.39 19 385N, 86W 725. 723 2.41 2.75 < 0.10 1.14 0.15 20 - 391N, 89W 725 724 3.50 4.56 < 0.11 1.36 < 0.065 21- 395N, 88W 725 718 NSR NSR NSR NSR NSR 22 385N, 75W 727 718 1.42 2.09 < 0.06 1.38 0.11 23 366N,134W 736 731 2.66 2.88 < 0.12 < 0.42 0.26 24 380N,126W 735 729 1.76 2.35 < 0.097 < 0.14 < 0.079 '
25 368N.116W 734 727 4.17 3.55 < 0.12 1.61 < 0.024
-Mean 2.39 3.51 0.107 1.09 0.13 S.D. 0.808 1.42 0.02 0.49 0.097 TABLE 3 UCSA HACKGROUND HORElIOLE DATA
- Soil Concentration " (pCi/gm)
Ra-226 U-238 U-235 Th-232 Cs-137 3.75 5.13 < 0.22 1.78- < 0.047
- Located approximately 282 feet (800 meters) east-southeast of the USCA ' Hot Spot *, at grid coordinato 342N,10W
" This borehole was sampled from ground level (730 ft) to a depth of 6 feet. The data represents a composite of the O to 6 foot borehole interval.
- Chbract:rization c:d Dose Assessm::t:
Union Carbide Spoils Area Page 8 of 10 TABLE 4 COMPARISON OF URANIUM 238 DECAY CIIAIN EQUILIBRIUMS FROM VARIOUS SOURCES Ra-226 to U-238 No. of Standard Sample Group Samples Range Mean Deviation Background Borehole 1 n/a 0.73 n/a Boreholes: 2, 4, 6, 8 & 15 (split spoon sewed) 36 0.41 1.52 0.738 0.224 Boreholes: 1, 3, 7, 9,10 14,16 25 (single composite sample) ill 0.41 1.36 0.73 0.24 Pre-R mediation Hot Spot Area 3 1.24 1.47 1.33 0.12 Post-Remediation Hot Spot Area (Excavated) 9 0.60 - 1.31 0.973 0.255 Bldg 3 Exhaust Ventillation Debris 3 1.067 1.84 1.34 0.43 TABLE 5 UCSA SOIL SAMPLE AND DutECT EXPOSURE RATE DATA FOLLOWING REMEDIATION OF IIOT SPOT
- Sample Gross Gamma Exposure Rate Soil Concentration, pCi/gm Location at 1 Meter ( Rem /hr) Ra 226 U-238 U-235 Th 232 Cs-137 l 1 8 1.76 1.78 < 0.09 0.94 < 0.06 2 8 1.65 2.28 < 0.104 1.09 < 0.08 3 10 1.09 0.86 < 0.06 < 0.21 0.091 4 9 9.74 7.44 < 0.23 < 0.25 0.37 5 10 3.2 3.16 < 0.14 1.46 0.37 6 13 1.86 2.26 < 0.12 < 0 29 0.34 7 10 2.3 3 84 < 0,12 1.74 0.15 8 10 3.66 3 01 < 0.14 < 0.55 0.62 9 11 4.22 5.24 - < 0.19 < 0.61 0.55 Mean 9.9 3 28 3.32 0.13 0.79 0.29 S.D, 1.54 2.63 1.99 0.05 0.55 0.21 This excavation removed the initial uranium ore contamination that was discovered in the UCSA. This is a 10 12 foot diameter excavation centered on or about grid
- coordinate 391N,72W
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