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SITE INFORMATION AND CORRESPONDENCE_PRE 2019
Environmental Health - Public
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SITE INFORMATION AND CORRESPONDENCE_PRE 2019
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Last modified
5/11/2021 3:15:46 PM
Creation date
5/11/2021 1:18:05 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3000 – Underground Injection Control Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
PRE 2019
RECORD_ID
PR0009077
PE
2960
FACILITY_ID
FA0004038
FACILITY_NAME
ARCO BULK FACILITY
STREET_NUMBER
2700
Direction
W
STREET_NAME
WASHINGTON
STREET_TYPE
ST
City
STOCKTON
Zip
95206
CURRENT_STATUS
01
SITE_LOCATION
2700 W WASHINGTON ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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Stantec <br /> April 30, 2010 <br /> Page 1 of 3 <br /> Reference: First Quarter 2010 Site Status, Groundwater Monitoring and Remedial Summary Report- <br /> Stockton Terminals Technical Committee Facilities <br /> Appendix C -Stantec Standard Procedures <br /> STANDARD PROCEDURE FOR GROUNDWATER SAMPLING <br /> Depth to Groundwater/SPH Thickness Measurements <br /> Prior to purging each of the wells, the depth to groundwater and thickness of SPH, if present, <br /> within each well casing is measured to the nearest 0.01 foot using either an electronic water <br /> level indicator or an electronic oil-water interface probe. Measurements are taken from a point <br /> of known elevation on the top of each well casing as determined in accordance with previous <br /> surveys. <br /> Groundwater Monitoring Well Purging <br /> Groundwater wells may or may not be purged depending on the requirements of the project. <br /> Where purging is conducted prior to sampling wells that do not contain SPH, a dedicated 1-inch <br /> diameter PVC "stinger," bailer or groundwater pump may be used to purge the wells. Purge <br /> water may be discharged directly to a vacuum truck via the "stinger", or contained onsite in <br /> holding tanks or 55-gallon DOT-approved drums. To help assure that the collected samples are <br /> representative of fresh formation water, the conductivity, temperature, and pH of the <br /> groundwater are monitored and recorded using a Cambridge Hydac meter or equivalent during <br /> purge operations. Purge operations are determined to be sufficient once successive <br /> measurements of pH, conductivity, and temperature stabilize to within +/- 10 percent. <br /> During purging a minimum of three (3) casing volumes are removed from each well. However, <br /> in the case of very slow recharging wells, purging is deemed sufficient if the well contents are <br /> completely evacuated during purge operations. Unless recharge takes more than two hours, <br /> wells are sampled once the well is recharged to within 80 percent of pre-purge groundwater <br /> elevation. For very slow recharging wells (wells pumped dry during purging), samples may be <br /> collected after two hours of recharge. <br /> Groundwater Sample Acquisition and Handling <br /> Following purging operations, groundwater samples are collected from each of the wells using <br /> pre-cleaned, single-sample polypropylene, disposable bailers. The groundwater sample is <br /> discharged from the bailer to the sample container through a bottom emptying flow control valve <br /> to minimize volatilization. <br /> Collected water samples are discharged directly into laboratory provided, pre-cleaned, 40 <br /> milliliter (ml) glass vials and sealed with Teflon-lined septum and screw-on lids. Labels <br /> documenting sample number, well identification, collection date and time, type of sample and <br /> type of preservative (if applicable) are affixed to each sample. The samples are then placed <br /> into an ice-filled cooler for delivery under chain-of-custody to a laboratory certified by the State <br /> of California Department of Health Services Environmental Laboratory Accreditation Program to <br /> perform the specified tests. <br />
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