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ARCHIVED REPORTS_XR0005610
EnvironmentalHealth
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14800
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3500 - Local Oversight Program
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PR0545626
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ARCHIVED REPORTS_XR0005610
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Last modified
11/19/2024 1:50:29 PM
Creation date
4/29/2020 1:42:36 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005610
RECORD_ID
PR0545626
PE
3528
FACILITY_ID
FA0000957
FACILITY_NAME
LATHROP GAS & FOOD MART*
STREET_NUMBER
14800
Direction
S
STREET_NAME
STATE ROUTE 99
STREET_TYPE
RD
City
MANTECA
Zip
95336
APN
19702004
CURRENT_STATUS
02
SITE_LOCATION
14800 S HWY 99 RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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i <br /> PROBLEM ASSESSMENT REPORT <br /> 14800 West Frontage Road Manteca California <br /> I4 3 Groundwater Conditions <br /> Groundwater elevations have risen, since Aegis began recording measurements <br /> (January 1991), a maximum average of approximately 3 21 feet and fallen a maximum <br /> average of approximately 0 71-feet (Table 5) The rise of groundwater occurred between <br /> the months of February and September 1991 (Figure 6) The direction of groundwater <br /> flow for the period of January through August 1991 was north-northeast Beginning in <br /> October 1991 through January 1992, groundwater flow had no apparent direction <br /> Beginning with the February 1992 measurements and continuing to the present <br /> (April 20, 1992), groundwater flow is to the southwest (Figure 7) <br /> 4 4 Distribution of Petroleum Hydrocarbons in Groundwater <br /> Figure 8 indicates the distribution of concentrations of TPH, as gasoline, and benzene in <br /> groundwater As shown on the figure, the highest concentrations of petroleum <br /> hydrocarbons were reported in the water sample collected from MW-4 on <br /> January 31, 1992 Concentrations of TPH, as gasoline, and benzene shown on Figure 8 <br /> are also reported in Table 3 <br /> Floating liquid hydrocarbons have not been observed in any of the nine wells at the <br /> project site Figure 8 indicates an inferred "zero line" for the extent of dissolved <br /> hydrocarbons in groundwater <br /> 5.0 REMEDIAL ACTION ALTERNATIVES <br /> The following sections discuss appropriate sod and groundwater remedial alternatives <br /> iEach section provides a general description and technical critique of the respective <br /> remediation alternative <br /> 5.1 Soil <br /> In general, sal remediation alternatives are dictated by site size, subsurface conditions, <br /> contaminant types, contaminant concentrations, and the volume of contaminated soil <br /> Sal remediation alternatives can be broken into two broad categories, ex-situ and in-situ <br /> Ex-situ sal remediation involves excavation of the soil and the selection of an appropriate <br /> I treatment and/or disposal option In-situ remediation options generally include the <br /> prevention of the migration of contaminants or destruction/removal of the contaminants <br />' while still in the subsurface Typically, sal treatment options are effective for a limited <br /> number of organic compounds The presence of certain organic compounds <br /> (polychlorinated byphenyls, certain pesticides, etc ) and certain inorganic compounds <br /> I (metals, acids, etc ) above regulated concentrations may limit treatment and disposal <br /> options In some cases where multiple contaminants are involved, treatment is utilized <br /> to reduce contaminant concentrations of a select number of compounds in order to <br /> increase disposal options <br /> 90-097A PAR 8 <br />
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