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ARCHIVED REPORTS_XR0004910
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3500 - Local Oversight Program
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PR0545431
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ARCHIVED REPORTS_XR0004910
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Last modified
3/9/2020 4:53:32 PM
Creation date
3/9/2020 12:00:20 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004910
RECORD_ID
PR0545431
PE
3528
FACILITY_ID
FA0005191
FACILITY_NAME
FULLER MOBILE HOME PARK
STREET_NUMBER
365
Direction
E
STREET_NAME
LOUISE
STREET_TYPE
AVE
City
LATHROP
Zip
95330
APN
19627022
CURRENT_STATUS
02
SITE_LOCATION
365 E LOUISE AVE
P_LOCATION
07
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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I <br /> Fuller Mobile Nome Park <br />' 36S E. Louise Ave., Lathrop, California May 28, 1998 <br /> • Phase II Site Characterization - Continued Page: 6 <br />' and the 310,000 ug/kg found at B-11 at 12 5' in depth in the 1998 sample These <br /> comparisons are used based on the proximity to the former UST location <br />' 6.0 Groundwater Conditions <br /> The water table was approximately 10 feet below ground level as the borings were being <br />' drilled During the quarterly event on April 8, 1998, subsequent water levels before <br /> sampling recorded water levels in the vicinity of 8 5 feet below ground level (Table 3) <br />' A groundwater gradient 0 0160 ft/ft was calculated (Figure 4) The direction is S63°W <br /> across the site <br /> I <br /> 7.0 Conclusions and Recommendations <br /> IThe soil contamination "plume" has been defined at this site A groundwater <br /> contamination plume exists at varing depths from approximately 10' bgl to approximately <br /> lie <br /> 32 5' bgl at the eastern boundary of the former underground tanks The lateral and <br /> vertical extent is completely defined Only one (1) monitoring well showed some traces of <br /> contamination The groundwater gradient direction is (at the time of sampling - April 8, <br /> 1998) to the SW With the shallow water table and the exceptionally flat groundwater <br /> gradient, contaminants have been moving laterally with the variable gradients caused by <br /> pumping of wells, irrigation of nearby fields and precipitation The Delhi sand that covers <br /> I the area is a very permeable sand that overlies a sandy silt (in some areas) that is in contact <br /> with the water table This is evidenced by contamination over 50 feet down gradient and <br /> over 60 feet laterally from the past gradients, and both soil and water samples have higher <br /> Icontamination levels to the south and west of the former tank site <br /> The following facts support the vertical and lateral definition of both soil and <br />' groundwater <br />' The most recent groundwater data collected indicates only Diesel contamination present at <br /> monitoring well #7 This 60 ug/L of Diesel is within the State of Californias allowable <br /> level of 100 ug/L All other wells tested non-detected for all analytes The water sample <br />' collected from boring B-12 at 12 5' bgl indicates 3000 ug/L of Gasoline, 4 4 ug/L of <br /> Ethyl-Benzene and 33 ug/L of total Xylenes These levels of Ethyl-Benzene and total <br /> Xylenes are well below the established allowable levels (Xylenes - 1,750 ug/L, E-Benzene <br />' 700 ug/L) The Gasoline level does exceed the allowable level of 5 ug/L <br /> The defined mass of the secondary source of petroleum hydrocarbon is calculated to be <br /> approximately 1,150cubic yards in quantity underlying the former UST location The <br />
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