Baseline dioxin exposure in Hämeenkyrö: Difference between revisions
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'''Scope'''<br> | '''Scope'''<br> | ||
'''Baseline dioxin exposure in Hämeenkyrö''' inhabitants. The daily intake and the adipose tissue concentration of polychlorinated dibenzo-p-dioxins, dibenzofurans (PCDD/Fs) and biphenyls (PCBs) in Hämeenkyrö population. | '''Baseline dioxin exposure in Hämeenkyrö''' inhabitants. The daily intake and the adipose tissue concentration of polychlorinated dibenzo-p-dioxins, dibenzofurans (PCDD/Fs) and biphenyls (PCBs) in Hämeenkyrö population. | ||
[[Category:Risk assessment on Hämeenkyrö municipal solid waste incinerator]] | |||
[[Category:Exposures]] | |||
[[Category:Dioxins]] | |||
==== Description ==== | ==== Description ==== | ||
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Note: During the nursing period, the PCDD/F intake of a child can be 1-2 orders of magnitude | Note: During the nursing period, the PCDD/F intake of a child can be 1-2 orders of magnitude | ||
higher than that of an adult. | higher than that of an adult. | ||
Revision as of 20:15, 20 February 2007
Scope
Baseline dioxin exposure in Hämeenkyrö inhabitants. The daily intake and the adipose tissue concentration of polychlorinated dibenzo-p-dioxins, dibenzofurans (PCDD/Fs) and biphenyls (PCBs) in Hämeenkyrö population.
Description
Polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs, "dioxins") are ubiquitously present, stable and persistent environmental contaminants. They are fat soluble and thus tend to bioaccumulate in tissue lipid and in the food chain. More than 90 % of the average human intake of dioxins originates from food, especially food of animal origin. In Finland the main source is fish, whose contribution is 72-94 % of the total PCDD/F intake via food.
Here we will use the daily PCDD/F intake estimated for the Finnish population in average as a starting point. In addition, the other variable in this model, "Dioxin emissions in Hämeenkyrö", may affect the estimate of baseline dioxin exposure in Hämeenkyrö.
For the adipose tissue PCDD/F concentration the value estimated for the general population living in Finnish inland is used.
It is noteworthy, that some subgroups within society, such as nursing babies and people consuming lot of fish may be more highly exposed to dioxins than the average people.
PCBs, another group of persistent environmental contaminants, were included as they behave similarly in the food chain and have partly similar health effects as dioxins.R↻
References
- Holtta P, Kiviranta H, Leppaniemi A, Vartiainen T, Lukinmaa PL, Alaluusua S. Developmental dental defects in children who reside by a river polluted by dioxins and furans. Arch Environ Health. 2001 Nov-Dec;56(6):522-8.
- Kiviranta H, Ovaskainen ML, Vartiainen T. Market basket study on dietary intake of PCDD/Fs, PCBs, and PBDEs in Finland. Environ Int. 2004 Sep;30(7):923-32.
- Kiviranta H, Tuomisto JT, Tuomisto J, Tukiainen E, Vartiainen T. Polychlorinated dibenzo-p-dioxins, dibenzofurans, and biphenyls in the general population in Finland. Chemosphere. 2005 Aug;60(7):854-69.
- Tuomisto et al. 1999. Synopsis on dioxins and PCBs. Publications of the National Public Health Institute B17/1999.
Definition
Comes from literature.
Unit
- Daily intake: WHO-TEQ pg/kg body weight
- Adipose tissue concentration: WHO-TEQ pg/g fat
Result
- Average daily intake of PCDD/Fs 0.79 pg/kg bw
- Average daily intake of PCBs 0.74 pg/kg bw
- Average adipose tissue PCDD/F concentration 26.4 pg/g
- Average adipose tissue PCB concentration 18.1 pg/g
Note: During the nursing period, the PCDD/F intake of a child can be 1-2 orders of magnitude higher than that of an adult.