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ARCHIVED REPORTS_XR0010358
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0543041
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ARCHIVED REPORTS_XR0010358
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Last modified
5/18/2020 3:14:47 PM
Creation date
5/18/2020 2:53:57 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0010358
RECORD_ID
PR0543041
PE
2960
FACILITY_ID
FA0024604
FACILITY_NAME
HUMAN SERVICES AGENCY
STREET_NUMBER
145
Direction
S
STREET_NAME
SUTTER
STREET_TYPE
ST
City
STOCKTON
Zip
95202
APN
14912016
CURRENT_STATUS
01
SITE_LOCATION
145 S SUTTER ST
P_LOCATION
01
QC Status
Approved
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LSauers
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EHD - Public
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7ontinue <br /> SGYENS.t016LL M75 <br /> decay rates of benzene, it is estimated 12 years ould be required to attain cleanup <br /> levels Groundwater monitoring woulduring t period <br /> The program BIOSCREEN was used te movement and biodegradation of benzene <br /> in the zone 4 aquifer under the influence of advection, dispersion, sorption and biodegradation. <br /> Benzene was used as the modeled chemical because it is the most soluble and mobile of the <br /> BTEX compounds. BIOSCREEN uses the Domenico (1987) analytical solute transport equation <br /> model to predict chemical concentrations. The results of modeling are presented in Appendix <br /> A The purpose of the modeling was to 1) predict the future extent and concentration of a <br /> dissolved contaminant plume, 2) to assess the possible risk to potential downgradient receptors <br /> 3) and to provide technical support for intrinsic remediation <br />' Benzene concentrationr <br /> p edications were made for 10, 20 and 30 years after a petroleum release <br /> The results of modeling indicate that the dissolved BTEX groundwater plume will not extend <br /> more than 300 feet beyond the source area and that it is very unlikely that the plume will pose <br /> a risk to potential downgradient receptors <br /> Evaluation <br /> Effectiveness This alternative would be effective in protecting human health and the <br /> environment There are no human receptors nearby who would be exposed to the contaminated <br /> groundwater during the period it is undergoing remediation There are no surface water bodies <br /> nearby that could be impacted by this groundwater Groundwater in this area moves slowly (6 7 <br /> feet per year) and as a result, is not likely to impact distant receptors The effectiveness of this <br /> alternative will be ensured by monitoring If monitoring shows this alternative to be ineffective, <br /> additional remediation options could be employed without much risk due to the slow <br /> groundwater migration rates. <br /> The BTEX compounds comprise one of the most optimum contaminant classes for <br /> bioremediation BTEX degrades readily under correct conditions; these favorable conditions are <br /> present at the site <br /> Implementabdity This alternative would be the least intrusive for this very high traffic (both <br /> vehicle and pedestrian) area with access constraints This alternative would be easy to <br /> implement and is anticipated to require only two more wells and no other construction which <br /> would impact local services Implementation would require development of a long-term <br /> monitoring program and performance of 5-year reviews Groundwater sampling and monitoring <br /> of the contaminant levels in the groundwater would be conducted for an approximate 10- to 12- <br /> year period The 5-year reviews would examine the current plume location and determine if any <br /> new downgradient receptors are present which may require an alternate course of action. <br /> Cost For cost estimation purposes 10 years of groundwater monitoring was assumed The <br /> overall cost of this option was estimated to be $273,000 Costs are shown in Appendix B, Table <br /> 2 <br /> UPROJECTS\SAN10Q W WA=ONPL 38 <br />
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