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2900 - Site Mitigation Program
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PR0543548
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Last modified
6/3/2020 11:15:53 AM
Creation date
6/3/2020 10:30:27 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0543548
PE
2960
FACILITY_ID
FA0024728
FACILITY_NAME
SUPER STORE INDUSTRIES LATHROP DISTRIBUTION CENTER
STREET_NUMBER
16777
STREET_NAME
HOWLAND
STREET_TYPE
RD
City
LATHROP
Zip
95330
APN
19816026
CURRENT_STATUS
01
SITE_LOCATION
16777 HOWLAND RD
P_LOCATION
07
QC Status
Approved
Scanner
TSok
Tags
EHD - Public
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Geosyntec <br /> sands and gravels (USACE, 2013). As biosparge wells are operated over time, the groundwater <br /> within the injection ZOI,now with elevated DO concentrations,moves downgradient.This slower <br /> migration of DO downgradient of the biosparge point is not included as part of the well ZOI; <br /> however, these elevated DO concentrations are still expected to promote the biodegradation of <br /> sulfolane in groundwater beyond the initial ZOI. <br /> Because sulfolane is present in the highly transmissive zone, a ZOI ranging from 15 to 25 feet <br /> around the sparge point is expected.The ZOI may also be enhanced laterally by two factors: 1)the <br /> confinement of the transmissive zone by overlying lower-permeability silts and clays, which will <br /> likely limit vertical movement of the injected air; and 2)high groundwater velocity in the vicinity <br /> of the test areas due to ongoing pumping in the area. Therefore, placing the wells at different <br /> distances from each other allows for flexibility to conduct the pilot test with various groundwater <br /> flow directions and horizontal gradients. The proposed well layout at each PTA is shown on <br /> Figures 4a, 4b and 4c. Please note these well locations are approximate; exact locations will be <br /> adjusted in the field depending on access constraints and existing above-ground and underground <br /> utilities. <br /> Each of the proposed biosparge/observation wells will be screened to monitor and/or deliver air <br /> within the primary sulfolane transport pathway zone in the well-graded sand and gravel at depths <br /> of approximately 240 to 270 feet bgs. Using this pilot test well layout near the new supplemental <br /> characterization wells installed at locations 1, 2 and 3, Geosyntec will confirm biosparge ZOI, <br /> evaluate the persistence of DO, and confirm ability to aerobically biodegrade sulfolane. In <br /> addition, Geosyntec will evaluate effects of biosparging on geochemical parameters including <br /> ammonia, sulfate, nitrate and total and dissolved iron and manganese and aesthetic parameters <br /> such as color that may affect water quality. These data will help design potential future full-scale <br /> biosparge injection and monitoring well spacings. Based on the data and results of the ongoing <br /> laboratory microcosm study, it is possible that nutrient amendment (likely diammonium <br /> phosphate) and/or bioaugmentation (with sulfolane degraders from either the BSW area or a <br /> commercial culture) may be necessary to promote aerobic sulfolane degradation. Should this be <br /> necessary, Geosyntec would pursue the required Waste Discharge Requirement(WDR)approval. <br /> Operation and performance monitoring of the pilot test is initially proposed to be conducted for <br /> approximately 2 to 3 months to demonstrate feasibility of ISB at PTA A and B (and possibly <br /> PTA C),and to evaluate the need to optimize ISB for full-scale design, if necessary. If biosparging <br /> is successful, the pilot test may be extended coincident with development of a full-scale approach <br /> to offer continued protection of the downgradient supply wells. <br /> In-Situ Bioremediation Pilot Test Work Plan—GSH Lathrop 7 <br />
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