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PR0535342
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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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11.4 For intrusive analysis of surface or sediment, it is recommended that a sample be <br /> collected from a 4- by 4-inch square that is 1 inch deep. This will produce a soil sample of <br /> approximately 375 grams or 250 cm3, which is enough soil to fill an 8-ounce jar. The sample should <br /> be homogenized, dried, and ground before analysis. The sample can be homogenized before or <br /> after drying. The homogenization technique to be used after drying is discussed in Section 4.2. If <br /> the sample is homogenized before drying, it should be thoroughly mixed in a beaker or similar <br /> container, or if the sample is moist and has a high clay content, it can be kneaded in a plastic bag. <br /> One way to monitor homogenization when the sample is kneaded in a plastic bag is to add sodium <br /> fluorescein dye to the sample. After the moist sample has been homogenized, it is examined under <br /> an ultraviolet light to assess the distribution of sodium fluorescein throughout the sample. If the <br /> fluorescent dye is evenly distributed in the sample, homogenization is considered complete; if the <br /> dye is not evenly distributed, mixing should continue until the sample has been thoroughly <br /> homogenized. During the study conducted to provide data for this method, the homogenization <br /> procedure using the fluorescein dye required 3 to 5 minutes per sample. As demonstrated in <br /> Sections 13.5 and 13.7, homogenization has the greatest impact on the reduction of sampling <br /> variability. It produces little or no contamination. Often, it can be used without the more labor <br /> intensive steps of drying, grinding, and sieving given in Sections 11.5 and 11.6. Of course, to <br /> achieve the best data quality possible all four steps must be followed. <br /> 11.5 Once the soil or sediment sample has been homogenized, it should be dried. This can <br /> be accomplished with a toaster oven or convection oven. A small aliquot of the sample (20 to 50 <br /> grams) is placed in a suitable container for drying. The sample should be dried for 2 to 4 hours in <br /> the convection or toaster oven at a temperature not greater than 150°C. Microwave drying is not <br /> a recommended procedure. Field studies have shown that microwave drying can increase variability <br /> between the FPXRF data and confirmatory analysis. High levels of metals in a sample can cause <br /> arcing in the microwave oven, and sometimes slag forms in the sample. Microwave oven drying can <br /> also melt plastic containers used to hold the sample. <br /> 11.6 The homogenized dried sample material should be ground with a mortar and pestle and <br /> passed through a 60-mesh sieve to achieve a uniform particle size. Sample grinding should <br /> continue until at least 90 percent of the original sample passes through the sieve. The grinding step <br /> normally takes an average of 10 minutes per sample. An aliquot of the sieved sample should then <br /> be placed in a 31.0-mm polyethylene sample cup (or equivalent) for analysis. The sample cup <br /> should be one-half to three-quarters full at a minimum. The sample cup should be covered with a <br /> 2.5 pm Mylar(or equivalent) film for analysis. The rest of the soil sample should be placed in a jar, <br /> labeled, and archived for possible confirmation analysis. All equipment including the mortar, pestle, <br /> and sieves must be thoroughly cleaned so that any cross-contamination is below the MDLs of the <br /> procedure or DQOs of the analysis. <br /> 12.0 DATA ANALYSIS AND CALCULATIONS <br /> Most FPXRF instruments have software capable of storing all analytical results and spectra. The <br /> results are displayed in parts per million and can be downloaded to a PC, which can provide a hard <br /> copy printout. Individual measurements that are smaller than three times their associated SD should <br /> not be used for quantitation. <br /> 13.0 METHOD PERFORMANCE <br /> 13.1 This section discusses four performance factors, field-based method detection limits, <br /> precision, accuracy, and comparability to EPA-approved methods. The numbers presented in <br /> Tables 4 through 9 were generated from data obtained from six FPXRF instruments. The soil <br /> samples analyzed by the six FPXRF instruments were collected from two sites in the United States. <br /> CD-ROM 6200 - 17 Revision 0 <br /> January 1998 <br />
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