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ARCHIVED REPORTS_XR0012618
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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P
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PERSHING
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5608
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3500 - Local Oversight Program
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PR0545653
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ARCHIVED REPORTS_XR0012618
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Last modified
5/6/2020 4:48:28 PM
Creation date
5/6/2020 4:00:14 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012618
RECORD_ID
PR0545653
PE
3528
FACILITY_ID
FA0003727
FACILITY_NAME
CHEVRON STATION #96465 (INACT)
STREET_NUMBER
5608
Direction
N
STREET_NAME
PERSHING
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
APN
10815011
CURRENT_STATUS
02
SITE_LOCATION
5608 N PERSHING AVE
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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( a u <br /> ,L. <br /> f SECTION V : <br /> r <br /> GEP ERAL QUALITY CONTROL PRACTICES <br /> A. Blanks <br /> 1. method Blanks <br /> Method blanks are introduced on a daily basis or at a <br /> frequency of ane-in-twenty if more than that number of <br /> determinations are run in one day. The blanks consist <br /> of organic-free or deicnized water which is then <br /> carried through the analytical scheme as for real <br /> E samples. They serve to locate any contamination asso- <br /> ciated with laboratory storage, laboratory instrumen- <br /> tation, or equipment coming in contact with the sample <br /> during processing. They provide the fundamental base- <br /> line against which the sample signal is measured. <br /> 2. Field and Tra,rel Blanks <br /> These closely related types of blanks find their most <br /> extensive application in anal ysis faz volatile organic <br /> compounds. For each kind, the blank begins as organic- <br /> free reagent water in the laboratory. For a travel <br /> blank, a sample vial is filled wit'3 the reagent water <br /> at the laboratory and then carried with the '�iample <br /> containers out to the field anu back to the laboratory. <br /> Field blanks are carried to the sample site in a cepa- <br /> rate container, with a vial being filled at the <br /> sampling location. In either case, the blank serves to <br /> identify and nossibly correct for airborne contami- <br /> nation associated with collecting or transporting the <br /> .s <br /> } sample. <br /> 3. Sample Blanks <br /> These blanks came into play when native sample char- <br /> acteristics--most often color or. turbidity--interfere <br /> with a determination. If the method in question relies <br /> i on spectrophotometric detection, the sample's original <br /> absorbance at the wavelength of interest is measured <br /> and subtracted from the absorbance of the final <br /> developed color. The value is recorded in the bound <br /> bench hook so both the apparent concentration and the <br /> corrected value may be calculated. <br /> i <br /> V-1 <br /> i <br />
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