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WORK PLANS FILE 2
Environmental Health - Public
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DURHAM FERRY
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3500 - Local Oversight Program
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PR0544624
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WORK PLANS FILE 2
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Last modified
7/3/2019 6:03:33 PM
Creation date
7/3/2019 3:33:15 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
FileName_PostFix
FILE 2
RECORD_ID
PR0544624
PE
3526
FACILITY_ID
FA0005206
FACILITY_NAME
GEORGES SERVICE
STREET_NUMBER
1600
Direction
W
STREET_NAME
DURHAM FERRY
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25510004
CURRENT_STATUS
02
SITE_LOCATION
1600 W DURHAM FERRY RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Geologfeal recklucs/Ac. Page 9 <br /> ' IRAP—Pilot Test <br /> Project No. 425.2 <br /> March 21,2005 <br /> ' 4.8 Soil Sampling <br /> ' Discrete soil samples will be collected in 6.0-inch brass liners using a 2.0-inch modified <br /> California split spoon sampler. All soil samples will be sealed with Teflon, capped with <br /> plastic end caps, labeled and placed in a cooler at 4° Celsius for transport to the laboratory <br /> ' following Chain of Custody protocol. <br /> Chemical Testing <br /> ' The soil samples will be analyzed for chemical appropriate constituents. <br /> 4.9 Sparge Point <br /> tThere are several commercially available sparge points to consider for use at the site. The <br /> apparatus selected will be chosen after consultation with the ozone equipment subcontractors. <br /> ' 4.10 Ozone Sparging Equipment <br /> ' The ozone sparging equipment will consist of an ozone generator, air compressor, manifold <br /> piping, pressure gauges and distribution valves. Three bids must be solicited for the project <br /> in order to stay in compliance with USTCFP requirements. <br /> The required injection pressures and flow rates utilized in the sparging system must be <br /> sufficient to overcome the head pressure of the overlying water column and the capillary <br /> ' pressure of the subsurface soil. The flow rates must be as high as possible to deliver ozone to <br /> the maximum possible area of the plume. The injection pressures will be lower than the <br /> pressures which may cause the lateral spreading of contamination plume. - k, <br /> Initially, air will be injected into the subsurface to open up the soil pore space. The <br /> pressurized air will be delivered through diffusers that will introduce fine bubbles into the <br /> ' soil. The bubbles will form micro-channels or preferential pathways through which the air <br /> will flow. While in the channels the air will allow the gasoline to undergo a phase transfer <br /> from dissolved to vapor phase. After the initial air injection, the ozone will then be <br /> ' introduced into the soil at a concentration of approximately 5% ozone & 95% oxygen. The <br /> system will operate in pulse mode to allow the micro-channels to repeatedly fill and empty <br /> which will cause a reaction chamber type response. The ozone will oxidize the MTBE as <br /> ' well as other constituents and unconsumed oxygen will serve to augment the bio-remediation <br /> capacity of the aquifer. <br /> ' The EPA has stated that 1 PSI of injection pressure is necessary for every 2.3 feet of <br /> hydraulic head. (USEPA: How to Evaluate Alternative Cleanup Technologies for <br /> ' Underground Storage Tank Sites, May, 1995). Water Table is at about 12 feet bgs. This <br /> would require an injection pressure of 4.4 PSI(10 feet divided by 2.3). <br /> 1 <br />
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