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WORK PLANS 1994-2010
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0540667
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WORK PLANS 1994-2010
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Entry Properties
Last modified
2/8/2019 8:42:54 AM
Creation date
2/7/2019 4:39:15 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
FileName_PostFix
1994-2010
RECORD_ID
PR0540667
PE
2960
FACILITY_ID
FA0023252
FACILITY_NAME
WELDON CHURCH PROPERTY
STREET_NUMBER
104
Direction
W
STREET_NAME
BEVERLY
STREET_TYPE
PL
City
TRACY
Zip
95376
CURRENT_STATUS
01
SITE_LOCATION
104 W BEVERLY PL
QC Status
Approved
Scanner
WNg
Tags
EHD - Public
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02 December 1998 <br /> AGE-NC Project No. 95-0106 <br /> Page 2 of 4 <br /> A total of 15 soil borings have been advanced on and off the site, 7 of which have been completed <br /> as ground water monitoring well,providing data concerning hydrocarbon impact on soil and ground <br /> water, soil composition, and ground water flow direction. Laboratory analysis of soil samples <br /> collected from monitoring wells and soil probe borings constrain the plume of impacted soil to the <br /> immediate vicinity of the former UST excavation. The lateral extent of impacted ground water <br /> appears to be delineated northeast, east, south, west and northwest of the former UST excavation, <br /> but ground water samples collected north of the former UST excavation, from well MW4, have <br /> consistently contained total petroleum hydrocarbons quantified as gasoline (TPH-g), benzene, <br /> toluene, ethylbenzene and total xylenes(BTEX). Over the last five monitoring events, benzene and <br /> TPH-g concentrations in ground water samples collected from MW4 have averaged 131.8 <br /> micrograms per liter (µg/1) and 3,040 ug/l, respectively. Benzene concentrations exceeding the <br /> California maximum contaminant level (MCL) for drinking water of 1 4g/1 represents a potential <br /> threat to human health and ground water in a residential area. Lower concentrations of petroleum <br /> hydrocarbons have been detected in samples collected from MW1, located approximately 25 feet <br /> north-northeast of the former UST excavation, but were not detected during the last monitoring <br /> event. <br /> The occurrence of TPH-g and BTEX in ground water encountered in an off-site well (MW4) <br /> indicates that a plume of dissolved hydrocarbons has migrated north of the site. The lateral extent <br /> of the impacted ground water has not been delineated <br /> Two potential migration routes for the hydrocarbon-impacted ground water are suggested by the <br /> impacted ground water encountered in well MW4: <br /> • Petroleum hydrocarbons may be migrating as dissolved constituents at shallow depth, <br /> approximately 5 to 10 feet bsg through clay-rich soil, in the shallow saturated zone and <br /> capillary fringe zone, or <br /> • As dissolved constituents migrating through sandy soil layers lying 10 to 25 feet bsg. <br /> In the former case, greater risk to human health and safety may be anticipated, but in the latter case, <br /> greater risk to ground water may exist due to the higher degree of mobility of dissolved <br /> hydrocarbons in sandy soil. Figures 3 and 4 show available soil and selected analytical data in cross <br /> sectional view. <br /> Advanced GeoEnviron mental,Inc. <br />
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