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call. Participants for the future TPP3 meeting will include the addition of other local stakeholders to be <br />determined once the SI reporting phase has begun. <br />Stockton AASF PA Findings (Slides 9-14): <br />The PA findings for the Stockton AASF were presented. Information reported in the PA was collected <br />through in-person interviews and a visual site inspection. <br />Three areas of interest (AOIs) were identified where annual fire training with aqueous film forming foam <br />(AFFF) was conducted as early as 1992 and less frequently since 2010: <br />o AOI 1- Airfield Fire Training Area (FTA). Tri -Max TM fire extinguishers discharged and stationed at <br />airfield. <br />o AOI 2- Wash Rack FTA. Tri-MaxTM fire extinguishers used in live fire training and re -filled at wash <br />rack. <br />o AOI 3- Butler Building Parking Area FTA. Tri-MaxTM fire extinguishers used in live fire training. <br />Underlying soil has been disturbed in area due to Butler Building construction. <br />Potential adjacent sources were discussed including the Montezuma Fire Station, French Camp Fire <br />Station, Stockton Metropolitan Airport, and Aramark Uniform and Career Apparel. <br />Mr. Marcus Pierce (CA Water Board) pointed out a former wash rack located between the current wash <br />rack and airfield and near a former petroleum site. The former wash rack may be a potential PFAS <br />release area needing further investigation. Recent investigations at Stockton AASF are captured in the <br />CA Water Board's GeoTracker site. <br />Brian Pierskalla, CAARNG, noted a case associated with a petroleum -release at the AASF has been <br />closed and associated monitoring wells abandoned. However monitoring wells associated with the <br />CAARNG's Field Maintenance Shop (FMS) #24 (adjacent to the west of the AASF) are potentially <br />available to be gauged during the SI for the purpose of assessing groundwater gradient. <br />Stockton AASF SI Overview (Slides 15-18): <br />• Data quality objectives (DQOs) were presented for the SI. The primary DQOs were to confirm the <br />presence or absence of a PFAS release at a potential source area and to gather data to refine the <br />conceptual site model (CSM). Secondary goals are to determine the presence/absence at the ARNG <br />facility boundary. <br />• The preliminary CSM presented the surrounding surface water flow direction. A ditch (labeled Rydberg <br />Creek) is located along the southern and western boundary of facility and flows northwest before <br />connecting to the French Camp Slough. The oil water separator at the wash rack is connected to the <br />City of Stockton's sanitary sewer. <br />• The preliminary CSM presented an inferred groundwater flow direction to the north/northeast which is <br />generally consistent with groundwater gradients measured at Stockton AASF during previous <br />investigations. Based on available data, groundwater is expected to be encountered at depths of 25 to <br />30 feet below ground surface. <br />• The current understanding of the CSM is that there are potentially complete pathways between the <br />potential source areas and human receptors (mainly site and construction workers) via inhalation of <br />dust, ingestion of surface soil, ingestion of surface water/sediment, and ingestion of subsurface soil. A <br />potentially complete pathway also exists for construction workers and off -facility residents via ingestion <br />of shallow groundwater (for groundwater shallower than 15 feet). Additionally, potentially complete <br />pathways exist for recreational users and trespassers via inhalation of dust, ingestion of surface soil, <br />and ingestion of surface water/sediment. <br />Stockton AASF SI Approach (Slides 19-23): <br />• The scope of work for the SI was presented. Soil borings will be installed at locations within release <br />areas as well as downgradient of the potential source areas at the facility boundary. Ten DPT borings <br />are proposed and will be converted to temporary monitoring wells. Groundwater samples will be <br />collected from each temporary well. Soil samples are proposed at the ground surface, mid -point, and <br />above the water table at each boring location. Six hand auger surface soil samples are also proposed <br />adjacent to the release areas. <br />• As presented below, surveying the temporary monitoring wells was discussed. <br />ARNG PA/SI, Stockton AASF CA 2 24 February 2021 <br />