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� _ <br />'YABLE 1'- CHECKLIST OF REQUIRED DATA U <br />FOR. i NO FURTHER ACTION REQUESTS AT UNDERGROUND TANK SITES <br />Site Name and Location: <br />Earthgrains Baking Companies, Inc., 2651 S. Airport Way, Stockton, San Joaquin County <br />(RB #390065) _ <br />Y <br />1. Distance to production wells for municipal, domestic, - <br />A 2008 sensitive receptor survey reported two domestic <br />agriculture, industry and other uses within 2000 feet of the site. <br />wells (200'south and 600, south) and one irrigation well <br />(370'south) within 2,000' of the site. The wells are not <br />Y <br />2. Site maps, to scale, of area impacted showing locations of <br />threatened by the USTs release. <br />In 4-87, two 6,000 -gallon gasoline USTs were removed. In <br />any fanner and existing tank systems, excavation contours and <br />9-89, two 12,000 -gallon diesel USTs and associated <br />sample locations, boring and monitoring well elevation <br />piping and dispensers were removed. In 2-96, one 1,000. <br />contours, gradients, and nearby surface waters, buildings, <br />gallon diesel UST was removed. <br />streets, and subsurface utilities, <br />Y <br />3. Figures depicting lithology (cross section), treatment system <br />Site lithology consists of clay, silt, sand, and gravel to <br />diagrams; - <br />104', the total depth investigated. <br />Y <br />4. Stockpiled soil remaining on-site or off-site disposal (quantity); <br />The location of the 450 y excavated soil disposed <br />offsite was not discussed in the available reports. <br />Y <br />5. Monitoring wells remaining on-site, fate; <br />Thirteen (13) monitoring wells (MW -1 through MW -13) two piezometers (PZ -1 <br />and PZ -2) and eight remediation wells (SP -1 through SP -6, SP -A, and VW -1) <br />:will be properly destroyed. <br />6. Tabulated results of all groundwater, <br />Depth to groundwater varied from 36' bgs to 56' bgs. Groundwater flow <br />elevations and depths to water, <br />direction was predominantly towards the east. Groundwater gradient <br />varied from 0.001 Wft to 0.003 ft/ft. <br />7. Tabulated results of all sampling <br />All data adequately tabularized in various reports, including closure report. <br />and analyses: <br />Y❑ Detection limits for confirmation <br />sampling <br />QN Lead analyses <br />_ <br />onc <br />B,Centration�contours of contaminants found and those remaining in soil and <br />The extent of the identified <br />groundwater, and both <br />--contaminationa esscritie—U-0 e- - <br />Y] Lateral and l Vertical extent of soil contamination <br />available reports. <br />FT Lateral and Vertical extent of groundwater contamination. <br />9. Zone of influence calculated and assumptions used for subsurface remediation <br />SVE/AS was the engineered remediation. <br />system and the zone of capture attained for the soil and groundwater remediation <br />system; <br />10. Reports/ information FY -1 Unauthorised Release Form FE QMRs (56) 8-93 to 4-10 <br />❑Y Well and boring logs. PAR FRP FY Other. Closure Reports (11-09 8 6-11)) <br />Y <br />11. Best Available Technology (BAT) used or an explanation for not using <br />USTs removal, over -excavation, SVE(AS and <br />I <br />BAT; <br />natural attenuation. <br />I, <br />12. Reasons why background washs unattainable <br />Residual soil and groundwater contamination remains on-site. <br />BAT,' <br />Y <br />13. Mass balance calculation of substance treated <br />Consultant estimated residual soil mass as 8,580 lbs of TPHg; and <br />versus that remaining; _ <br />1096 lbs TPHg remained in groundwater. <br />7Y <br />14. Assumptions, parameters, calculations and <br />Soil concentrations did exceed Region 2 Environmental Screening <br />model used in risk assessments, and fate and <br />Levels (ESLs) for commercial use at depths of 15' bgs or more, below <br />transport modeling; - <br />typical direct contact depth. A soil vapor survey was not required. <br />` <br />Fate and transport modeling shows no impacts to nearby sensitive <br />- <br />receptors. Consultant states site does not re resent a significant risk. <br />Y <br />15. Rationale why conditions remaining at site. will <br />Soil and groundwater contamination reportedly are limited in extent. <br />not adversely impact water quality, health, or other <br />Land use (commercial) is not expected to change in the foreseeable <br />beneficial uses; and <br />future. TPH is estimated to reach WQGs in 2043. <br />By: <br />JLB <br />Comments In 4-87, two 6,000 -gallon gasoline USTs were removed; in 9-89, two 12,000 -gallon diesel USTs and <br />associated piping and dispensers were removed; in 2-96;.one 1,000 -gallon diesel UST was removed.at the <br />Date: <br />-subject site.: Minor residual soil and groundwater contamination remains on-site. Based upon the limited <br />12/19nj/2011 <br />extent of contamination reported in soil and groundwater, a stable groundwater plume with declining <br />concentrations, no foreseeable changes in future land use (commercial), and minimal risks from soil, soil <br />va or and aroundwater, Regional Board staff concur with San Joa uin CountClosure Recommendation. <br />