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SITE INFORMATION AND CORRESPONDENCE_2004-2014
Environmental Health - Public
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SITE INFORMATION AND CORRESPONDENCE_2004-2014
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Last modified
4/7/2020 2:56:47 PM
Creation date
4/7/2020 2:44:28 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
2004-2014
RECORD_ID
PR0506824
PE
2960
FACILITY_ID
FA0007648
FACILITY_NAME
DDRW - SHARPES
STREET_NUMBER
850
Direction
E
STREET_NAME
ROTH
STREET_TYPE
RD
City
LATHROP
Zip
95330
APN
19802001
CURRENT_STATUS
01
SITE_LOCATION
850 E ROTH RD BLDG S-108
P_LOCATION
07
P_DISTRICT
003
QC Status
Approved
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Mr. Maurice Benson <br /> December 15, 2009 <br /> Page 2 <br /> on recommendations in the Treatment Technology Investigation Results Technical <br /> Memorandum. The pilot study location was selected based on groundwater sampling <br /> results conducted as part of a cone penetrometer (CPT) investigation in 2006, 2007, <br /> and 2008. The CPT-investigation detected TCE and its breakdown products, cis-1, 2- <br /> dichloroethene and vinyl chloride present in groundwater in the North Balloon. The CPT <br /> investigation indicated TCE concentrations up to 420 micrograms per liter (Ng/L) were <br /> found in fine-grained layers of the saturated zone between depths of 50 and 70 feet <br /> below ground surface (bgs). Site characterization data showed that large portions of <br /> the TCE concentrations were present in fine-grained layers. <br /> DTSC has reviewed the work plan and has the following comments: <br /> General Comments <br /> 1.) The results from the radius of injection/influence calculations indicate that the <br /> effective ROI in the High Permeability Test Area was lower than the measured <br /> ROI for the Low Permeability Test Area. Specifically, the ROI for the High <br /> Permeability areas measured approximately 8 feet, with low permeability <br /> locations resulting in a 10 foot ROI. The results of the two permeability tests are <br /> counter intuitive in the sense that the lower permeability units should have <br /> demonstrated a lower ROI in comparison to the higher permeability units. The <br /> report does not discuss this discrepancy, leaving one to conclude that perhaps <br /> the High Permeability ROI was solely based on the existing monitoring well (MW) <br /> MW308 and the fact that there may have been under-sampling of the radial <br /> distances away from the injection points, missing the actual distance the oil <br /> substrate traveled under injection. <br /> 2.) EOS concentrations decreased significantly during the 12-month monitoring <br /> event. EOS concentrations decreased to less than 20 mg/L indicating that the <br /> EOS was successful in enhancing the reductive dechlorination of TCE and its <br /> breakdown products. TCE rebound was noted during the 12-month monitoring <br /> event, acknowledging that additional EOS injections may be necessary as TCE <br /> desorbs and diffuses from the tighter grain formations where EOS was <br /> distributed. <br /> 3.) The reductive dechlorination process created by the injection of EOS in the <br /> subsurface appears to have increased concentrations of iron, dissolved <br /> manganese and arsenic in saturated sub-surface, more noticeably in the lower <br /> permeability areas of monitoring wells MW305AB1, and MW306AB. High <br /> permeability areas also had observed increases in iron, manganese and arsenic. <br />
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