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ARCHIVED REPORTS_XR0011673
Environmental Health - Public
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EHD Program Facility Records by Street Name
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HOWLAND
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2900 - Site Mitigation Program
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PR0009015
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ARCHIVED REPORTS_XR0011673
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Last modified
2/5/2020 8:19:52 AM
Creation date
2/5/2020 8:09:02 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011673
RECORD_ID
PR0009015
PE
2960
FACILITY_ID
FA0004094
FACILITY_NAME
J R SIMPLOT (OCCIDENTAL CHEMICAL)
STREET_NUMBER
16777
STREET_NAME
HOWLAND
STREET_TYPE
RD
City
LATHROP
Zip
95330
APN
19818005
CURRENT_STATUS
01
SITE_LOCATION
16777 HOWLAND RD
P_LOCATION
07
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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GEOMATRIX <br /> disposal facility. After Simplot cleaned out the tanks in 1988, the sump pump connection was <br /> 1 changed to an aboveground pipe that transfers the stormwater to another part of the facility and <br /> ultimately to the Lathrop facility lined ponds located just east of Howland Road. <br /> 2.5 Area Hydrogeology <br /> Except where locally graded, the area ground surface drains toward the southwest. Soil in the <br /> Lathrop facility area consists of alluvial deposits of the San Joaquin and Stanislaus Rivers, Delhi <br /> Fane sands, Dinuba fine sandy loams and Fresno fine sandy loams with varying permeabilities from <br /> ' rapid to moderate (SCS, 1951). <br /> The California Department of Water Resources (DWR, 1967) indicates that the surficial, recent <br /> ' alluvial sediments in the Lathrop area are underlain by the Victor formation. The Victor <br /> formation comprises coarse-grained materials much like the surficial alluvium. The surficial <br /> 1 alluvium and the Victor formation reportedly extend from the surface to about 150 feet below <br /> ground surface (bgs) in the Lathrop area. In 1964, groundwater in the Lathrop area was at about <br /> 15 feet bgs or at an elevation of 0 feet above mean sea level. DWR suggested that area pumping <br /> ' has drawn down water levels allowing sea water incursion from the San Joaquin River delta. <br /> The U. S. Geological Survey (USGS, 1981) indicates that groundwater in San Joaquin County is <br /> used for municipal, industrial, and agricultural water needs. Groundwater in western San Joaquin <br /> County,which is from marine sediments of the Coast range, is of poorer quality than groundwater <br /> ' in eastern San Joaquin County, which is from igneous sediments of the Sierra Nevada range. This <br /> is manifested by a chloride plume that was characterized as 100 to 250 mg/Q in the Lathrop area. <br /> ' USGS also found that"Agricultural practices also appear to have affected the groundwater quality <br /> as demonstrated by greater-than-average concentrations of nitrate and total dissolved solids." <br /> ' The San Joaquin County Flood Control and Water Conservation District (FCWCD, 1991) <br /> reported that groundwater in the Lathrop area was at a depth of about 20 feet bgs and flowed to <br /> ' the north/northwest. <br /> Shallow groundwater below the Lathrop facility occurs at a depth of about 10 to 15 feet bgs and <br /> ' flows generally to the southwest (RWQCB, 1994). Shallow groundwater is of fair mineral quality g Y <br /> with total dissolved solids ranging from about 800 to 1,000 mg/Q. However, shallow groundwater <br /> ' has been found to contain detectable pesticides and is currently being remediated by OXY using <br /> a pump and treat method (TreaTek, 1992). Shallow groundwater below most of the Lathrop <br /> facility contained measurable concentration of DBCP, EDB, and/or sulfolane at the start of <br /> groundwater remediation in 1982. Shallow groundwater is currently being extracted via 7 extrac- <br /> tion wells. The extracted groundwater is then treated using activated carbon to removed DBCP <br /> 5 <br />
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