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ARCHIVED REPORTS_XR0005274
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PR0545536
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ARCHIVED REPORTS_XR0005274
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Last modified
3/12/2020 3:37:04 PM
Creation date
3/12/2020 1:53:58 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005274
RECORD_ID
PR0545536
PE
3528
FACILITY_ID
FA0001506
FACILITY_NAME
STOCKTON POLICE DEPARTMENT
STREET_NUMBER
22
Direction
E
STREET_NAME
MARKET
STREET_TYPE
ST
City
STOCKTON
Zip
95202
APN
14904001
CURRENT_STATUS
02
SITE_LOCATION
22 E MARKET ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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soil of this area. The presence of fat clay from approximately 7 to 10 feet below grade further reduces <br /> the potential for vertical migration of residual contaminants. <br /> �. 4_2 Groundwater <br /> No dissolved petroleum hydrocarbon analytes were detected at any time during groundwater sampling <br /> +— from I989 to the present. <br /> V 5.0 FATE AND TRANSPORT ANALYSIS <br /> 55.11 Analysis of Problem <br /> To assess the threat to groundwater beneath the site, an evaluation of the potential migration of the <br /> hydrocarbons present in the soil was performed. The Fate and Transport exposure assessment is based <br /> y on a chemical's behavior in the environment, the rate and frequency of release, and the media into <br /> which it is released. For releases to soil, data on weather patterns, soil conditions and the underlying <br /> aquifer were obtained. The seasonal soil compartmental model SESOIL(General Sciences Corp.,June <br /> 1995) was utilized to determine the rate of vertical migration (leaching) toward groundwater at the <br /> subject site. <br /> 5_2 Processes Affecting Fate and Transuort <br /> The three general categories of processes affecting subsurface transport of petroleum hydrocarbons are <br /> hydrodynamic, abiotic (physiochemical), and biotic. Each of these processes in turn are dependent <br /> upon the physical properties of the subsurface and the physiochemical and biological properties of <br /> petroleum hydrocarbons. <br /> L.. <br /> Hydrodynamic processes impact contaminant transport by affecting the rate and direction(s) of <br /> groundwater flow(in both the saturated and unsaturated zones) and include advection, dispersion, and <br /> preferential flow. These properties are largely controlled by the physical properties of the subsurface in <br /> terms of the hydraulic conductivity (permeability) distribution, the driving head distribution (both <br /> spatially and temporally), and formation dispersivity. Generally, the contaminant properties do not <br /> exert a strong influence on hydrodynamic processes, however, for very low groundwater flow <br /> velocities, molecular diffusion (controlled by chemical-specific diffusion) may be significant (Knox and <br /> others, 1993). <br /> For the petroleum hydrocarbons at the subject site, the abiotic process of sorption is one of the most <br /> important in assessing contaminant fate. The physical property of the subsurface which largely controls <br /> this process is the organic carbon content of the sediments. The contaminant properties which control <br /> the process are solubility and octanol-water partition coefficient(Domenico and Schwartz, 1990). <br /> w.-W43681repor \scwil.doc 5 <br /> sh*H <br />
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