Environmental Health Criteria 214
Environmental Health Criteria 214
Environmental Health Criteria 214
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HUMAN EXPOSURE ASSESSMENT<br />
samples values value<br />
>LOQ 10 50 95 (GM)<br />
Dustfalla 3282 - 1.4 21.0 579 4.52<br />
Arsenicb 3279 965 < 4 33 1313 5.4<br />
Boron 2896 511 < 0.06 0.64 47.1 0.13<br />
Cadmiumb 3282 0 5 44 833 11.7<br />
Calcium 3277 25 17 273 2679 51.2<br />
Chromium 3282 14 0.02 0.28 3.92 0.07<br />
Copper 3277 1167 < 0.3 1.5 48.8 0.33<br />
Iron 3277 74 2 41 765 7.7<br />
Lead 3282 0 0.11 1.17 86.6 0.29<br />
Magnesium 3277 26 2 25 342 5.2<br />
Phosphorus 3277 1063 < 1.8 17 542 2.8<br />
Zinc 3277 15 0.9 8.6 108 2.2<br />
Units are µg m-2d-1 unless otherwise indicated.<br />
a mg m-2d-1 .<br />
b ng m-2d-1 .<br />
8.3 Sampling design considerations<br />
Section 8.2.2 describes numerous innovative methods that have<br />
been developed and used by researchers to collect settled dust from<br />
surfaces. Many more examples can be found in the literature. However,<br />
there has been little standardization among the methods. Differences<br />
in vacuum pump flow rates, nozzle shapes and sizes, and sampling<br />
technique will affect dust-pickup characteristics of vacuum sampling<br />
methods and will, therefore, affect the results. Differences in wipe<br />
sampling material and technique will also affect the results from wipe<br />
samples. Different recovery rates of dust from alternative<br />
sedimentation methods can also have a large effect on analytical<br />
results. These differences among methods, which are not well<br />
documented in the literature, can make interpretations and comparisons<br />
between studies difficult. It is important that sampling methods are<br />
well described when results from settled dust sampling are reported.<br />
Sampling design considerations for soil should follow the<br />
objectives of the study and consider the particular conditions of the<br />
site being monitored. For example, multiple soil samples can be<br />
obtained around the perimeter of a house at a sufficient distance so<br />
that the soil is representative of material that might be tracked into<br />
the home. In this case, the samples might be composited. Backyard soil<br />
might vary in the number and amounts of contaminants present, as well<br />
as usage and specific activities by residents. The number and location<br />
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