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ARCHIVED REPORTS_XR0012415
Environmental Health - Public
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EHD Program Facility Records by Street Name
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M
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MARCH
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2701
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3500 - Local Oversight Program
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PR0545517
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ARCHIVED REPORTS_XR0012415
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Last modified
3/11/2020 11:52:06 PM
Creation date
3/11/2020 11:39:51 AM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012415
RECORD_ID
PR0545517
PE
3528
FACILITY_ID
FA0003798
FACILITY_NAME
MARCH LANE 76*
STREET_NUMBER
2701
Direction
W
STREET_NAME
MARCH
STREET_TYPE
LN
City
STOCKTON
Zip
95219
APN
11619007
CURRENT_STATUS
02
SITE_LOCATION
2701 W MARCH LN
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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technology combines the urut operations of air stripping and oxidative <br /> decomposition in a single process which can be catalytically accelerated In the <br /> C-SpargeTM pro:,ess, air and ozone are injected directly into groundwater through <br /> ' specially-designed spargers to create small "microbubbles" that have a very high <br /> surface area to volume ratio As these microbubbles rise within a column of <br /> ' water, they extract or "strip" VOCs from groundwater by aqueous to gas <br /> partitioning Upon entering the nucrobubbles, the VOCs are rapidly oxidized by <br /> the process of Criegee oxidation The ozone contained within the bubbles reacts <br /> to decompose the chlonnated ethane molecule in an extremely rapid gas/liquid <br /> phase reaction whose end products are carbon dioxide, very dilute hydrochloric <br /> acid, and water By increasing the ozone content within the bubbles, the rate of <br /> ' oxidation reaction is increased Properly applied, the reaction has been used to <br /> rapidly detoxify halogenated VOCs (HVOCs), ethene and ethane derivatives and <br /> aromatic compounds in groundwater sources to below drinking water standards <br /> ' without producing unwanted harmful by-products (Kerfoot, 1997, Kerfoot, et al , <br /> 1998) <br /> Oras entering a small bubble of volume 4n? increases until reaching an <br /> asymptotic value of saturation If we consider the surface of the bubble to be a <br /> ' membrane, a first order equation can be written for the monomolecular reaction <br /> dx = -k(Q-x) {1) <br /> dt <br /> Where x = the time varying concentration of the substance in the bubble <br /> ' dxldt = the rate of change of vapor concentration within the gaseous <br /> phase <br /> Q = the external concentration of the HVOC <br /> ' K = the absorption constant, set by Henry's partitioning coefficient <br /> If at time t = 0, x = 0, then <br /> X = Q(1-e i') (Z) <br /> ' The constant k is found to be <br /> -k= dxrdt (3) <br /> ' Q-x <br /> Normally, the rate of adsorption reaches an asymptotic value because the <br /> ' concentration of x within the bubble becomes at equilibrium with the Henry's <br /> coefficient However, if ozone decomposes the incoming vapor, the mass <br /> ' removal rate will increase <br /> . Since MTBE occupies a partitioning region similar to the common fuel <br /> aromatics benzene, toluene, methyl benzene, xylenes (Reisinger, et at , 1986), <br /> 1 <br />
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