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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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04 January 2000 <br /> AGE-NC Project No. 95-0106 <br /> Page 3 of 5 <br /> • Petroleum hydrocarbons may be migrating as dissolved constituents through clay-rich soil <br /> at shallow depths, approximately 5 to 10 feet bsg, in the shallow saturated zone and capillary <br /> fringe zone; or <br /> • Petroleum hydrocarbons may be migrating as dissolved constituents through sandy soil layers <br /> lying 10 to 25 feet bsg. <br /> In the former case, a greater potential for human exposure may be anticipated. Conversely,the latter <br /> case would demonstrate a natural barrier, approximately 10 feet thick, to human exposure. In <br /> addition, migration through the upper fine-grained unit would retard the spread of hydrocarbons, <br /> while migration via the lower coarse-grained unit would facilitate lateral spread of hydrocarbons, <br /> potentially impacting a greater volume of ground water. <br /> AGE proposes the following scope of work to test the two scenarios, to properly assess the extent <br /> and magnitude of the plume of dissolved hydrocarbons, and to derive information to properly assess <br /> the risk posed by the presence of petroleum hydrocarbons in soil and ground water: <br /> • Advance two soil probe borings to approximately 18 feet bsg, collect continuous soil <br /> samples,collect ground water samples near the capillary fringe zone at approximately 6 feet <br /> bsg, and collect ground water samples from the deeper saturated zone, presumably in sandy <br /> soil, at 17.5 feet bsg. <br /> • Advance five soil probe borings to collect soil and grab ground water samples near the <br /> capillary fringe and in the deeper saturated zone as described above, to further assess the <br /> hydrocarbon-impacted ground water north of the former UST location. Figure 1 shows the <br /> proposed probe boring locations. <br /> • Advance one hand auger boring to the capillary fringe zone, estimated to lie at approximately <br /> 6 feet bsg,to collect one soil sample and grab ground water sample. The hand auger boring <br /> will not exceed a depth of 9 feet bsg. If soil or ground water samples from the hand auger <br /> boring yield field indications of petroleum hydrocarbons, a second hand auger boring (the <br /> contingency hand auger boring on Figure 1)will be advanced approximately 30 feet further <br /> down-gradient for similar soil and ground water sampling. <br /> • Establish a vertical sequence of soil lithology to delineate potential permeable pathways <br /> (sandy soil) with the continuous cores. <br /> • Analyze the soil and ground water samples for TPH-g,BTEX and oxygenated fuel additives <br /> (DIPE, ETBE, MTBE, TAME and TBA) in accordance with EPA Methods 8015M/5030, <br /> 8020/602 and 8260M, respectively. <br /> Advanced GeoEnvironmental,Inc. <br />
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