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ARCHIVED REPORTS XR0010889
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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ELKHORN
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1050
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2900 - Site Mitigation Program
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PR0505234
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ARCHIVED REPORTS XR0010889
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Last modified
8/1/2019 3:25:51 PM
Creation date
8/1/2019 2:23:45 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0010889
RECORD_ID
PR0505234
PE
2951
FACILITY_ID
FA0001103
FACILITY_NAME
Elkhorn Golf Club
STREET_NUMBER
1050
STREET_NAME
ELKHORN
STREET_TYPE
DR
City
STOCKTON
Zip
95209
CURRENT_STATUS
02
SITE_LOCATION
1050 ELKHORN DR
P_LOCATION
99
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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f <br /> r- 27 June 1996 <br /> AGE-NC Project No. 95-0118 <br /> -; Page 15 of 23 <br /> 7.3.3. INOCULATION WELLS <br /> The effective radius of influence of inoculation wells is typically 15 feet. Existing extraction wells <br /> could be used for inoculation; however additional wells might have to be installed. Temporary <br /> inoculation points could also be utilized. <br /> `.' 7.3.4. MONITORING ACTIVITIES <br /> -`3 After inoculation,the inoculation wells and ground water monitoring wells should be monitored for <br /> -' several months by periodic field measurements of organic vapors, carbon dioxide, and oxygen. <br /> Ground water samples should be collected and analyzed for petroleum hydrocarbon concentrations <br /> to monitor remediation progress. Quarterly or semi-annual monitoring activities should include the <br /> installation of soil borings to collect soil samples to monitor bacterial populations, nutrient <br /> availability and the soil remediation progress. If monitoring indicates areas of slow remediation, <br /> additional inoculations may be required. <br /> 7.3.5. DURATION <br /> f <br /> Duration(and cost)are dependent on the volume of soil to be remediated,the number of inoculation <br /> and monitoring wells and inoculation events, the average concentrations of contaminants and <br /> nutrients, and the temperature and permeability of the soil. Theoretically,the volume of soil affected <br /> l-j by the inoculation well should increase rapidly atfirst,then gradually decline as the affected volume <br /> increases and the bacteria encounter decreasing hydrocarbon concentrations toward the margins of <br /> the contaminant plume. In-situ remediation of soil at the Elkhorn site would likely require 6 to 18 <br /> Fa months to reduce hydrocarbon concentrations to acceptable levels. <br /> 7.3.6: FEASIBILITY <br /> ;.._ Results of the rinicrobiological analysis of soil samples (Appendix C) indicate that indigenous <br /> hydrocarbon-degrading bacteria constitute a high proportion of the total microbiological population <br /> at the site,however,the total microbiological population is low. The concentrations of hydrocarbon- <br /> degrading bacteria may be due to the presence of hydrocarbons in the soil providing a food source <br /> for the bacteria. The total colony units (CFUs) of the soil at the site are inadequate for <br /> bioremediation, without inoculation of additional microbes and nutrients. <br /> . i <br /> The low concentrations of nitrogen,both oxidized and reduced, low levels of biologically available <br /> carbon sources and the possible presence of high concentrations of inorganic constituents may have <br /> __J <br />
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