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ARCHIVED REPORTS XR0007281
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0518132
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ARCHIVED REPORTS XR0007281
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Last modified
7/10/2019 7:05:43 PM
Creation date
7/10/2019 11:54:05 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007281
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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. 06 March 2002 <br /> AGE-NC Project No 01-0865 <br /> Page 7of9 <br /> AGE believes the available data may actually represent a partitioned plume of impacted ground <br /> water It is well known that the various fuel components have differing migration rates in ground <br /> water,that MTBE has the most rapid migration rate due to its low adsorption potential for inorganic <br /> minerals, and that the BTEX compounds migration rates are less than MTBE Benzene commonly <br /> has the most rapid migration rate for a hydrocarbon, and often is the first compound detected at the <br /> leading edge of a dissolved hydrocarbon plume, xylenes typically are the slowest moving aromatic <br /> compound and lag behind near the release point The monitoring data from MW-4,near the former <br /> UST site and the only well consistently yielding benzene and xylenes,may actually demonstrate the <br /> principal The highest benzene concentrations in the well were encountered during the period from <br /> Mach 1998 to June 1999,the highest xylenes concentrations have been detected since approximately <br /> September 2000 to present (December 2001) Toluene concentrations have always been low or <br /> undetectable, ethylbenzene may have had peak concentrations from December 1997 to September <br /> 1999, slightly ahead of the inferred benzene peak concentration period <br /> The aliphatic hydrocarbons making up the bulk of TPH-g have varying migration rates that depend <br /> on chain-size and configuration,but are generally slower than benzene The eastern part of the plume <br /> is in a flat area adjacent to agricultural land, application of fertilizers to the agricultural land may <br /> have stimulated bacterial growth which has in turn selectively degraded any volatile aromatic <br /> compounds, especially benzene, that reached the area <br /> The former UST pit was located on the levee, in an elevated position relative to the ASTs and fields <br /> located toward the east, and slightly elevated relative to the water body on the west Ground water <br /> flow has been toward the east, at a higher gradient in the area near the levee and lower gradient <br /> toward the east <br /> Mapping the dissolved fuel component concentrations shows high MTBE and TPH-g concentrations <br /> east of the AST site and elevated BTEX concentrations in the former UST area Although the data <br /> set is sparse (three ground water sample points), dissolved benzene and total xylenes were present <br /> in samples collected from the UST area(B7) extending to the southeast of the AST area(DP-5) In <br /> this area where the aromatics are present, the highest benzene concentration was detected in DP-5 <br /> (the leading aromatic hydrocarbon plume9), the highest total xylenes concentration was in MW-4 <br /> (trailing plume?) Figures 7 and 8 illustrate the approximate extent of dissolved benzene and xylenes, <br /> respectively, in shallow ground water <br /> The core of high MTBE concentrations hes toward the ease and northeast of the dissolved aromatic <br /> compounds plume (leading edge?) Although the data set is not robust, AGE believes the <br /> contaminant distribution could be interpreted as a partitioned plume of fuel constituents, with the <br /> MTBE plume nearly completely detached from the source area The unusual aspect of the dissolved <br /> contaminant distribution is the high TPH-g concentrations also located northeast and east of the <br /> dissolved aromatic hydrocarbon plume,similar to the MTBE distribution may be related to selective <br /> bacterial degradation of aromatic hydrocarbons, as noted above <br />
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