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Environmental Health - Public
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EHD Program Facility Records by Street Name
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LOWER SACRAMENTO
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7910
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3500 - Local Oversight Program
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PR0545441
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Last modified
3/9/2020 6:21:27 PM
Creation date
3/9/2020 2:39:21 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
RECORD_ID
PR0545441
PE
3528
FACILITY_ID
FA0003733
FACILITY_NAME
NORTH SIDE SHELL
STREET_NUMBER
7910
STREET_NAME
LOWER SACRAMENTO
STREET_TYPE
RD
City
STOCKTON
Zip
95210
APN
07949006
CURRENT_STATUS
02
SITE_LOCATION
7910 LOWER SACRAMENTO RD
P_LOCATION
01
QC Status
Approved
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dog information will be utilized in the selection of this grain size. The gravel pack will be selected such <br /> that it will permit the development of a zone of higher hydraulic conductivity adjacent to the well <br /> } screen but will not allow piping of the finer-grained formation into the well bore. The slot size of <br /> +" the well screen will be selected such that it will retain a minimum of 90 percent of the gravel pack <br /> material. <br /> r.. <br /> 1 Monitorip Well D vel m nt <br /> If monitoring wells are installed, each monitoring well will be developed after construction with a <br /> w 1.75-inch-diameter manual pump until the water produced is relatively sediment free or until <br /> measurements of pH, specific conductance, and temperature stabilize. If the well is pumped dry <br /> a. during the development process, recharged rates will be recorded. No water or chemicals will be <br /> introduced into the monitoring wells during well development. All developed water will be placed <br /> in drums on site for later disposal. <br /> ' I& Ground Water Sampling <br /> A minimum of 24 hours following well development, and after water levels have been allowed to <br /> stabilize in the well, three to five wetted casing volumes of liquid will be removed from each well <br /> by bailing with a laboratory-cleaned teflon bailer. Measurements of pH, specific conductance, and <br /> temperature will be made at regular intervals during this procedure. Removal of Iiquid from each <br /> well will continue until the measurement pH,specific conductance, and temperature have stabilized. <br /> 6. A liquid sample will then be collected from each well with a laboratory-cleaned, dedicated teflon <br /> bailer. Each sample will be appropriately labeled and stored on ice from the time of collection <br /> through the time of delivery to the laboratory. Ground water samples will be transported to the <br /> laboratory and analyzed within the EPA-specified holding times for the requested analyses. <br /> 1.7 Petroleum Product <br /> If free petroleum product is present in a well, the thickness of the product layer will be measured <br /> 60 by collecting a sample in a transparent teflon bailer with a check valve at the bottom or by <br /> measurement using appropriate fluid-level sounding equipment. The sample will be transferred to <br /> an appropriate sample container and subsequently submitted for fuel fingerprint analysis at the <br /> laboratory. <br /> 2.0 ANALYTICAL PROCEDURES <br /> All soil samples submitted to the laboratory will be analyzed by EPA Method 8020 for benzene, <br /> toluene ethylbenzene, xylene, (BTEX) and by EPA Method 8015 for total purgeable petroleum <br /> hydrocarbons (TPPH). All ground water samples submitted to the laboratory will be analyzed by <br /> ' EPA Method 602 for BTEX and by EPA Method 8015 for TPPH. Total lead will be analyzed in soil <br /> L. and ground water samples by EPA Methods 6010. <br /> ONE <br /> W <br />
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