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SITE INFORMATION AND CORRESPONDENCE_2008-2015
Environmental Health - Public
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SITE INFORMATION AND CORRESPONDENCE_2008-2015
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Last modified
3/31/2020 3:00:55 PM
Creation date
3/31/2020 2:41:07 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
2008-2015
RECORD_ID
PR0506203
PE
2960
FACILITY_ID
FA0007271
FACILITY_NAME
LINCOLN CNTR ENV REMEDIATION TRUST
STREET_NUMBER
0
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
CURRENT_STATUS
01
SITE_LOCATION
PACIFIC AVE
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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8 LFR <br /> LFR proposes to implement the laboratory testing wells ERD-3 and ERD-18 because of their <br /> relatively elevated hazardous substance concentrations (1,300 and 1,720 micrograms per liter, <br /> respectively), their different placements vertically (ERD-18 is in the upper A-zone while ERD-3 is <br /> in the lower A-zone), their low resistance to flow during injections (indicating good <br /> communication with the surrounding aquifer), and their positions north (ERD-18) and south (ERD- <br /> 3) of the center of the array of injection wells. The two wells will be sampled semiannually and <br /> analyzed for: <br /> • VOCs and end products (e.g., ethene and ethane) <br /> • biogeochemical indicators of redox conditions (e.g., DO, ORP, nitrate, manganese, sulfate, <br /> iron (II), and methane) <br /> • organic substrate (as TOC) <br /> RWQCB Comment 2: <br /> The assumption has been made that based on the increased daughter products detected in MW- <br /> 108A, dehalococcoides populations must also have increased in MW-1084 and in the ERD Barrier <br /> Area in general. Dehalococcoides are the microbes responsible for driving ERD to innocuous end <br /> products. Staff concurs that it was a good idea to have performed this analysis on samples from the <br /> five wells listed on page 9. Please propose a sampling frequency for adding this analysis in those <br /> well to the monitoring program. Confirmation of dehlococcoides should be established, not <br /> assumed. <br /> Response 2: <br /> Laboratory analysis for the genus dehalococcoides was conducted voluntarily outside the current <br /> monitoring program as an additional line of evidence that the bacteria capable of mediating the <br /> complete dechlorination of tetrachloroethene (PCE) were present at the Site. As discussed in the <br /> Injection Completion Report, laboratory results confirmed that dehalococcoides is present in <br /> sufficient numbers to be detected by the microbial test in B-zone well MW-20513; however, <br /> dehalococcoides is not detected above the reporting limit in the other four wells tested, namely <br /> wells MW-108A, MW-122A-U, MW124A-L, and MW-21413. As discussed during the June 16, <br /> 2008 conference call, the four aforementioned wells will be sampled semiannually for one year to <br /> confirm that dehalococcoides is present in each well. It is important to note that the objective of <br /> this testing is to confirm that the microorganism is present, but not to monitor microbial population <br /> size or changes in microbial population over time. Therefore, testing for dehalococcoides will stop <br /> after two sampling events or after only one sampling event if its presence is confirmed by a <br /> laboratory result above the laboratory reporting limit. <br /> Itr-Response to RWQCR-Lincoln-JU108.06750.doc:LMT 3 <br />
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