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SITE INFORMATION AND CORRESPONDENCE FILE 2
Environmental Health - Public
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EHD Program Facility Records by Street Name
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DURHAM FERRY
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1600
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3500 - Local Oversight Program
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PR0544624
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SITE INFORMATION AND CORRESPONDENCE FILE 2
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Last modified
7/3/2019 6:16:25 PM
Creation date
7/3/2019 3:32:21 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
SITE INFORMATION AND CORRESPONDENCE
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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Former Georges Service Page 2 of 3 <br /> 1600 Durham Ferry Road 16 January 2008 <br /> Tracy, CA 95376 <br /> degradation of the petroleum hydrocarbons in groundwater in an offsite area <br /> where other remedial options cannot be readily applied. <br /> The EHD is concerned with a few technical issues regarding the recommended <br /> remedial approaches, the greater concern being with the air sparging proposal. <br /> The EHD notes that the site geology consists primarily of fine-grained soil from <br /> surface to approximately 20 feet bsg and is coarse-grained from approximately <br /> 20 feet to 40 feet bsg, and consists of alternating coarse- and fine-grained units <br /> to total depth explored (approximately 95 feet bsg). The depth to water on the <br /> site is generally on the order of 12 feet bsg, thus air sparged into the saturated <br /> zone at either 22 feet bsg or 38 feet bsg must migrate vertically through low <br /> permeability soil to reach the vadose zone in either natural soil or the excavation <br /> backfill. As the vertical permeability may be one to two orders of magnitude less <br /> than the horizontal permeability, the EHD is concerned that sparged air will tend <br /> to migrate horizontally and not necessarily remove stripped hydrocarbons into <br /> the excavation backfill vadose zone for recovery. This potential problem <br /> becomes more likely as the distance between the sparging point and the former <br /> excavation increases; one proposed sparge point is nearly 50 feet from the <br /> former excavation. The EHD is concerned that air sparged such great distances <br /> from the proposed recovery point simply will not be recovered, and may therefore <br /> act to spread the plume rather than remediate it. <br /> The EHD will approve a phased approach toward testing SVE and IAS on your <br /> site and recommends the following approach: <br /> • Conduct a limited SVE test on the existing SVE wells in the excavation <br /> backfill to characterize recovered air and vapor without benefit of IAS; <br /> • Install and utilize IAS wells AS-5 through AS-8 and test with SVE system, <br /> note differences in SVE response, operate the IAS well(s) with a tracer to <br /> document potential recovery of the sparged air; <br /> • If the air injected in the initial IAS wells is recovered, step outward to the <br /> more remote proposed IAS wells and test in like manner; <br /> • Include a monitoring design to detect any plume migration caused by <br /> unrecovered sparged air. <br /> Submit a work plan to the EHD by 17 March 2008 for pilot testing SVE and IAS <br /> that addresses the concerns and recommendations noted above. <br /> The EHD recognizes the limited options available to address and remediate <br /> impacted groundwater that has migrated off-site. Submit a work plan for installing <br /> and monitoring the ORC installation. Much of this has been included in the RAP, <br /> but the EHD believes a method for closely monitoring the effectiveness of the <br /> system should be included. The proposed ORC installation points in the roadway <br /> are in a high traffic area and a traffic control plan accepted by the appropriate <br /> traffic agency for that location must be properly implemented for worker and <br /> motorist safety. <br /> WP Comment Letter 0108.doc <br />
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