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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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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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;f <br /> 1 <br /> and reported with 99 percent confidence that the <br /> concentration is greater than zero. It is determined <br /> from the analysis of the analyte in question in the <br /> appropriate matrix. The procedure for establishing the <br /> method detection limit is provided in Appendix B of 40 CFR <br /> Part 136 as published in the Federal Register of October <br /> 26, 1984. Appropriate use of detection limits minimizes <br /> confusion in subsequent use of the data. <br /> In general, the protocol for determination of the method <br /> detection limit is too laborious to permit its routine <br /> application in the laboratory. Instead, the "estimated <br /> f detection limit" is determined on a daily basis by any one <br /> of the several approaches cited in the above reference. It <br /> should be noted that detection limits, ne matter how <br /> estimated, are highly variable. They depend on the <br /> instrument, the analyst, reagent purity, and other factors. <br /> In many instances, the detection limit will be dictated by <br /> the nature of interferences present in the sample matrix <br /> rather than instrumental considerations. <br /> D. Assessment <br /> Before the significance of analytical data can be assessed, <br /> one needs to know how precise, how accurate, and how <br /> complete are the data subsets. Precision is amenable to <br /> strict definition by the analysis of replicate results <br /> according to schemes outlined in the USEPA Bandbook for <br /> Analytical Quality Control in Water and Wastewater <br /> Laboratories, March, 1979, Chapter 6. Accuracy is .somewhat <br /> more i (cult to assess. Spike recovery determinations, <br /> regular analysis of laboratory control standards, and use <br /> of external check samples contribute to the general <br /> assurance that the accuracy of a determination is within <br /> acceptable limits. The ultimate accuracy of a <br /> determination also depends on factors external to the <br /> laborataory such as sampling and storage conditions. <br /> Completeness is the most difficult characteristic to <br /> assess, depending as it does upon such factors as <br /> J representativeness of sampling and subsampling, selection <br /> of the appropriate analytical parameters, and scope of the <br /> sampling program relative to the size of the environmental <br /> question being addressed. <br /> While ultimate assessment depends on the experienced <br /> judgment of knowledgeable individuals, statistical treat- <br /> ment of the data can provide some objective measure of <br /> their soundness.. The Federal Register of October 26, 1984, <br /> includes required calculations for accuracy on spiked <br /> VIII-3 <br /> 11 <br />
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