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FIELD DOCUMENTS_CASE 2
Environmental Health - Public
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3500 - Local Oversight Program
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FIELD DOCUMENTS_CASE 2
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Last modified
5/12/2020 3:46:46 PM
Creation date
5/12/2020 2:57:33 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
FIELD DOCUMENTS
FileName_PostFix
CASE 2
RECORD_ID
PR0545660
PE
3528
FACILITY_ID
FA0003909
FACILITY_NAME
PORT OF STOCKTON
STREET_NUMBER
2201
Direction
W
STREET_NAME
WASHINGTON
STREET_TYPE
ST
City
STOCKTON
Zip
95203
APN
14503001
CURRENT_STATUS
02
SITE_LOCATION
2201 W WASHINGTON ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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C <br /> maximum depth explored at the site..Soils encountered near the former dispenser area(borings B5- <br /> 4 and B5-5) comprise mostly clay. A 1- to 2-foot thick bed of sand occurs beneath the former <br /> dispenser area at about 17 feet bgs. <br /> Data from nearby studies indicate that the current depth to groundwater in the vicinity ranges from <br /> about 5 to 10 feet bgs(SPGC, 1998, and EMCON, 1998). Seasonal fluctuations in the water table <br /> appear to range from about 3 to 5 feet,-with some as much as 6 to 9 feet. Tank removal inspection <br /> records for this and other Port sites (dating back to 1987) indicate that no groundwater was <br /> encountered during excavation of tanks or soil resampling to a depth of as much as 16 feet bgs. <br /> Water levels in this area have risen as much as 8 feet since 1994, 2 to 3 feet of which appear to be <br /> attributable to the heavy and prolonged E1 Nino rainfall events of last winter. The static water level <br /> in the borings emplaced near the former USTs(borings B5-1 to-3)was about 9 feet bgs on August <br /> 5,while water levels in the borings emplaced near the former dispenser area(borings B54 and-5) <br /> were about 11 feet bgs. Based on nearby studies(SPGC, 1998, and EMCON, 1998)groundwater <br /> flow directions in the vicinity appear to be variable,ranging from west northwest to east southeast. <br /> Flow direction changes may be due to tidal influences produced by the deep water channel to the <br /> north and the San Joaquin River to the west and southwest of the Port complex. <br /> 3.0 SUMMARY OF ACTPVfrlES <br /> Activities during this investigation included installation and development of monitoring wells, <br /> sampling of monitoring wells, elevation survey of monitoring wells, and completion of a survey of <br /> nearby supply wells that could be affected if contamination were to nnigrate off site. All activities <br /> were conducted in general accordance with procedures described in the work plan. <br /> 3.1 INSTALLATION OF MONITORING WELLS <br /> Monitoring well installation services were provided by West Hazmat Drilling Corporation (West <br /> Hazmat)of Rancho Cordova, California; a C-57 licensed drilling contractor, and geologic logging <br /> of the borings was provided by Geomatrix Consultants, Inc. of Fresno, California. The borings <br /> were drilled using a CME-75 drill rig.:Prior to drilling operations,Underground Services Alert was i <br /> contacted and underground utilities marked by respective utility companies. In addition,the Port's <br /> tmaintenance department was notified and they examined the site for underground utilities. West <br /> Hazmat obtained an approved monitoring well installation permit from PHS/EHD(Appendix A)and <br /> monitoring wells were constructed on May 17, 1999. <br /> Wells MW5-1 and MW5-2 are located within 3 feet of previous borings B 5-1 and B5-5;respectively <br /> L (Figure 2). No soil samples were collected from the borings for these wells ,because of their <br /> proximity to previous borings, from which samples were collected to depths of 26 and 20 feet <br /> 4 PHILIP P. Ross <br /> �s <br /> s R.G. <br />
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