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ARCHIVED REPORTS_XR0012617
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545652
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ARCHIVED REPORTS_XR0012617
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Last modified
7/20/2020 10:42:49 AM
Creation date
5/6/2020 12:25:55 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012617
RECORD_ID
PR0545652
PE
3528
FACILITY_ID
FA0003638
FACILITY_NAME
JEMCO VENETIAN CARDLOCK
STREET_NUMBER
4555
Direction
N
STREET_NAME
PERSHING
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
APN
11017001
CURRENT_STATUS
02
SITE_LOCATION
4555 N PERSHING AVE
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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£� 011, �. <br /> v V- <br /> i <br /> and for BTEX by EPA Method 8020. Table 2 summarizes the analytical results of groundwater <br /> sampling from September 1986 to May 199I. Table 3 summarizes the well gauging and LPPH <br /> monitoring from August 1987 to May 1991. <br /> 2.6 BAIL TESTS <br /> In October 1988,EA conducted several bail tests in the wells on the site in anticipation of their <br /> use as recovery wells(EA 1989). Four wells (MW 1,MW2,MW3,and MW6)were tested. The <br /> tests were accomplished by quickly extracting 2.1 gallons of water using a PVC bailer and allow- <br /> ing the aquifer to rebound to its initial water level. <br /> Recovery data were monitored and collected with a HERMIT Model SE 100013 Environmental <br /> Data Logger and a 10-psi pressure transducer. The transmissivity value for each test was esti- <br /> mated using the Well Hydraulic Interpretation Program(WHIZ') of Hydro-Geo Chem.,Inc. The <br /> average values of transmissivity(T)ranged from 10.9 (MW6) to 80 ft2/day (MW3) (Table 4); <br /> values of hydraulic conductivity calculated front these values ranged from about 3 ft/day(MW6) <br /> to 28 ft/day(MW3). The results obtained from wells MW3 and MW6 were probably affected by <br /> the presence of LPPI-I in those wells: a decrease in transmissivity in three consecutive tests of <br /> MW3,from 80 to 12 ft2/day,might have been caused by fuel replacing the,water in the pores of <br /> the soil and gravel pack around the well when bailing lowered the water level, decreasing the <br /> ability of soil and sand to conduct water. In addition, screen slots covered with petroleum <br /> hydrocarbons can considerably decrease a well's efficiency and affect the results of the test. <br /> Values of transmissivity and hydraulic conductivity derived from these tests are in Table 4. <br /> On 3I May 1990 several bail tests were conducted in the new monitoring/recovery wells to <br /> determine hydraulic properties of this deeper saturated zone and potential capacity of the wells. <br /> Bail test results are presented in Table 4. <br /> 2.7 PUMPING AND INJECTION TESTS <br /> To better determine the hydraulic properties of the saturated zone under former Exxon RS <br /> 7-3142 and to more accurately size the treatment system,EA conducted pumping tests in wells <br /> RW 1 and RW2, <br /> On 18 September 1990 a preliminary pump test was conducted in well RW 1 to establish a sus- <br /> tainable pumping rate for this well. The test lasted about 1.2 hours and determined that a pump- <br /> ing rate of 3.6 gpm should be used for the actual pump test. Wells RW2 and RW3 were moni- <br /> tored during the preliminary test, but no significant drawdown (move than 0.01 feet) was ob- <br /> served. The total drawdown observed in well RW 1 during this initial test was 6.26 feet. <br /> On 19 September,a long-term pumping test was conducted in well RWI; a submersible pump <br /> pumped from the well to a temporary storage tank. The test was started at 0804 hours, after all <br /> c62/..Q7394Vj-91A. 4 <br />
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