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PR0535342
EnvironmentalHealth
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4700 - Waste Tire Program
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PR0535342
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PR0535342
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Entry Properties
Last modified
7/29/2020 5:32:38 PM
Creation date
7/22/2020 8:36:59 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4700 - Waste Tire Program
RECORD_ID
PR0535342
PE
4740
FACILITY_ID
FA0020390
FACILITY_NAME
RENEWED RESOURCES CORP
STREET_NUMBER
29425
Direction
S
STREET_NAME
MACARTHUR
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25312026
CURRENT_STATUS
02
SITE_LOCATION
29425 S MACARTHUR RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\gmartinez
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EHD - Public
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6.5 Mortar and pestle: glass. agate, or aluminum oxide; for grinding soil and sediment <br /> samples. <br /> 6.6 Containers: glass or plastic to store samples. <br /> 6.7 Sieves: 60-mesh (0.25 mm), stainless-steel, Nylon, or equivalent for preparing soil and <br /> sediment samples. <br /> 6.8 Trowels: for smoothing soil surfaces and collecting soil samples. <br /> 6.9 Plastic bags: used for collection and homogenization of soil samples. <br /> 6.10 Drying oven: standard convection or toaster oven, for soil and sediment samples that <br /> require drying. <br /> 7.0 REAGENTS AND STANDARDS <br /> 7.1 Pure Element Standards: Each pure, single-element standard is intended to produce <br /> strong characteristic x-ray peaks of the element of interest only. Other elements present must not <br /> contribute to the fluorescence spectrum. A set of pure element standards for commonly sought <br /> analytes is supplied by the instrument manufacturer, if required for the instrument; not all instruments <br /> require the pure element standards. The standards are used to set the region of interest (ROI) for <br /> each element. They also can be used as energy calibration and resolution check samples. <br /> 7.2 Site-specific Calibration Standards: Instruments that employ fundamental parameters <br /> (FP) or similar mathematical models in minimizing matrix effects may not require SSCS. If the FP <br /> calibration model is to be optimized or if empirical calibration is necessary, then SSCSs must be <br /> collected, prepared, and analyzed. <br /> 7.2.1 The SSCS must be representative of the matrix to be analyzed by FPXRF. <br /> These samples must be well homogenized. A minimum of ten samples spanning the <br /> concentration ranges of the analytes of interest and of the interfering elements must be <br /> obtained from the site. A sample size of 4 to 8 ounces is recommended, and standard glass <br /> sampling jars should be used. <br /> 7.2.2 Each sample should be oven-dried for 2 to 4 hours at a temperature of less <br /> than 150°C. If mercury is to be analyzed, a separate sample portion must remain undried, as <br /> heating may volatilize the mercury. When the sample is dry, all large, organic debris and <br /> nonrepresentative material, such as twigs, leaves, roots, insects, asphalt, and rock should be <br /> removed. The sample should be ground with a mortar and pestle and passed through a 60- <br /> mesh sieve. Only the coarse rock fraction should remain on the screen. <br /> 7.2.3 The sample should be homogenized by using a riffle splitter or by placing 150 <br /> to 200 grams of the dried, sieved sample on a piece of kraft or butcher paper about 1.5 by 1.5 <br /> feet in size. Each comer of the paper should be lifted alternately, rolling the soil over on itself <br /> and toward the opposite comer. The soil should be rolled on itself 20 times. Approximately <br /> 5 grams of the sample should then be removed and placed in a sample cup for FPXRF <br /> analysis. The rest of the prepared sample should be sent off site for ICP or AA analysis. The <br /> method use for confirmatory analysis should meet the data quality objectives of the project. <br /> 7.3 Blank Samples: The blank samples should be from a "clean" quartz or silicon dioxide <br /> matrix that is free of any analytes at concentrations above the method detection limits. These <br /> CD-ROM 6200 - 9 Revision 0 <br /> January 1998 <br />
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