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PR0535342
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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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mixed in well and stay on top of the coarser-grained particles in the sample cup. One way to reduce <br /> such error is to grind and sieve all soil samples to a uniform particle size thus reducing sample-to- <br /> sample particle size variability. Homogeneity is always a concern when dealing with soil samples. <br /> Every effort should be made to thoroughly mix and homogenize soil samples before analysis. Field <br /> studies have shown heterogeneity of the sample generally has the largest impact on comparability <br /> with confirmatory samples. <br /> 4.3 Moisture content may affect the accuracy of analysis of soil and sediment sample <br /> analyses. When the moisture content is between 5 and 20 percent, the overall error from moisture <br /> may be minimal. However, moisture content may be a major source of error when analyzing <br /> samples of surface soil or sediment that are saturated with water. This error can be minimized by <br /> drying the samples in a convection or toaster oven. Microwave drying is not recommended because <br /> field studies have shown that microwave drying can increase variability between FPXRF data and <br /> confirmatory analysis and because metal fragments in the sample can cause arcing to occur in a <br /> microwave. <br /> 4.4 Inconsistent positioning of samples in front of the probe window is a potential source <br /> of error because the x-ray signal decreases as the distance from the radioactive source increases. <br /> This error is minimized by maintaining the same distance between the window and each sample. <br /> For the best results, the window of the probe should be in direct contact with the sample, which <br /> means that the sample should be flat and smooth to provide a good contact surface. <br /> 4.5 Chemical matrix effects result from differences in the concentrations of interfering <br /> elements. These effects occur as either spectral interferences (peak overlaps) or as x-ray <br /> absorption and enhancement phenomena. Both effects are common in soils contaminated with <br /> heavy metals. As examples of absorption and enhancement effects; iron (Fe) tends to absorb <br /> copper(Cu) x-rays, reducing the intensity of the Cu measured by the detector, while chromium (Cr) <br /> will be enhanced at the expense of Fe because the absorption edge of Cr is slightly lower in energy <br /> than the fluorescent peak of iron. The effects can be corrected mathematically through the use of <br /> fundamental parameter (FP) coefficients. The effects also can be compensated for using SSCS, <br /> which contain all the elements present on site that can interfere with one another. <br /> 4.6 When present in a sample, certain x-ray lines from different elements can be very close <br /> in energy and, therefore, can cause interference by producing a severely overlapped spectrum. The <br /> degree to which a detector can resolve the two different peaks depends on the energy resolution of <br /> the detector. If the energy difference between the two peaks in electron volts is less than the <br /> resolution of the detector in electron volts, then the detector will not be able to fully resolve the <br /> peaks. <br /> The most common spectrum overlaps involve the Kp line of element Z-1 with the KQ line of <br /> element Z. This is called the K,,/K, interference. Because the KQ:K, intensity ratio for a given <br /> element usually is about 7:1, the interfering element, Z-1, must be present at large concentrations <br /> to cause a problem. Two examples of this type of spectral interference involve the presence of large <br /> concentrations of vanadium (V) when attempting to measure Cr or the presence of large <br /> concentrations of Fe when attempting to measure cobalt (Co). The V Ka and Ko energies are 4.95 <br /> and 5.43 keV, respectively, and the Cr Ka energy is 5.41 keV. The Fe Ka and Kp energies are 6.40 <br /> and 7.06 keV, respectively, and the Co KQ energy is 6.92 keV. The difference between the V Kp and <br /> Cr KQ energies is 20 eV, and the difference between the Fe Kp and the Cc Ka energies is 140 eV. <br /> The resolution of the highest-resolution detectors in FPXRF instruments is 170 eV. Therefore, large <br /> amounts of V and Fe will interfere with quantitation of Cr or Co, respectively. The presence of Fe <br /> is a frequent problem because it is often found in soils at tens of thousands of parts per million <br /> (ppm). <br /> CD-ROM 6200 -4 Revision 0 <br /> January 1998 <br />
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