Conceptual Site Model - Argonne National Laboratory
Conceptual Site Model - Argonne National Laboratory Conceptual Site Model - Argonne National Laboratory
WVDP Phase 1 CSAPsamples. 10 pCi/L and 500 pCi/L were selected as thresholds for Sr-90 and tritium,respectively, because based on ELIMS data results above these activity concentrationswere consistently above method detection limits and so indicative of contaminationimpacts rather than simply measurement error. Contamination was encountered at bothlocations. It is not clear if this contamination represented releases from WMA 3activities, or originated from releases associated with the main processing facility’sactivities.C.6 Planned Phase 1 DP ActivitiesFor a more complete description of planned Phase 1 DP activities, see the Phase 1 DP, Section3.1 and Section 7.5.The waste tank mobilization and transfer pumps, the Con-Ed Building, the Equipment Shelter andcondensers, and the piping and equipment in the HLW transfer trench are slated for removal aspart of Phase 1.Phase 1 does not include the four underground waste tanks, the Permanent Ventilation SystemBuilding, the Supernatant Treatment System Support Building, the high level waste transfertrench itself, or the underground infrastructure.Some Phase 1 activities planned for WMA 1 affect WMA 3. These include a temporary sheetpiling wall that will run along a portion of the WMA 1 and WMA 3 boundary, and a permanentslurry wall that will extend into WMA 3 (Figure C.15). Depending on the outcome of CSAP datacollection work, the planned excavation in WMA 1 may be revised in a way that extends intoWMA 3.C.7 Conceptual Site ModelBased on the limited available information, the conceptual site model (CSM) for WMA 3 is asfollows. A number of potential releases within the WMA 3 footprint are known to have occurred,or may have occurred that likely impacted surface and subsurface soils and groundwater. Inaddition, environmental media within WMA 3 have likely been affected to some degree byreleases elsewhere at the WVDP site. These include air deposition contamination on surface soilsRev. 1 C-10
WVDP Phase 1 CSAPand subsurface contamination resulting from contaminant migration via groundwater from theProcess Building.After initiation of the WVDP, the surface of WMA 3 underwent significant reworking. Thisreworking may have covered contaminated soils with clean cover, removed contaminated surfacesoils for disposition elsewhere, and/or re-used contaminated soils as backfill for buildingfoundations or buried infrastructure.Groundwater flow underneath WMA 3 is expected to be, in general, towards the northeast.Consequently one would expect a greater likelihood for groundwater contamination as one movesfrom west to east (assuming releases within the WMA 3 footprint) and from south to north(assuming impacts from contaminated groundwater originating with Process Building activities).Figure C.16 shows the current CSM for surface soils. Figure C.17 shows the CSM for soilsdeeper than 1 m. Figure C.18 shows the CSM for contaminated groundwater beneath WMA 3.C.8 WMA 3-Specific Characterization Goals• Develop an inventory of buried infrastructure• Evaluate appropriateness of the current list of Radionuclides of Interest (ROI)• Verify absence of additional ROI• Determine level and extent of surface contamination• Identify the presence/absence of subsurface soil contamination• Identify soil waste stream characteristics• Define required extent of WMA 1 excavation• Obtain data to support Phase 2 planningC.9 CSAP Pre-Remediation Data Collection and Associated Decision-MakingCSAP pre-remediation data collection will consist of a number of components described in moredetail below.Rev. 1 C-11
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WVDP Phase 1 CSAPsamples. 10 pCi/L and 500 pCi/L were selected as thresholds for Sr-90 and tritium,respectively, because based on ELIMS data results above these activity concentrationswere consistently above method detection limits and so indicative of contaminationimpacts rather than simply measurement error. Contamination was encountered at bothlocations. It is not clear if this contamination represented releases from WMA 3activities, or originated from releases associated with the main processing facility’sactivities.C.6 Planned Phase 1 DP ActivitiesFor a more complete description of planned Phase 1 DP activities, see the Phase 1 DP, Section3.1 and Section 7.5.The waste tank mobilization and transfer pumps, the Con-Ed Building, the Equipment Shelter andcondensers, and the piping and equipment in the HLW transfer trench are slated for removal aspart of Phase 1.Phase 1 does not include the four underground waste tanks, the Permanent Ventilation SystemBuilding, the Supernatant Treatment System Support Building, the high level waste transfertrench itself, or the underground infrastructure.Some Phase 1 activities planned for WMA 1 affect WMA 3. These include a temporary sheetpiling wall that will run along a portion of the WMA 1 and WMA 3 boundary, and a permanentslurry wall that will extend into WMA 3 (Figure C.15). Depending on the outcome of CSAP datacollection work, the planned excavation in WMA 1 may be revised in a way that extends intoWMA 3.C.7 <strong>Conceptual</strong> <strong>Site</strong> <strong>Model</strong>Based on the limited available information, the conceptual site model (CSM) for WMA 3 is asfollows. A number of potential releases within the WMA 3 footprint are known to have occurred,or may have occurred that likely impacted surface and subsurface soils and groundwater. Inaddition, environmental media within WMA 3 have likely been affected to some degree byreleases elsewhere at the WVDP site. These include air deposition contamination on surface soilsRev. 1 C-10