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ARCHIVED REPORTS XR0000247
Environmental Health - Public
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3500 - Local Oversight Program
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PR0543431
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ARCHIVED REPORTS XR0000247
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Last modified
2/5/2019 2:39:28 PM
Creation date
2/5/2019 1:10:37 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0000247
RECORD_ID
PR0543431
PE
3528
FACILITY_ID
FA0003683
FACILITY_NAME
Caltrans-Stockton
STREET_NUMBER
1604
Direction
S
STREET_NAME
B
STREET_TYPE
St
City
Stockton
Zip
95206
APN
171-090-08
CURRENT_STATUS
02
SITE_LOCATION
1604 S B St
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
Scanner
WNg
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EHD - Public
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SECTION 5.0 RESULTS AND DISCUSSIONS <br /> 5.2 HISTORICAL TRENDS OF PETROLEUM HYDROCARBONS IN SUBSURFACE <br /> 5.2.1 Soil Trends <br /> Based on soil sample results summarized in Tables 3-1 and 3-2 for previous subsurface <br /> investigations, the majority of the petroleum hydrocarbons appear to be in the vadose zone The <br /> vadose zone soil plume was observed to be bounded by borings SB-1, SB-2, MW-1, MW-2, <br /> MW-3, and VW-1 (GEOCON, 1996b) The volume of petroleum-hydrocarbon impacted soil was <br /> estimated by GEOCON to be approximately 1,150 cubic meters (m) (1,500 cubic yards [yd']) <br /> GEOCON did not estimate the mass of petroleum hydrocarbons in soil URSGWC has estimated <br /> the masses of TPH-g and benzene in soil based on soil analytical data reported by Alton and <br /> GEOCON A discussion of the estimated masses of TPH-g and benzene in sobs is included in <br /> Section 5 4 <br /> 5.2.2 Groundwater Trends <br /> The historical results of petroleum hydrocarbon in groundwater through Third Quarter 1999 are <br /> presented in Table 3-3 Historical concentration trends in groundwater for four wells (MW-1, <br /> MW-6, VW-1, and VW-2) are presented on Figure 5-4 Concentrations below the laboratory <br />�* detection limit were plotted as half of the detection limit The figures depict significant decreases <br /> in both TPH-g and benzene concentrations with time along with the increase in groundwater <br /> elevations with time MTBE concentrations have fluctuated in the four wells depicted on Figure <br /> 5-4, however, the magnitude has been similar since 1997 <br /> 5.3 SLUG TEST RESULTS <br /> Slug tests were performed in wells MW-1, MW-6, and MW-11 at Stockton Yard Table 5-3 <br /> provides a summary of the transmissivities and hydraulic conductivities that were estimated for <br /> the respective wells for both the falling head and rising head slug tests The results were slightly <br /> higher for the rising head test as compared to the failing head test The estimated hydraulic <br /> conductivities ranged from 1 3x10"2 to 7 6x10"3 centimeters/second (cm/s) The transmissivity, <br /> calculated assuming an aquifer thickness equal to the well screen length, ranged from 4 1 to <br /> 9 5 square centimeters/second (cm'/s) These results suggest a groundwater velocity ranging <br /> from 5 4 x 10' to 9 2 x 10 cm/s, or 17 to 29 meters/year (56 to 95 feet/year), based on the slug <br /> test data and the April 1999 groundwater gradient calculated by PSI using the gradient depicted <br /> on Figure 5-2, the groundwater velocity ranges from 0 2x10'5 cm/s, or 5 to S meters/year (16 to <br /> 27 feet/year) These hydraulic conductivity estimates are indicative of a soil type consistent with <br /> sand/silty sand However, the hydraulic conductivity estimated by slug testing may be <br /> . overestimated due to the influence of the surrounding sand pack on the rate of rise and fall of the <br /> 51PRC UI040100041SYYARDMAINTYARD5A.DOC 5-3 URS Greiner Woodward Clyde <br />
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