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Appendix D Food Codes for NHANES - OEHHA

Appendix D Food Codes for NHANES - OEHHA

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Scientific Review Panel Draft February, 2012<br />

Following 24 hour dermal exposure + 24 hour post-exposure (total of 48 hours<br />

from initiation of exposure), the TCDD content of the liver was determined. The<br />

uptake of TCDD under the experimental protocols ranged from 0.54 ± 0.06 to<br />

1.01 ± 0.22% and averaged 0.76 ± 0.16%. The percent uptake of TCDD in liver<br />

was not affected by the applied TCDD dose (12.5 or 125 ng/kg BW), the<br />

presence of crankcase oil in the soil, the use of soil that had been<br />

environmentally contaminated with TCDD, or by the use of haired or hairless<br />

rats.<br />

Peak liver concentrations <strong>for</strong> TCDD administered orally and dermally were used<br />

to correct <strong>for</strong> incomplete absorption in the calculation of relative dermal<br />

absorption. The calculation is based on the assumption that the source of fecal<br />

TCDD following oral exposure is unabsorbed TCDD. The estimated relative<br />

dermal bioavailability is 1.5% from laboratory-contaminated soil and 1.6% from<br />

environmentally contaminated soil.<br />

Diliberto et al. (1996) note that during the first 48 hours following oral exposure,<br />

TCDD in rat feces included both unabsorbed TCDD and absorbed TCDD that<br />

was excreted in bile. However the data suggest that at 48 hours, absorbed<br />

TCDD contributes only about 10% of the fecal TCDD.<br />

Poiger and Schlatter (1980) applied radiolabeled TCDD in a soil/water paste<br />

<strong>for</strong>mulation (26, 350, or 1300 ng in 14.3 mg soil/cm 2 skin) to the backs of hairless<br />

rats and measured the appearance of label in the livers. The soil (organic carbon<br />

content unspecified) was taken from the Seveso region and was TCDD-free.<br />

Measurements were taken 48 hours after the initiation of a 24 hour exposure<br />

period.<br />

The average percentage of dose in the liver after dermal application was 0.05,<br />

1.7, and 2.2% <strong>for</strong> the 26, 350, and 1300 ng dose groups, respectively. The<br />

authors noted that other researchers observed that 70% of total body burden of<br />

administered TCDD is found in the liver of rats. Using this estimate, the<br />

corrected dermal absorption of total applied dose is 0.07, 2.4, and 3.1% <strong>for</strong> the<br />

26, 350, and 1300 ng dose groups, respectively. The authors also compared the<br />

liver uptake of dermally applied TCDD from a soil/water paste to the uptake from<br />

methanol, and found the soil/water paste caused a reduction in the fractional<br />

uptake (compared to methanol) of 12 percent (1.6 ng TCDD/kg BW) or 15<br />

percent (5.8 ng/kg BW).<br />

TCDD in acetone vehicle was applied to human skin in vitro to estimate the<br />

capacity of skin to store TCDD (Weber et al., 1991). Although TCDD did not<br />

readily penetrate the skin into the saline receptor fluid (0.03% of dose) after 16.7<br />

hrs exposure, a major portion of the dose was found in skin. The percent of dose<br />

absorbed in skin at 16.7 hrs was 56% at a skin loading of 65 ng/cm 2 , and 40% at<br />

a skin loading of 6.5 ng/cm 2 .<br />

F-52

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