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ARCHIVED REPORTS_XR0010194
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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SONORA
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3500 - Local Oversight Program
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PR0545695
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ARCHIVED REPORTS_XR0010194
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Last modified
5/27/2020 5:36:37 PM
Creation date
5/27/2020 4:31:51 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0010194
RECORD_ID
PR0545695
PE
3528
FACILITY_ID
FA0003877
FACILITY_NAME
CITY OF STOCKTON FIRE STATION #2
STREET_NUMBER
110
Direction
W
STREET_NAME
SONORA
STREET_TYPE
ST
City
STOCKTON
Zip
95203
APN
13731025
CURRENT_STATUS
02
SITE_LOCATION
110 W SONORA ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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A S S O C I A T E S I N C <br /> possible migration of petroleum hydrocarbons in soil caused by surface water flushing <br /> contaminants into the groundwater is minimal due to the asphalt and concrete surface on site <br />' The groundwater gradient direction has generally been towards the east with a magnitude of <br /> 0 002 ft/ft which makes it unlikely that the plume will migrate off site in the short term <br /> ♦ Cntenon 3 <br /> This alternative would not immediately remediate soil or groundwater to levels acceptable to <br /> regulatory agencies Natural degradation of residual hydrocarbons would occur over time but <br />' generally occurs at slower rates in lower permeabihty soils such as the silts and clays found <br /> beneath the site <br /> ♦ Cntenon 4 <br /> Additional costs for implementing this alternative are related to the costs associated with the <br />' continued monitoring to ensure natural attenuation is occurring and the permitting and <br /> destruction of existing wells at project completion The cost of this alternative is estimated to <br /> be about $11,000 per year for monitoring, $7,000 to $15,000 for enhancing biodegradation <br />' with introduction of oxygen if warranted, and$15,000 for a closure plan and well destruction <br /> ♦ Cntenon 5 <br /> This alternative is effective in minimizing the health-based risks in the short term Exposure to <br /> humans by contamination releases to the air due to dust, or through ingestion or dermal <br /> exposure to impacted soil or groundwater is minimal during groundwater monitoring and well <br /> destruction activities but is otherwise nonexistent <br /> ♦ Cntenon 6 <br /> The long-term effectiveness of this alternative may be unacceptable This alternative would <br /> reduce the toxicity and volume of the contaminants in the soil by natural biodegradation, but <br />' the rate of reduction is not known but is likely poor The possibility for health-based risks in <br /> the long term is low to moderate as long as the site remains surfaced and exposure of humans <br /> to impacted soil does not occur during any type of site excavation or structure demolition <br />' activities With a poor rate of reduction, impacted groundwater may migrate off-site in the <br /> long term <br /> ♦ Cntenon 7 <br /> Of all the alternatives the passive remediation approach is the easiest to implement <br /> Groundwater monitoring activities would continue to ensure natural attenuation is occurring, <br />' but monitoring may continue for an extended period of time When concentrations have <br /> reduced to levels acceptable to the regulatory agencies or an apparent decreasing trend is <br /> evident, a closure plan will be submitted Well destruction permits would be obtained from the <br />' appropriate agencies and the wells would be destroyed by overdnlling the well casing and sand <br /> • pack and pressure grouting the boring to the surface when concentrations have been reduced <br /> to an acceptable level <br /> W 162574 OlVilot-fa report doc 11 <br />
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