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Environmental Health Criteria 214

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HUMAN EXPOSURE ASSESSMENT<br />

Some residents still catch and consume considerable amounts of local<br />

fish and shellfish, particularly crabs, during summer and autumn. The<br />

crabs contain high concentrations of PCDDs/Fs with a predominance of<br />

tetra- and hexa-CDFs and PCB-209.<br />

In the study by Johansen et al. (1996), 24 male crab consumers<br />

were recruited non-randomly from news announcements and 10 controls<br />

were drawn randomly from the population register. PCDDs/Fs and PCBs<br />

were measured in blood samples. Information on crab and fish<br />

consumption and intake of fatty food items were collected and the<br />

fishing site reported. The study was designed to determine if<br />

consumption of crabs from the contaminated fjord area led to increased<br />

body burden of PCDDs/Fs and PCBs. From the patterns of PCDDs/Fs and<br />

PCBs congeners in crabs, can congeners in blood be inferred sources?<br />

Finally, can exposure estimates based on blood levels be predicted by<br />

reported crab intake of location? A considerable increase of PCDDs/Fs<br />

in blood was found upon consumption of contaminated crabs. A direct<br />

relationship was found between blood level and the number of crabs<br />

times contamination level. See Fig. 46 from Johansen et al. (1996).<br />

The PCDD/F profile in the high intake group clearly reflected the<br />

profile found in the crab hepatopancreas. PCB-209 does not appear to<br />

be absorbed since it did not increase after crab consumption.<br />

Using a simplified toxicokinetic calculation, good correlation<br />

( r = 0.61) was reported between estimated yearly intake based on<br />

blood values and intake based on reported intake and the fishing site.<br />

The intake calculated for the controls was 9.7 pg TEQ/kg body weight<br />

per week, in good agreement with estimated intake from food in Norway<br />

(8-10 pg TEQ/kg body weight per week). The average exposures of the<br />

moderate and high-intake groups were 31 (10-61) pg/kg body weight per<br />

week and 62 (24-114) pg/kg body weight per week. Most individuals in<br />

the high-intake group exceeded the recommended Nordic tolerable weekly<br />

intake (TWI) of 35 pg/kg body weight per week<br />

12.4.3 Exposure to volatile organic compounds and urinary metabolites<br />

In Tokyo, Nakahama et al. (1997) measured personal VOC exposures<br />

over 12 h and the metabolites in urine. Thirteen men and 17 women<br />

participated. The VOCs 1,1,1-trichloroethane, trichloroethylene and<br />

tetrachloroethylene were sampled with passive absorbent badges.<br />

Trichloroethanol and trichloroacetic acid corrected for creatinine<br />

were measured in urine. Personal exposures were well correlated<br />

( r = 0.80) with urinary metabolites. Interestingly, women inhaled<br />

twice as much VOCs as men, perhaps because of increased exposure to<br />

household chemicals and cosmetics.<br />

http://www.inchem.org/documents/ehc/ehc/ehc<strong>214</strong>.htm<br />

Page 224 of 284<br />

6/1/2007

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