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Environmental Health - Public
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3500 - Local Oversight Program
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PR0544305
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
4/3/2019 3:00:50 PM
Creation date
4/3/2019 2:46:36 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0544305
PE
3528
FACILITY_ID
FA0003736
FACILITY_NAME
CLIPPER GROUP
STREET_NUMBER
3730
Direction
E
STREET_NAME
MUNFORD
STREET_TYPE
AVE
City
STOCKTON
Zip
95205
APN
17956010
CURRENT_STATUS
02
SITE_LOCATION
3730 E MUNFORD AVE
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
Scanner
WNg
Tags
EHD - Public
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lwftr/ 1%01-1 <br /> Ms. Linda Turkatte <br /> December 14, 1995 <br /> Page 3 <br /> (Spring, 1986) to more than 75 feet below grade (April, 1992). The most recently recorded depth to <br /> water was approximately 72.5 feet below grade (May, 1995). <br /> Figure 3 also shows the estimated extent of residual hydrocarbon contamination. Based upon analytical <br /> results of soil samples collected during drilling of well MW 1, it appears that residual gasoline <br /> constituents associated with the line leak existed only in clay soils between approximately 18 and 50 <br /> below grade. Based upon the literature, one can estimate transverse dispersion of contaminants to be ' <br /> approximately 1/8 that of longitudinal dispersion (Illinois State Water Survey, Bulletin 65, 1981). <br /> Therefore, the estimated maximum extent of impacted soil in 1986 was a zone roughly equivalent to <br /> a vertical cylinder 32 feet tall (between depths of 18 and 50 feet) by 11 feet in diameter in the vicinity <br /> of well MW L Based on this configuration, approximately 115 cubic yards of soil had been impacted <br /> by approximately 0.18 pounds (0.025 gallons) of benzene. A standard calculation sheet is included in <br /> Attachment B. Based upon analytical results, toluene, ethylbenzene, and xylenes were present at <br /> slightly smaller masses. However, no TPHG was detected in any samples. <br /> Natural in-situ biodegradation of hydrocarbon constituents over time is widely documented in the <br /> literature with the rate of decay limited by the available oxygen (Borden and Bedient, 1986). Decay <br /> constants have been determined at laboratory and field scales for certain gasoline constituents, including <br /> benzene. Benzene decay constant values from numerous independent studies reported average values <br /> ranging from 0.35% to 4.0% per day ( Howard and others, 1991). <br /> In order to predict the expected concentration at a given time, we can extrapolate from a known <br /> concentration using the following equation from the law of exponential change: <br /> Y = Yoe <br /> where yo is the original concentration, In a equals 1, k is the degradation rate (negative number for <br /> decreasing progression), and t is the elapsed time. <br /> For soil, we seek the value of t at which <br /> Yoe = 0.0056yo, <br /> because this will be the time when the concentration will be at the detection limit (the ratio of the <br /> detection limit for benzene in soil [0.005 ppm] to the initial maximum concentration of benzene in soil <br /> [0.89 ppm] is 0.0056). The Yo's cancel in this equation to leave <br /> e't = 0.0056, <br /> groundze\hendrix\phs1295.jp1 <br />
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