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3500 - Local Oversight Program
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PR0544466
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/16/2019 3:38:58 PM
Creation date
5/16/2019 2:51:00 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0544466
PE
3528
FACILITY_ID
FA0005303
FACILITY_NAME
HOLT OF CALIFORNIA
STREET_NUMBER
1521
Direction
W
STREET_NAME
CHARTER
STREET_TYPE
WAY
City
STOCKTON
Zip
95206
APN
16337015
CURRENT_STATUS
02
SITE_LOCATION
1521 W CHARTER WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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t <br /> ti <br /> Soi� R�ediet�en l►1_ ta�net',�ytg6 <br /> saeh of the 5 soil re-mediation alternatives have+ been compared and <br /> ranked against one another for each of the nine qualifying <br /> criterion. Alternatives are given 1 - 3 prints based upon their <br /> ability to most criteria objectivcr. One point is given for <br /> alternatives tlsat meet criteria least effectivdly, three points ! <br /> given for alternatives that meet criteria most effectively. The <br /> relative rankings are shown on Table 2 along with n Cumulati'/e <br /> "score" for each approach. <br /> The scoring rationale for each criterion sa discussed below. <br /> Criterion 1.: The excavation approaches (1 and 2) provido a lower <br /> level of protection for human health arA the environment and also <br /> represent a potential threat of further groundwater contz:mAnstion <br /> since the majority of soil hydrocarbons are at the capillary <br /> fringe. Generally the prrcass of excavation AA8,11ts in Truman <br /> exposure to hydrocarbon compounds due to direct volatilization ani <br /> contact with soils and dist. in situ removal .f hydrocarbons from <br /> the affected soil area using vapor extraction tez-hniyues or <br /> bioremediation (3 and 5) would have a slightly higher level of <br /> protection for the -environment. Neither of these twchniques 1 <br /> exposes humans to direct volitization of hydrocarbon3 however both � <br /> of these approaches are limited by the extremely low soil <br /> permeability to both vapor and water. Capping of tho soils with ++ <br /> los pornwabili`y cover is an affective mothod for limiting the i <br /> ly <br /> migration of hydrocarbons in the underlying soils. if p atururaall <br /> maintained the cap would isolate the impacted soils and natural <br /> chsmic•sl and biologic degradation processes would further mitigate <br /> the potential impauts. <br /> Criterion 2. Alternatives 1, 3, and 5 will each result in <br /> reduction of the toxicity, mobility and volume of contaminants <br /> although, as mention above in-situ treatment will have limited <br /> efficacy. Altftrr.utives 2 and 4 would both reduce mobil:'ty but <br /> would z-oly on nature: degradation processor to reduce contamisiant <br /> toxicity and volume. <br /> Criterion 3. : All five approaches can be implemented within <br /> regulatory guidelines. <br /> Criterion 4. : Conservative estimates for both capital and <br /> oper-ating costs for sail remediation indicate that excavation would <br /> be the most costly of these alternatives. This dvas not include t <br /> certain costa associated with excavation which are Presently <br /> unknown including, the lose of use, the cost of removing and , <br /> temporarily storing clean soil which is removed, and the threat to <br /> the structural integrity of buildings on-site. in-situ treatment <br /> methods due to permeability limitAtions would be more costly than E <br /> a capping approach. F <br /> 3 <br /> "c.4o3.WF <br />
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