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ARCHIVED REPORTS_XR0003917
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545420
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ARCHIVED REPORTS_XR0003917
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Last modified
3/5/2020 5:49:46 PM
Creation date
3/5/2020 4:52:54 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003917
RECORD_ID
PR0545420
PE
3528
FACILITY_ID
FA0003815
FACILITY_NAME
TESORO (SPEEDWAY) 68154
STREET_NUMBER
2500
Direction
W
STREET_NAME
LODI
STREET_TYPE
AVE
City
LODI
Zip
95240
APN
02740006
CURRENT_STATUS
02
SITE_LOCATION
2500 W LODI AVE
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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air stripping, aeration, adsorption, absorption, ultraviolet oxidization, chemical <br /> oxidization, or biological. <br /> The removal of groundwater by pumping creates a depression in the groundwater <br /> potentiometric surface that draws in groundwater from the surrounding area. This <br /> depression (radius of influence) can contain the petroleum hydrocarbon plume and <br /> prevent further migration of the plume downgradient toward sensitive receptors such as <br /> drinking water wells. <br /> 3.1.3 In-situ Bioremediation <br /> Remediation of organic contaminants dissolved in groundwater can be accomplished <br /> through bioremediation. Biodegradation of organic compounds occurs naturally in the <br /> subsurface due to the activity of microorganisms. Aerobic and anaerobic bacteria break <br /> down the organic compounds into simple inorganic compounds such as carbon dioxide <br /> and water. Natural biodegradation is often limited due to the lack of nutrients and oxygen <br /> in the subsurface. <br /> Bioremediation is the process by which natural biodegradation is accelerated by the <br /> addition of oxygen and nutrients. Injection wells are installed into the water bearing zone <br /> to inject air and nutrients to aid the biodegradation process and accelerate the rate of <br /> biodegradation reactions. <br /> 3.1.4 Containment Barriers <br /> Containment of the groundwater can be accomplished by installing either a low <br /> permeability barrier to prevent the flow of groundwater or a reactive barrier to chemically <br /> control migration of the contaminants. In shallow groundwater conditions (<20 feet), a <br /> slurry wall can be installed using a backhoe or excavator and filling the trenches with a <br /> bentonite/cement slurry. In deeper groundwater areas, the low permeability material is <br /> installed using a large diameter auger rig with overlapping drilling locations to eliminate <br /> gaps in the barrier. The borings created by the drilling rig are filled with the bentonite <br /> cement slurry. A reactive barrier is constructed using a material that chemically reacts <br /> with the contaminates to reduce or oxidize them to inert compounds. <br /> 3.2 Evaluation of Remedial Alternatives <br /> In this section, the remedial alternatives. presented in Section 3.1 are evaluated with <br /> respect to constraints of implementation at an operational service station, relative <br /> advantages and disadvantages, and potential costs. The rationale for implementation of <br /> the proposed alternative is also provided. <br /> M <br /> 3-2 <br /> E53r1E:1U5A100651REPORT510065P201.DOC-98usg:I Rev.0,1/26199 <br /> 20A41-007.001 <br />
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