Conceptual Site Model - Argonne National Laboratory
Conceptual Site Model - Argonne National Laboratory Conceptual Site Model - Argonne National Laboratory
WVDP Phase 1 CSAPcontaminating subsurface soils between the boundary of WMA 2 and Erdman Brook along thefootprints of Lagoons 2 and 3.The data collection plans for WMA 12 South as described below, do not explicitly address thepossibility of subsurface soil contamination that is overlain by clean soils. The only areas wherethis is believed to be a plausible possibility are along the boundary with WMA 2, resulting fromactivities within WMA 2. Soil sampling to depth will also be taking place in WMA 2 along theboundary with WMA 12 South to address this possibility. If subsurface soil contamination thatextends into WMA 12 South is encountered as part of that effort, sampling will continue intoWMA 12 South until it is spatially bounded.Because both Erdman Brook and Franks Creek are primarily eroding features in this area of thesite, one would not expect to see sediment contamination extending more than one meter into thesubsurface. One would expect to find “bathtub ring” contamination along banks deposited byhigh flows that mobilize and transport contaminated soils and sediments.The limited historical groundwater data available for WMA 12 South show low level tritium andSr-90 impacts, predominately along the border with WMA 2, and to a lesser degree along theborder with WMA 7. Groundwater flow from the boundaries is likely inwards towards the centerof WMA 12 South, with discharges likely occurring to Erdman Brook and Franks Creek.There are no surface soil historical samples within WMA 12 South that exceed surface soil CG wrequirements. However, two surface soil samples (SS-08 and SS-04) come close, and may haveexceeded a Sum of Ratios (SOR) of unity if all 18 ROI had been analyzed. In addition, some ofthe most elevated areas identified by direct exposure readings were not sampled. Based on theexisting data, Figure J.12 indicates where contamination is expected to possibly exist above Phase1 CG w standards in soils, where measurable impacts are not likely to be above CG w standards,and where contamination is very unlikely to be above CG w standards.There is historical evidence of sediments exceeding sediment CG w requirements. Figure J.13shows the portions of Erdman Brook and Franks Creek where sediment CG requirements applyand the likelihood that contamination might be present above sediment CG w requirements. Basedon the very limited data available, Cs-137 appears to be the primary concern in WMA 12 Southsoils and sediments, followed by Sr-90.Rev. 1 J-8
WVDP Phase 1 CSAPJ.8 WMA 12 South-Specific Characterization Goals• Evaluate appropriateness of the current list of ROI• Verify absence of additional ROI• Determine extent of surface contamination• Determine level and extent of sediment contamination• Identify soil waste stream characteristics• Obtain data to support Phase 2 planning• Determine contamination status of various gullies and seeps that feed Erdman Brook andFranks Creek.J.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.J.9.1Gamma Walkover Survey DataThe purpose of performing a gamma walkover survey of the WMA 12 area is to identify the leveland extent of surface contamination. This includes both general trends in average activityconcentrations pertinent to the CG w requirement, as well as the identification of isolated, moreelevatedanomalies that might be indicative of discrete releases and/or CG emc concerns.A complete (100%) logged gamma walkover survey (GWS) will be conducted for accessibleareas within WMA 12 South including exposed soils/sediments associated with Erdman Brookand Franks Creek. Examples of areas that would not be accessible are areas where standing wateris present in wetlands or ponds. Based on the GWS results, surface soil and sediment areas withinWMA 12 South will be divided into four categories: (1) surface soils where GWS data indicatecontamination above CG w requirements; (2) surface soils where GWS data indicatecontamination, but it is not clear if contamination exceeds surface soil CG w requirement; (3)surface soils where GWS indicate impacts, but those impacts are not expected to exceed surfacesoil CG w standards; and (4) surface soils where there is no indication of impacts abovebackground conditions. The purpose of this data collection is to provide insights into the spatialRev. 1 J-9
- Page 424 and 425: WVDP Phase 1 CSAPFigure H.7 WMA 9 A
- Page 426 and 427: WVDP Phase 1 CSAPFigure H.9 WMA 9 A
- Page 428 and 429: WVDP Phase 1 CSAPFigure H.11 WMA 9
- Page 430 and 431: WVDP Phase 1 CSAPFigure H.13 Histor
- Page 432 and 433: WVDP Phase 1 CSAPFigure H.15 WMA 9
- Page 434 and 435: WVDP Phase 1 CSAPA steel security f
- Page 436 and 437: WVDP Phase 1 CSAPFigure I.4 shows W
- Page 438 and 439: WVDP Phase 1 CSAPshine from facilit
- Page 440 and 441: WVDP Phase 1 CSAPI.7 Conceptual Sit
- Page 442 and 443: WVDP Phase 1 CSAPA complete (100%)
- Page 444 and 445: WVDP Phase 1 CSAPgross activity lev
- Page 446 and 447: WVDP Phase 1 CSAP• If a sample in
- Page 448 and 449: WVDP Phase 1 CSAPI.9.8Required Labo
- Page 450 and 451: WVDP Phase 1 CSAPTable I.1 Historic
- Page 452 and 453: WVDP Phase 1 CSAPContractor Fab Sho
- Page 454 and 455: WVDP Phase 1 CSAPFigure I.3 WMA 10
- Page 456 and 457: WVDP Phase 1 CSAPFigure I.5 WMA 10
- Page 458 and 459: WVDP Phase 1 CSAPFigure I.7 WMA 10
- Page 460 and 461: WVDP Phase 1 CSAPFigure I.9 WMA 10
- Page 462 and 463: WVDP Phase 1 CSAPFigure I.11 WMA 10
- Page 464 and 465: WVDP Phase 1 CSAPFigure I.13 WMA 10
- Page 466 and 467: WVDP Phase 1 CSAPFigure I.15 Initia
- Page 468 and 469: WVDP Phase 1 CSAPBrook northwest of
- Page 470 and 471: WVDP Phase 1 CSAP• Lagoon 3 (in W
- Page 472 and 473: WVDP Phase 1 CSAPThe limited Cs-137
- Page 476 and 477: WVDP Phase 1 CSAPdistribution of su
- Page 478 and 479: WVDP Phase 1 CSAPoIf GWS results in
- Page 480 and 481: WVDP Phase 1 CSAPon historical info
- Page 482 and 483: WVDP Phase 1 CSAPA select portion o
- Page 484 and 485: WVDP Phase 1 CSAPTable J.1 Historic
- Page 486 and 487: WVDP Phase 1 CSAPFigure J.1 WMA 12
- Page 488 and 489: WVDP Phase 1 CSAPFigure J.3 WMA 12
- Page 490 and 491: WVDP Phase 1 CSAPFigure J.5 1982 WM
- Page 492 and 493: WVDP Phase 1 CSAPWMA 12 NorthWMA 12
- Page 494 and 495: WVDP Phase 1 CSAPFigure J.9 WMA 12
- Page 496 and 497: WVDP Phase 1 CSAPFigure J.11 WMA 12
- Page 498 and 499: WVDP Phase 1 CSAPFigure J.13 WMA 12
- Page 500 and 501: WVDP Phase 1 CSAPlater in this sect
- Page 502 and 503: WVDP Phase 1 CSAP• Direct measure
- Page 504 and 505: WVDP Phase 1 CSAPK.9.2 Surface Soil
- Page 506 and 507: WVDP Phase 1 CSAPpurpose is to reso
- Page 508 and 509: WVDP Phase 1 CSAP• If a portion o
- Page 510 and 511: WVDP Phase 1 CSAPFigure K.1 WMA 12
- Page 512 and 513: WVDP Phase 1 CSAPFigure K.3 WMA 12
- Page 514 and 515: WVDP Phase 1 CSAPFigure K.5 WMA 12
- Page 516 and 517: WVDP Phase 1 CSAPFigure K.7 WMA 12
- Page 518 and 519: WVDP Phase 1 CSAPFigure K.9 Initial
WVDP Phase 1 CSAPcontaminating subsurface soils between the boundary of WMA 2 and Erdman Brook along thefootprints of Lagoons 2 and 3.The data collection plans for WMA 12 South as described below, do not explicitly address thepossibility of subsurface soil contamination that is overlain by clean soils. The only areas wherethis is believed to be a plausible possibility are along the boundary with WMA 2, resulting fromactivities within WMA 2. Soil sampling to depth will also be taking place in WMA 2 along theboundary with WMA 12 South to address this possibility. If subsurface soil contamination thatextends into WMA 12 South is encountered as part of that effort, sampling will continue intoWMA 12 South until it is spatially bounded.Because both Erdman Brook and Franks Creek are primarily eroding features in this area of thesite, one would not expect to see sediment contamination extending more than one meter into thesubsurface. One would expect to find “bathtub ring” contamination along banks deposited byhigh flows that mobilize and transport contaminated soils and sediments.The limited historical groundwater data available for WMA 12 South show low level tritium andSr-90 impacts, predominately along the border with WMA 2, and to a lesser degree along theborder with WMA 7. Groundwater flow from the boundaries is likely inwards towards the centerof WMA 12 South, with discharges likely occurring to Erdman Brook and Franks Creek.There are no surface soil historical samples within WMA 12 South that exceed surface soil CG wrequirements. However, two surface soil samples (SS-08 and SS-04) come close, and may haveexceeded a Sum of Ratios (SOR) of unity if all 18 ROI had been analyzed. In addition, some ofthe most elevated areas identified by direct exposure readings were not sampled. Based on theexisting data, Figure J.12 indicates where contamination is expected to possibly exist above Phase1 CG w standards in soils, where measurable impacts are not likely to be above CG w standards,and where contamination is very unlikely to be above CG w standards.There is historical evidence of sediments exceeding sediment CG w requirements. Figure J.13shows the portions of Erdman Brook and Franks Creek where sediment CG requirements applyand the likelihood that contamination might be present above sediment CG w requirements. Basedon the very limited data available, Cs-137 appears to be the primary concern in WMA 12 Southsoils and sediments, followed by Sr-90.Rev. 1 J-8