My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
FIELD DOCUMENTS
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
V
>
VICTOR
>
930
>
2900 - Site Mitigation Program
>
PR0505363
>
FIELD DOCUMENTS
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
5/17/2019 9:45:35 AM
Creation date
5/16/2019 2:23:25 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0505363
PE
2960
FACILITY_ID
FA0005584
FACILITY_NAME
VALLEY PACIFIC LODI PLANT & CARDLOCK
STREET_NUMBER
930
Direction
E
STREET_NAME
VICTOR
STREET_TYPE
RD
City
LODI
Zip
95240
APN
04905023
CURRENT_STATUS
01
SITE_LOCATION
930 E VICTOR RD
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
Scanner
AMeuangkhoth
Tags
EHD - Public
Jump to thumbnail
< previous set
next set >
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
283
PDF
Print
Pages to print
Enter page numbers and/or page ranges separated by commas. For example, 1,3,5-12.
After downloading, print the document using a PDF reader (e.g. Adobe Reader).
View images
View plain text
8 / ORGANIC ANALYTICAL METHODS - GC <br />If the RF value over the working range is a constant (less than <br />10% relative standard deviation), the RF can_ be assumed to be <br />invariant and the average RF can be used for calculations. Alter- <br />natively, the results can be used to plot a calibration curve of <br />response ratios, As/Ais against RF. <br />7.2.3.4 The working calibration curve or RF must be verified <br />on each working day by measuring one or more calibration standards. <br />If the response for any parameter varies from the predicted response <br />by more than +10%, either the test must be repeated using a fresh <br />calibration standard, or a new calibration curve must be prepared <br />for that compound. <br />7.3 Gas chromatographic analysis <br />7.3.1 Introduce volatile compounds to the gas chromatograph using <br />direct injection, headspace (Method 5020), or purge -and -trap (Method <br />5030). <br />7.3.2 Table 1 summarizes the estimated retention times and detec- <br />tion limits for a number of organic compounds analyzable using this <br />method. An example of the separation achieved by Column 1 is shown in <br />Figure 1. An example of the separation achieved by Column 2 is shown in <br />Figure 2. <br />7.3.3 Calibrate the system immediately prior to conducting any <br />analysis and recheck for each type of waste. Calibration should be <br />done no less frequently than at the beginning and end of each analysis <br />session. <br />8.0 Quality Control <br />8.1 Before processing any samples, the analyst should demonstrate <br />through the analysis of a distilled water me.hod blank that all glassware <br />and reagents are interference -free. Each time a set of samples is extracted <br />or there is a change in reagents, a method blank should be processed as a <br />safeguard against chronic laboratory contamination. The blank samples should <br />be carried through all stages of the sample preparation and measurement. <br />8.2 Standard quality assurance practices should be used with this <br />method. Field replicates should be collected to validate the precision of <br />the sampling technique. Laboratory replicates should be analyzed to validate <br />the precision of the analysis. Fortified samples should be carried through <br />all stages of sample preparation and measurement; they should be analyzed <br />to va Idate the sensitivity and accuracy of the analysis. If the fortified <br />waste samples do not indicate sufficient sensitivity to detect less than or <br />equal to 1 pg/g of sample, then the sensitivi�y of the instrument should be <br />
The URL can be used to link to this page
Your browser does not support the video tag.