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3500 - Local Oversight Program
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PR0544705
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Last modified
7/29/2019 10:46:31 AM
Creation date
7/29/2019 10:40:58 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
RECORD_ID
PR0544705
PE
3526
FACILITY_ID
FA0003754
FACILITY_NAME
CALIFORNIA FUELS
STREET_NUMBER
3147
Direction
S
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95206
APN
17512003
CURRENT_STATUS
02
SITE_LOCATION
3147 S EL DORADO ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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.i Microbubble Oxidation Smokes MTBE and BTEX Page 1 of 3 <br /> Microbubble Oxidation Smokes NITBE and BTEX <br /> C-Sparge TM Ozone Microsparging for Rapid Removal of MTBE and Benzene <br /> By William B. Kerfoot, Ph.D., LSP and Angus McGrath, Ph.D. <br /> A system called C-SpargingT which uses ozone/air injected periodically in <br /> conjunction with a pulsing pump has been demonstrated to reduce MTBE from <br /> over 1000 ppb to less than 100 ppb in less than 40 days. The rate of decay was cmass rxar <br /> found to be a ten-fold reduction in monitoring wells located 3 to 7 meters from the coaaaxasos p sowexsal <br /> injection point. Monitoring was performed weekly during and after treatment. r R mexN9ErsYurer; <br /> l=WW <br /> What is C-Sparginim ruaeauva ` <br /> The KVA process of C-SpargingTm, in sita air stripping with micro-encapsulated -� smsar e:uree <br /> ',^ CIAkt34Ni <br /> �i ozone, combines three- unit operations offering aone-two-three punch to knockout <br /> - MTBE. Firstly, fine bubbles with a high surface-to-volume ratio are injected into c <br /> the saturated zone to extract dissolved MTBE from contaminated groundwater. <br /> Secondly, ozone contained within the bubble and thin film around the bubble <br /> PUMP <br /> reacts extremely rapidly to decompose the MTBE into simple products, alcohols, <br /> acetate and formate. Thirdly, the residual oxygen from the reaction encourages azmin px <br /> bioremediation which consumes the breakdown products and converts them to <br /> carbon dioxide (CO2) and water (H2O). <br /> l r <br /> ri <br /> Ozone Microsparging is a Patented Technology for fn Situ Treatment of .ettvr <br /> Volatile Organic Compounds (VOCs) in Groundwater s smar t,wnt <br /> The reaction detoxifies groundwater containing MTBE and BTEX compounds, } rhssmoasT <br /> specifically benzene, rapidly to groundwater standards without producing hamif d c» u ALVE <br /> byproducts. The reaction is produced with very low ozone concentrations-molar ur uow <br /> zv <br /> ratios-compared to VOC concentrations in groundwater. The technology combines <br /> the unit operations of air stripping and oxidative decomposition in a single process asuatuwvmi.< <br /> which can be catalytically accelerated. In the C-SpargeTM process, air and ozone 'f' WAtSM1141 <br /> are injected directly into groundwater through specially-designed spargers to <br /> create "microbubbles" that have very high surface area-to-volume ratio. The Figure 1. master control unit <br /> Henry's Constant which regulates the partitioning of MTBE from aqueous to <br /> gaseous state is about one-tenth that of benzene derivatives. However, the surface-to-volume ratio increase of over 30- <br /> fold compensates to promote rapid in situ stripping of MTBE. As the "microbubbles" rise within a saturated column <br /> of groundwater, they extract or "strip" the VOCs from aqueous to gas partitioning. Upon entering the microbubbles, <br /> MTBE and BTEX compounds react with ozone in the gaseous state or in the aqueous "thin layer" surrounding the <br /> bubble to decompose. MTBE is rapidly degraded with time. The rate of decay is similar to that previously reported by <br /> Karpel vel Leitner, et. al. ( 1994). In both bench-scale testing and field testing, ozone microbubbles appeared effective <br /> _. in reducing MTBE concentrations to beyond 90% of original levels (Kerfoot, 2000). The rate of removal has been <br /> sensitive to ozone concentration, pressure, and iron silicate content. <br /> Site Specific System Set-up <br /> A-singlepargerg-master4ruit with-6-SpargepointsO wasinstalle -upgradie-nt of plume—region—. The—unit can-b <br /> installed with a dual-screened recirculation spargewell which has a lower Spargepoint® or with isolated <br /> Spargepoints®. The depth to groundwater was 2 to 3 meters. The general construction of a C-SpargeTM consists of a <br /> 100 mm casing leading to a 1 .5 meter screen with 0.5 meter above the water table, a blank casing which was <br /> bentonite-sealed in the annular space to prevent short-circuiting, and a lower 1 .5 meter screen (10 slot). Alongside this <br /> - .� was a 1 .5 cm diameter tubing leading from the wellhead region to a 50 mm microporous Spargepoint(k 46 cm long <br /> r_1 <br /> with a compression fitting situated below the lower double screen. <br /> -- The predominant soil type was gravelly sands. Water table level occurred at 2 to 3 meters. The predominant <br /> contaminated region extended vertically from 1 to 3 meters deep. The Spargepoints@ were installed at a depth of 10 <br /> — meters. <br /> i <br /> i <br /> http://www.kva-equipment.com/papers/microbub.htm 4/5/02 <br />
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