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Last modified
3/9/2020 8:39:33 AM
Creation date
3/9/2020 8:14:22 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0505465
PE
2951
FACILITY_ID
FA0003703
FACILITY_NAME
CITY OF STOCKTON ENGINE #12*
STREET_NUMBER
4010
Direction
E
STREET_NAME
MAIN
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
15727501
CURRENT_STATUS
02
SITE_LOCATION
4010 E MAIN ST
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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� N"001 <br /> City of Stockton, Fire Station No. 12 A68105.01 <br /> August 7, 1995 Page A-3 <br /> ■ Analytical instruments are serviced on a regular basis to monitor accurate calibration; <br /> .. ■ Organic-free water is monitored daily for quality; <br /> ■ Gas chromatographs are calibrated daily; <br /> ■ Method blanks are tested to check whether the glassware and reagents are free of <br /> interference from chemicals that would invalidate the analyses; and <br /> ■ Standards are prepared using the applicable reference materials. <br /> A-5 Disposal of Rinsate and Soil Cuttings: The soil cuttings generated by the drilling <br /> operations are sealed in 55-gallon United States Department of Transportation (DOT) <br /> approved steel drums. The augers and sampling equipment are cleaned on racks and the <br /> rinsate subsequently be transferred to 55-gallon DOT approved steel drums. The drums are <br /> temporarily stored on site at a location remote to the public. Each drum is labelled to <br /> identify its contents. The disposal of this material will be the responsibility of the client. <br /> This material must be disposed of in accordance with all applicable Federal, State and Local <br /> regulations. Cost of disposal of this material range from $65.00 to $100.00 a ton not <br /> including transportation and management fees. <br /> A-6 Standard Operating Procedures for Using Photoionization Detector(PID): The PID <br /> is calibrated in accordance with the manufacture's recommendations prior to use in the field. <br /> Upon arrival at the project site, the PID is used to monitor background concentrations of <br /> organic vapors in the atmosphere at the site. <br /> The background concentrations are measured in a location upwind and removed as possible <br /> from sources of organic vapors on the site. When background concentrations of organic <br /> vapors register as "0.0" on the PID, subsequent readings of "0.0" registered from samples <br /> .r tested in the field are recorded as "ND" (not detected). When background concentrations <br /> of organic vapors register at some quantity above "0.0", subsequent readings registered from <br /> samples tested in the field at or below this value are recorded as 'B/G" (background). <br /> A-7 Standard Operating Procedures for Performing Head Space Analysis: Head space <br /> analysis is performed using a photoionization detector (PID) or a drager tube. A soil <br /> sample is placed in a sealed glass container or plastic bag, agitated, and placed in a warm <br /> atmosphere. After approximately 15 minutes, which is generally sufficient for some of the <br /> volatiles to escape from the soil, the PID probe or tip of the drager tube is inserted into the <br /> container and the gas is sampled. The highest concentration of organic vapors recorded by <br /> the PID or the drager tube reading will be recorded. <br />
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