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Environmental Health - Public
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0544201
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Last modified
7/17/2026 9:31:23 AM
Creation date
7/17/2026 9:24:41 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0544201
PE
2965 - RWQCB LEAD AGENCY WASTE DISCHARGE SITE
FACILITY_ID
FA0025122
FACILITY_NAME
FORMER OCCIDENTAL CHEMICAL CORP - LATHROP FACILITY
STREET_NUMBER
16777
STREET_NAME
HOWLAND
STREET_TYPE
RD
City
LATHROP
Zip
95330
APN
19818005
CURRENT_STATUS
Active, billable
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
16777 HOWLAND RD LATHROP 95330
Tags
EHD - Public
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J.R. Simplot Company - 2 - 11 June 2024 <br /> San Joaquin County <br /> Site data must be compared to the criteria in the State Water Resources Control <br /> Board's Low-Threat Underground Storage Tank Case Closure Policy (LTCP) to <br /> determine case closure eligibility. The LTCP is composed of eight General Criteria and <br /> three media-specific criteria. The LTCP media-specific criteria is discussed below: <br /> 1. Groundwater: The historical Site well network is composed of three wells installed <br /> in 1989 (MW-1, MW-2, MW-3). At the time of installation, MW-1 and MW-2 <br /> groundwater samples contained TPH and BTEX and MW-3 groundwater samples <br /> contained only BTEX. Benzene was reported at 2,800 micrograms per liter (ug/L) at <br /> MW-1 . The Water Quality Objective (WQO) for benzene is 1 ug/L. At the time of <br /> installation in 1989, Weston states that the groundwater in the immediate vicinity of <br /> the Site flowed northeast due to onsite groundwater treatment pumping (fumigant <br /> remediation). Water Board staff has observed groundwater flow toward the north <br /> regionally at nearby cleanup cases. MW-1 has not been located by subsequent <br /> environmental consultants after the 1989 sampling event. The annual samples <br /> collected from MW-2 and MW-3 did not adequately characterize petroleum <br /> hydrocarbon constituents dissolved in groundwater at the Site. Site data does not <br /> explain how most of the benzene mass observed in 2017 (8,760 ug/L benzene in <br /> MW-2) migrated. <br /> 2. Petroleum Vapor Intrusion to Indoor Air: Depth to water in 2023 was around 11 feet <br /> below ground surface (bgs). Site data appear to meet Scenario 3 criteria of the <br /> LTCP. <br /> 3. Direct Contact and Outdoor Air Exposure: Soil samples BH-1 through BH-3 and soil <br /> samples collected from MW-1 through MW-3 installation appear to meet direct <br /> contact criteria; with the exception that naphthalene was not analyzed. <br /> LTCP General Criteria are not met. A conceptual site model that assesses the nature, <br /> extent, and mobility of the release has not been completed. Secondary source <br /> petroleum hydrocarbon impact to soil and groundwater has not been adequately <br /> investigated; therefore, secondary source may not have been removed to the extent <br /> practicable. Based on the increasing trend of petroleum hydrocarbons immediately <br /> following drought years, it is likely that contaminant mass is still adsorbed to soil near <br /> the source area. Please submit a work plan to assess petroleum hydrocarbon <br /> constituents present in soil near the former USTs and to assess the nature and extent of <br /> impact to groundwater. <br /> By 12 August 2024, upload to GeoTracker a work plan to assess petroleum <br /> hydrocarbon constituents present in soil and groundwater near the former USTs and to <br /> investigate the extent of petroleum hydrocarbon impact to groundwater. <br /> If you would like to discuss the components of the work plan or the path forward for the <br /> UST investigation, please reach out to schedule a planning meeting with me. <br />
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