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2900 - Site Mitigation Program
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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
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EHD - Public
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6 / ORGANIC ANALYTICAL METHODS - GC <br />and hold until all compounds have eluted. For a higher boiling range of <br />compounds, operate at 50' C isothermal for 2 min, then program at 3''min <br />to 110' C and hold until all compounds have eluted. Column 1 provides <br />outstanding separations for a wide variety of aromatic hydrocarbons. <br />Column 1 should be used as the primary analytical column because of its <br />unique ability to resolve para, meta, and ortho aromatic isomers. <br />Column 2: The carrier gas is helium at a flow rate of 30 ml/min. The <br />temperature program sequence is as fellows: 40' C isothermal for 2 min, <br />then 2'/min to 100' C and hold until all compounds have eluted. Col- <br />umn 2, an extremely high polarity column, has been used for a number of <br />years to resolve aromatic hydrocarbons from alkanes in complex samples. <br />However, since the resolution between some of the aromatics is not as <br />efficient as with Column 1, Column 2 should be used as a confirmatory <br />column. <br />7.2 Calibration. Assemble necessary gas chromatographic apparatus and <br />establish operating parameters equivalent to those indicated in Section 7.1. <br />7.2.1 By injecting secondary standards, adjust the sensitivity of <br />the analytical system for each compound being analyzed so as to detect <br />quantities of less than or equal to 1 µg for waste samples. Detection <br />limits to be used for groundwater analysis are given in Table 1. <br />Calibrate the chromatographic system using either the external <br />standard technique (Section 7.2.2) or the internal standard technique <br />(Section 7.2.3). <br />7.2.2 External standard calibration procedure <br />7.2.2.1 Prepare calibration standards at a minimum of three <br />concentration levels for each parameter by carefully adding 20.0 µl <br />of one or more secondary dilution standards to 100, 500, or 1,000 <br />ml of reagent water or the matrix under study. A 25-µ1 syringe <br />should be used for this operation. One of the external standards <br />should be at a concentration near, but above, the method detection <br />limit and the other concentrations should correspond to the expected <br />range of concentrations found in real samples or should define the <br />working range of the detector. These aqueous standards must be <br />prepared fresh daily. <br />7.2.2.2 Analyze each calibration standard according to the <br />procedure being used (direct aqueous injection, headspace, or <br />purge -and -trap) and tabulate peak height or area responses against <br />the concentration in the standard. The results can be used to <br />prepare a calibration curve for each compound. Alternatively, if <br />the ratio of response to concentration (calibration factor) is a <br />constant over the working range (less than 10% relative standard <br />deviation), linearity through the origin can be assumed and the <br />
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