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2900 - Site Mitigation Program
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PR0543479
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Entry Properties
Last modified
4/14/2025 4:02:21 PM
Creation date
5/5/2020 9:15:06 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0543479
PE
2960 - RWQCB LEAD AGENCY CLEAN UP SITE
FACILITY_ID
FA0024679
FACILITY_NAME
CANEPA'S CAR WASH
STREET_NUMBER
6230
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95204
APN
081360030
CURRENT_STATUS
Active, billable
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
6230 PACIFIC AVE STOCKTON 95204
Tags
EHD - Public
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c ancpa 's Car Wash (Pacific Avenue) <br /> Problem Assessment Report and Corrective Action Plan <br /> Page 12 <br /> there is no deficiency, then nutrient addition would not increase microbial activity). Oxygen could be <br /> introduced through air sparging m chemical addition (an oxvgen releasing compound such as peroxide <br /> OI C('), or ozone) . Ozone can oxidize contaminants directly or through the formation ofhydioxyl radicals, <br /> and can enhance aerobic microbial activity to produce decomposition . However, effective injection <br /> Would require closely-spaced injection wells as noted in the air sparging discussion below. <br /> Alternative i , soil vapor extraction, involves the installation of perforated well casings into the vadose <br /> zone above the groundwater level , and use of a vacuum to remove the soil vapor with subsequent ex situ <br /> treatment (as necessary). As noted in Section 3 . 0, this site has been undergoing relatively consistent soil <br /> vapor extraction since 1999 . The decrease in soil vapor contaminant concentrations is an indication that <br /> the majority of contaminated soil vapor has been removed , and the likely source of soil vapor <br /> contaminant concentrations is off-gassing from the groundwater. Soil vapor extraction is not an effective <br /> method for removing contaminants from the groundwater. Consequently, further soil vapor extraction <br /> will be considered only in combination with other treatment methods as appropriate. <br /> Alternative 4, air sparging, involves the direct injection of air into the groundwater at or below the depth <br /> of contamination. Air sparging can provide an oxygen supply, as discussed in Alternative 2, above. <br /> However, the primary purpose of air sparging is to strip or volatilize contaminants that are then released <br /> into the soil vapor above the groundwater. Air sparging would normally be used in conjunction with soil <br /> vapor extraction. Air sparging also tends to cause additional groundwater circulation, further dispersing <br /> dissolved oxygen for greater enhanced biodegradation . Air sparging can be severely limited by soil <br /> characteristics. If the soil is sufficiently dense, then the injected air does not reach far from the injection <br /> well , and a large number of closely-spaced injection points are necessary. Also, if the soil allows for the <br /> development of preferential pathways, then again the injected air would not reach a wide area. The soil <br /> on site is heterogeneous (highly variable with interlaced silts, sands, and clays). Consequently, in a effort <br /> to maximize the effectiveness of air sparging, a large number of injection wells would be required . <br /> Alternative 5 , es situ groundwater treatment (the pump and treat alternative), can be effective; however, <br /> removal of the hydrocarbons can be very slow because the saturated soils may release the hydrocarbons <br /> trapped in blind pore space very slowly . In this alternative, groundwater is pumped from the aquifer and <br /> treated on the surface by any one of several treatment systems . Consequently, groundwater pump and <br /> treat systems often require an inordinately long time to complete remediation. A major benefit of pump <br /> and treat is that migration of the plume of contaminated water can be captured and directed toward the <br /> Pumping well . <br /> Alternative 6 , is the use of combinations of Alternatives 2 through 5 . The purpose of teaming the <br /> alternatives is gain synergy from the different alternative attributes. Pump and treat has the advantages of <br /> plume capture and removal of the contaminated groundwater in addition to lowering the water table <br /> exposing formerly saturated soil, allowing for vapor extraction from that soil . The air sparging system <br /> couples aeration and circulation of the groundwater with air lift to extract contaminated groundwater in <br /> each of the air sparging wells. A vapor extraction system can be used extract the contaminant-containing <br /> air resulting from the air sparging, or without air sparging a vapor extraction system can remove the <br /> contaminants adhering to the soil above the lowered water table. In any scenario the addition of oxygen, <br /> nutrients, or chemical oxidizers can potentially increase in situ contaminant degradation. <br /> 7.2 COMPARISONS OF REMEDIATION ALTERNATIVES <br /> The analytical data from initial groundwater monitoring through current monitoring has not indicated <br /> sufficient natural biodegradation . Enhanced in situ bioremediation with or without chemical oxidation is a <br /> ow <br /> IL 4) CONDOR <br />
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