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COMPLIANCE INFO_PRE 2019
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COMPLIANCE INFO_PRE 2019
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Last modified
4/10/2019 11:54:44 AM
Creation date
11/6/2018 8:36:36 PM
Metadata
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Template:
EHD - Public
ProgramCode
2200 - Hazardous Waste Program
File Section
COMPLIANCE INFO
FileName_PostFix
PRE 2019
RECORD_ID
PR0514403
PE
2220
FACILITY_ID
FA0010747
FACILITY_NAME
South Bay Auto Auction
STREET_NUMBER
4101
Direction
S
STREET_NAME
AIRPORT
STREET_TYPE
Way
City
Stockton
Zip
95206
CURRENT_STATUS
02
SITE_LOCATION
4101 S Airport Way
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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FRuiz
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\MIGRATIONS3\222IAError\IAError\A\AIRPORT\4101\PR0514403\COMPLIANCE INFO 1995 - 2012.PDF
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EHD - Public
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H — I SOIL AND GROUNDWATER SAMPLING <br /> Former Parts Depot, Stockton, CA <br /> October 2009; Page 2 of 3 <br /> The borings contained unconsolidated deposits that consisted of clay and silt. Boring logs <br /> are shown in Attachment B. Soil samples were collected from each boring at an approximate <br /> depth of 6 feet,just below the estimated bottom of the septic field. The samples were <br /> analyzed for volatile organic compounds(VOCs)and semivolatile organic compounds <br /> (SVOCs). No compounds were detected. Laboratory reports are summarized in Table 1. The <br /> reports are presented in Attachment C. <br /> WESTERN PROPERTY BOUNDARY <br /> Three borings were drilled near the western property boundary,based on observations made <br /> during the Phase I ESA.The borings were drilled in areas with distressed/dead vegetation and <br /> stained soil.The adjacent property west of the John Deere property is currently occupied by a <br /> company(Siena Chemical)that is believed to manufacture chemicals for the swimming pool <br /> and cleaning industries.The borings were drilled within a few feet of a fence separating the <br /> properties. Boring locations are depicted on Figure 1. Soil samples were collected from the <br /> surface and at an approximate depth of 3 feet Boring logs are shown in Attachment B. The <br /> samples were analyzed for volatile organic compounds VOCs, SVOCs, Resource <br /> Conservation and Recovery Act(RCRA) metals,and indicator parameters including <br /> alkalinity, chloride,nitrogen, sulfate, and pH (Table 1). Laboratory reports are provided in <br /> Attachment C. <br /> The borings contained unconsolidated deposits that consisted of clay. Chloroform exceeded <br /> the U.S. EPA RSL for the protection of groundwater. Acetone was detected in three samples <br /> at levels that did not exceed the RSLs. It is likely that both compounds are the result of spills <br /> from the neighboring property. Based on observations made during the Phase I assessment, <br /> sodium hypochlorite solution(chlorine bleach)was stored by Sierra Chemical Co. in totes <br /> along the property boundary. When sodium hypochlorite is mixed with common industrial <br /> solvents such as acetone,it can produce chloroform. This may be the case at this site,as <br /> acetone and chloroform were the only VOCs detected along the western property boundary. <br /> SVOCs were not detected in any of the six soil samples from the western property boundary. <br /> Arsenic was detected at levels from 5.6 mg/kg to 13 mg/kg,while U.S. EPA's lowest RSL <br /> for arsenic is 0.0013 mg/kg. Barium was detected from 230 mg/kg to 450 mg/kg,versus the <br /> lowest RSL of 82 mg/kg. Therefore,both arsenic and barium exceeded the U.S. EPA RSLs. <br /> Lead and chromium were also detected,but did not exceed their respective RSLs. <br /> It is not clear whether the metal concentrations are naturally occurring or the result of <br /> anthropogenic sources. <br /> Sulfate was identified at concentrations ranging from 39 to 180 mg/kg,but there is no RSL <br /> for sulfate in soil.Nitrate(as N)ranged from 8 to 43 mg/kg. U.S. EPA does not have an <br /> RSL for the leaching-to-groundwater scenario, but the state of California enforces a <br /> provisional standard of 100 mg/kg nitrate. Chloride ranged from 55 mg/kg to 1300 mg/kg, <br /> with the highest concentrations being observed in soil samples collected near where tank <br /> cars containing chlorine were stored on sidings. (Photo 4). <br />
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