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Environmental Health - Public
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2900 - Site Mitigation Program
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PR0508125
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Last modified
2/24/2020 5:31:15 PM
Creation date
2/24/2020 2:46:03 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0508125
PE
2950
FACILITY_ID
FA0007950
FACILITY_NAME
7 ELEVEN #17647
STREET_NUMBER
1048
Direction
W
STREET_NAME
YOSEMITE
STREET_TYPE
AVE
City
MANTECA
Zip
95336
APN
21903003
CURRENT_STATUS
01
SITE_LOCATION
1048 W YOSEMITE AVE
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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ORC TECHNICAL BULLETIN # 1.2d <br /> Oxygen Release Compound,ORC® <br /> Alaska Field Results <br /> REGENESIS made its first sale to the Anchorage office of Hart-Crowser for <br /> implementation in Homer, Alaska. The site was a utility company property that had <br /> experienced significant hydrocarbon releases from tanks and pipelines. The <br /> dissolved phase was present in a shallow water table characterized by a coarse gravel. <br /> This gave the site a very high flow characteristic - possibly in excess of 40 feet a day <br /> during time of maximum flow. At the other extreme there was a dramatic reduction <br /> in flow throughout the winter freeze cycle. <br /> The unproven nature of the technology led to the suggestion of a pilot test, and at the <br /> same time, afforded the opportunity to make a comparative study against air sparging. <br /> The primary objective was to observe the extent of oxygen dispersivity with some <br /> attention placed on BTEX remediation. The experimental design is presented as <br /> Figure 1, Tables 1 and 2 present the data. Attempts to use air sparging failed because <br /> the sparge points fouled in the high iron environment and there was evidence of <br /> channeling. The results were impressive enough to warrant the purchase and _ <br /> installation of a full Oxygen Barrier. <br /> The layout of the site and the barrier system is presented in Figure 2. Although the <br /> test period was taking place during a period that included the freeze cycle, there was <br /> enough activity and measurements made during the thaw cycles on either side of the <br /> freeze, to show the barrier could reduce BTEX and TPH. <br /> In April, 1995, four months after installation, the following was recorded. At MWP-5 <br /> which is the furthest downgradient point before the road (that Hart-Crowser believes <br /> had yet to be traversed by flow), benzene was reduced from 320 ppb to 9.8 ppb and <br /> total BTEX went from 1361 ppb to 17 ppb. Gasoline range organics went to ND <br /> from 7.4 ppm. Diesel range organics rose from ND to .55 ppm, indicating there may <br /> have actually been a rise in background conditions during the course of operations. <br /> It is useful to note that the barrier was charged with the old, less active ORC-concrete <br /> formulation. The barrier was recharged in July with the current product that is packed <br /> in filter socks. <br /> Another round of data was collected in August about a month after installation. The <br /> results are presented in Figure 3. It is believed that after the thaw the recharge was <br />
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