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SITE INFORMATION AND CORRESPONDENCE
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EIGHT MILE
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2900 - Site Mitigation Program
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PR0518132
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
7/10/2019 1:23:26 PM
Creation date
7/10/2019 11:39:29 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0518132
PE
2960
FACILITY_ID
FA0013716
FACILITY_NAME
H & H MARINA
STREET_NUMBER
15135
STREET_NAME
EIGHT MILE
STREET_TYPE
RD
City
STOCKTON
Zip
95219
APN
06908021
CURRENT_STATUS
01
SITE_LOCATION
15135 EIGHT MILE RD
P_LOCATION
01
QC Status
Approved
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EHD - Public
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Mr. Andrew Smith • - 2 - • 4 June 2004 <br /> a. The SCM does not include the possibility of discharges during refilling of the <br /> AGTs. <br /> b. The SCM does not adequately explain how 190,000 micrograms per liter (µg/1) of <br /> methyl tertiary butyl ether (MTBE) in monitoring well MW-2 could be from <br /> USTs removed in October 1991. Although MTBE was added to gasoline in 1991, <br /> only two to 11 percent was added to gasoline prior to 1991. The high MTBE <br /> concentrations detected at the site are likely due to the higher percentage of <br /> MTBE added to gasoline,which started in late 1991 as opposed to the low <br /> percentage required when the USTs were active prior to October 1991. <br /> C. The SCM does not include monitoring well MW-4, which is downgradient of the <br /> USTs and has detections of MTBE ranging from 1.4 to 48 µg/1, in the cross- <br /> sections provided in the Report. Based on the concentrations of MTBE in MW-2 <br /> and MW-3, which range from 7.9 to 190,000µg/1, the concentrations in MW-4 <br /> would be higher if the pollution originated from the USTs. H&H Marina <br /> previously argued that the retaining wall diverted the pollution to the south of the <br /> wall and around MW-4, yet the cross-section figures focus downgradient of the <br /> center point of the wall instead of the area where hydrocarbon pollution could <br /> have potentially been diverted. <br /> d. The SCM does not adequately explain why the highest concentrations in <br /> groundwater are detected from samples collected near the AGTs. Furthermore, <br /> the cross-sections showing concentrations of constituents of concern in <br /> groundwater do not show the core of pollutants leading or trailing from the former <br /> USTs. <br /> e. Concentrations of MTBE and total petroleum hydrocarbons (TPH) as gasoline <br /> continue to fluctuate in accordance with groundwater elevations. However, the <br /> concentrations are not decreasing as would be expected from a release more than <br /> 12 years ago. The SCM needs to explain why concentrations in groundwater are <br /> not decreasing and why the soils near the former USTs "may have flushed <br /> MTBE"but not flushed the pollution for the other areas of the site. <br /> f. The SCM does not include a discussion of when the AGTs were installed, how the <br /> AGTs are constructed(each tank has three compartments), the capacity of the <br /> AGTs and each compartment of the tank,what each compartment of the tank <br /> contains, the estimated refilling of the AGTs (gasoline versus diesel), how the <br /> tanks are refilled, when MTBE-free fuels were first utilized at the site, and the <br /> schematics for the piping from the AGTs to the dispenser(s). <br /> g. The SCM points out a discrepancy between the detections of gasoline versus <br /> diesel, however, there is insufficient TPH as diesel data to make a comparison. <br />
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