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2900 - Site Mitigation Program
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PR0540772
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Last modified
5/28/2021 11:06:29 AM
Creation date
5/28/2021 10:44:47 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
RECORD_ID
PR0540772
PE
2960
FACILITY_ID
FA0023306
FACILITY_NAME
LARRYS AUTO REPAIR
STREET_NUMBER
308
Direction
N
STREET_NAME
GRANT
STREET_TYPE
ST
City
STOCKTON
Zip
95205
CURRENT_STATUS
01
SITE_LOCATION
308 N GRANT ST
P_LOCATION
01
QC Status
Approved
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SJGOV\dsedra
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EHD - Public
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31 January 2013 <br />AGE-NC Project No. 02-0926 <br />Page 17 of 21 <br />9.3.6. Cost <br />Installation of an in-situ air sparging system and soil vapor extraction system will not be <br />required as both systems and utility infrastructure is currently installed at the site. However, <br />a minimum of two additional air sparging wells and one vapor recovery well should be <br />installed to more rapidly remediate the residual hydrocarbon impact at the site. <br />In general sparging equipment maintenance and monitoring would range from $15,000 to <br />$20,000 annually. In addition to sparging maintenance additional utility and monitoring cost <br />for operation of the carbon based SVE system at the site would be accrued. It is expected <br />that an annual cost of $10,000 to $20,000 would be needed to maintain and monitor the <br />onsite vapor extraction system. Based upon a treatment period of 12 to 24 months, and <br />including replacement of any carbon that would be expended during the remedial process, <br />the total costs would be in the range of $35,000 to $50,000; these costs would not include <br />the installation of the proposed three remedial wells. <br />9.4. MONITORED NATURAL ATTENUATION (MNA) <br />Natural attenuation, or passive bioremediation, is an alternative relying on natural <br />processes to degrade hydrocarbons. Biodegradation is the most important natural <br />attenuation mechanism. No additional bacteria or nutrients are added to the soil or <br />groundwater . Essential nutrients required for biodegradation are commonly naturally <br />occurring in the subsurface. Dispersion of contamination is an effective physical <br />mechanism to allocate mass into the area of naturally occurring bacteria which consume <br />hydrocarbons. However, where high concentrations of hydrocarbons are present at the <br />site, nutrients may be completely consumed before hydrocarbon remediation is complete. <br />Oxygen depletion in the subsurface is a characteristic of biodegradation. The core of a <br />contaminant plume is typically under anaerobic conditions and only the margins are <br />aerobic. Therefore, even though anaerobic biodegradation is much slower than aerobic <br />biodegradation, anaerobic processes may dominate the degradation of contaminants. <br />Groundwater movement will generally assist in the transport of nutrients in the saturated <br />zone. <br />Natural attenuation is normally used where low concentrations of hydrocarbons are <br />present, following completion of another form of remediation or in an area where no <br />domestic wells or shallow receptors are threatened. <br />In regards to the site, both the soil and groundwater plumes are both highly concentrated <br />in the UST area and downgradient of the former UST area. Impacted soils continue to <br />intensify the groundwater plume, which is evident by the high concentrations encountered <br />Advanced GeoEnvironmental, Inc.
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