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ARCHIVED REPORTS XR0000990
EnvironmentalHealth
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BUSINESS LOOP 205
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3500 - Local Oversight Program
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PR0544135
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ARCHIVED REPORTS XR0000990
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Last modified
2/12/2019 10:38:48 AM
Creation date
2/12/2019 10:13:43 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0000990
RECORD_ID
PR0544135
PE
3528
FACILITY_ID
FA0005488
FACILITY_NAME
STRONG, RUTH
STREET_NUMBER
5157
Direction
W
STREET_NAME
BUSINESS LOOP 205
City
TRACY
Zip
95376
CURRENT_STATUS
02
SITE_LOCATION
5157 W BUSINESS LOOP 205
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
WNg
Tags
EHD - Public
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29 April 2005 <br /> r - <br /> AGE-NCProject No..98-0440' <br /> _ Page•17 of-18 <br /> Oxygen depletion in the subsurface is a ' haracteristic`of biodegradation: The core of a contaminant <br />' plume is typically under anaerobic conditions and only the margins are aerobic. Therefore, even , <br /> though anaerobic biodegradation is much slower than aerobic,biodegradation, anaerobic processes <br /> s -may dominate,the degradation of contaminants:Grourid-watei movement will generally assist in the - <br /> transport of nutrients in'the saturated zone. . <br /> The objective of the MNA is to collect ground water samples through techniques which generally ' <br /> minimize undesired exposure to atmospheric conditions when and where allowable;and to monitor <br />' for parameters which signal'the natural attenuation of dissolved-hydrocarbons. Generally the ; <br /> geochemical parameters'selected for monitoring are based on the'.use of terminal electron:acceptors <br /> I consume hydrocarbons. The sampling for NINA analysis would be.conducted <br />' during,the'monitoring events to reduce overall,costs, to established a'trend of the geochemical <br /> parameters and demonstrate the presents of terminal electron acceptors metabolized by-products. <br /> Natural attenuation is normally used where .low, concentrations of hydrocarbons are present, <br /> following completion of another form of remediation or in an area where no domestic or,irrigation <br /> wells are threatened. <br /> 'Co'sts for natural attenuation are generally lower than most active.remediation options; however, <br /> costs can be highly variable depending on the duration and type of monitoring required.' <br /> Fate and Transport modeling may be used to demonstrate the.potential for hydrocarbons to impact. <br /> nearby ground water receptors. Quarterly,ground water monitoring may also be.used to demonstrate', <br />' astable and declining ground water plume. <br /> 8.0. _ 'RECOMMENDATIONS <br /> The- following recommendations for .remediation are based upon data collected during the <br /> investigatiori'of the property and predicted responses from the site conceptual'model. <br /> • .. ' .. ' „1 - , , i .. Y i , . try <br />' .8.1, REMEDIATION OF-HYDROCARBON-IMPACTED SOIL ; <br />' Vadose',zone soil impacted by,TPH-d, TPH-g; and BTEX extends vertically to the saturated zone ` <br /> under,the former:UST and.surrounding areas to an approximate depth of 17 feet bsg. Excavation' <br /> would require the removal of a moderate. volume of'overburden soil in-the former 'UST and <br />' surrounding areas.Figure 9 illustrates the approximate area of proposed excavation. Because'there- <br />' appears.to be a low-feasibility for bioremediation and`monitored natural attenuation,AGE concludes <br />�. "Advanced GeoEnvireimental,Inc. <br />
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