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Appendix D Food Codes for NHANES - OEHHA

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Scientific Review Panel Draft February, 2012<br />

Kimura and Otaki (1972) used liver and kidney accumulation of cadmium in<br />

rabbits and hairless mice to estimate dermal absorption. A total dose of 30.5 mg<br />

Cd (in an aqueous CdCl2 solution) was administered to rabbit skin (n=1) in 5<br />

doses over 3 weeks. Two weeks after the final application, 0.40% of the applied<br />

dose was found in liver and kidney combined. In rabbits (n=2), a total dose of 61<br />

mg Cd was administered in multiple cream-like and milk-like ointment<br />

applications, resulting in 0.45 and 0.61%of the applied dose, respectively, in liver<br />

and kidney combined. The type of ointment vehicle used did not appear to<br />

greatly affect the absorption or accumulation characteristics of Cd. Dermal<br />

absorption of cadmium in hairless mice, estimated from kidney and liver<br />

accumulation, ranged from 0.07-0.27% after a single application of ointment<br />

(0.61 mg Cd). Cadmium absorption after multiple ointment applications on<br />

hairless mice ranged from 0.59 - 0.87% of applied dose.<br />

Aqueous 1.0, 0.1 and 0.01% cadmium solutions were painted onto the skin of<br />

mice and rats and air dried each day <strong>for</strong> ten days (Lansdown and Sampson,<br />

1996). Perceptible skin damage occurred at the two highest doses, likely<br />

resulting in increased dermal absorption. At the lowest dose, significantly<br />

increased skin content of cadmium was observed in both mice (138 ng Cd/g) and<br />

rats (248 ng Cd/g). Adequate data to estimate fractional absorption were not<br />

provided.<br />

Although no studies estimated dermal absorption of cadmium aged in soils,<br />

Aringhieri et al. (1985) reported that 80% of cadmium added to a soil containing<br />

high organic matter (14.2%) and high clay content (60%) was adsorbed to soil<br />

particles within 10 min of addition to a soil. Tang et al. (2006) observed that<br />

bioaccessibility of cadmium (relating closely to absorption following ingestion of<br />

soil) in strongly acidic soils spiked with cadmium reached nearly steady state<br />

levels as high as 77% after the first week of aging. In soils highly contaminated<br />

with heavy metals by industrial sources, the MgCl2-exchangeable fraction of<br />

cadmium was about 37% and was considered the most mobile and biologically<br />

available heavy metal in the samples examined (Hickey and Kittrick, 1984).<br />

F. 3.3.2 Discussion and Recommendation <strong>for</strong> a Cadmium and Cadmium<br />

Compounds ABS<br />

No in vivo studies investigating fractional absorption of cadmium from soil were<br />

located. The human in vitro study by Wester et al. (1992) provided the only<br />

quantitative data <strong>for</strong> dermal absorption of cadmium from soil. The retention and<br />

concentrating of cadmium in skin with slow systemic absorption demonstrate the<br />

necessity <strong>for</strong> including the cadmium found in exposed skin <strong>for</strong> estimating an ABS<br />

point estimate.<br />

The lack of quantitative in vivo studies and the use of 16 hr rather than 24 hr<br />

exposures support a point estimate based on the highest fractional absorption of<br />

0.2%, rather than a the lower estimate of 0.1% (based on an averaging of<br />

F-24

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