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ARCHIVED REPORTS_1996_2
EnvironmentalHealth
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4400 - Solid Waste Program
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PR0440001
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ARCHIVED REPORTS_1996_2
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Last modified
7/17/2020 3:53:09 PM
Creation date
7/3/2020 10:40:16 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
1996_2
RECORD_ID
PR0440001
PE
4433
FACILITY_ID
FA0004514
FACILITY_NAME
AUSTIN ROAD/ FORWARD LANDFILL
STREET_NUMBER
9069
Direction
S
STREET_NAME
AUSTIN
STREET_TYPE
RD
City
STOCKTON
Zip
95215
CURRENT_STATUS
02
SITE_LOCATION
9069 S AUSTIN RD
P_LOCATION
01
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\SW\SW_4433_PR0440001_9069 S AUSTIN_1996_2.tif
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EHD - Public
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FS <br />Section No: 8 <br />Page: 3 of 5 <br />Revision No: 2.0 <br />Date: January 15, 1994 <br />8.3.6 Selection of Calibration Levels <br />Two standards should be included per order of magnitude of concentration of the <br />calibration curve. For example 0.1, 1.0, 10.0 has 2 standards per order magnitude (0.1 <br />and 1.0? 1.0 and 10.0). In cases where instrumentation spans several orders of <br />magnitude, the SOP for that method may not require this policy. <br />1 1:: I .. 11. 1 <br />..1 1 ill ` i4a1 . t JI. 4 1 11 li. 1 f i 1 4, 1 .: 1 WA L141,1 <br />1. i 1: 1 .' <br />8.3.7 Calibration Analysis Sequence <br />The calibration must progress from the analysis of the lowest to highest standard unless <br />the instrumentation does not permit it. A blank must be analyzed after the highest <br />calibration standard. <br />If the analysis requires an initial high standard to set the gain, a blank must be run <br />before starting with the low calibration standard unless the instrumentation does not <br />permit it. <br />8.3.8 Calibration Acceptance Criteria <br />In general, for inorganics, the calculated value for standards must be wit 10% of the <br />expected value. However, the value determined by the calibration curve for the lowest <br />standard must be wit +/- 50% of the true value and if the calibration is linear <br />through the ori (at less than +/- 1/2 the detection limit). For organics, if a linear <br />regression is used, a single average response factor may be used. The percent relative <br />standard deviation for the individual response factors must be less than the <br />( <br />maximum value listed for the method in the SOP. <br />8.3.9 Calibration Check Compounds (CCC) and Initial Calibration Verifications (ICV°s) <br />The CCC or ICV is used to check the validity of the initial calibration. This standard is <br />composed of some or all of the same analytes used for calibration but from a different <br />source than the calibration standard. The standard should be at a concentration near the <br />midpoint of the curve. In many cases FGL uses a Laboratory Control Sample (LCS) as <br />an ICV. In this case the LCS verifies both the calibration and sample preparation. FGL <br />uses control charts for LCSIs and acceptance ranges for many analytes have been <br />statistically derived. Please see table 5-1 for acceptance limits. If calculated acceptance <br />criteria are not listed, the general acceptance range is +/-25% of the true value for <br />organics and +/-10% for inorganics. <br />8.3.10 Continuing Calibration Verifications (CCV) <br />The CCV is used to verify continuing calibration validity without having to completely <br />restandardize the instrument. Refer to specific EPA methods or SOPS to determine <br />whether this is required. The continuing calibration standard should be near the <br />mid -point of the calibration curve. If calculated acceptance criteria are not listed, the <br />general acceptance range is +/-25% of the true value for organics and +/-10% for <br />inorganics. <br />
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