Literature DB >> 8187706

PCDD and PCDF exposure and levels in humans in Germany.

H Beck1, A Dross, W Mathar.   

Abstract

For nonoccupationally exposed persons, the daily intake via food consumption has been calculated to be 0.35 pg/kg body weight per day for 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and 2.3 pg/kg body weight per day for TCDD equivalents (TEqs). As compared to food, other sources and pathways are of minor importance. Food of animal origin contributes most, although human exposure begins with atmospheric emissions depositing these compounds on plant surfaces. In the meantime, a possible additional body burden from cardboard containers for cow's milk and coffee filters has been practically excluded. Of the 210 existing PCDDs and PCDFs, only 15 2,3,7,8-substituted isomers with a characteristic congener pattern can be found in samples of human origin. In adipose tissue and milk samples, mean levels for 2,3,7,8-TCDD of 7.2 and 3.6 pg/g fat, respectively, and of 56 (range 18-122) and 30 (range 10-72) pg TEqs/g fat, respectively, were determined. Human data revealed a dependency of polychlorinated dibenzo-p-dioxins/polychlorinated dibenzofurans (PCDD/PCDF) levels on age. In human milk, levels became reduced with the number of children born to mothers and duration of breast-feeding period. The average daily intake for a breast-fed child has been calculated to be 17 pg 2,3,7,8-TCDD/kg body weight per day and 142 pg TEqs/kg body weight per day, respectively. Levels in adipose tissue of infants, even if breast fed, were distinctly lower compared to human milk. In human milk, adipose tissue, and whole blood, PCDD/PCDF concentrations have been found to be equal on a fat-weight basis. Liver fat accumulated PCDD/PCDF with an alteration in the congener distribution pattern, whereas brain, even on a fat-weight basis, showed the lowest concentrations. Elevated or even high levels were found in occupationally exposed persons working in special chemical plants or involved in specific processes. There are limited data suggesting slightly elevated PCDD/PCDF levels are due to long-term consumption of a large share of food produced near point sources with a heavy emission or ingestion of soil or dust from such areas.

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Year:  1994        PMID: 8187706      PMCID: PMC1566882          DOI: 10.1289/ehp.94102s1173

Source DB:  PubMed          Journal:  Environ Health Perspect        ISSN: 0091-6765            Impact factor:   9.031


  2 in total

1.  [Analytical methods for the determination of polychlorinated dibenzodioxins and dibenzofurans in human milk].

Authors:  P Fürst; C Fürst; H A Meemken; W Groebel
Journal:  Z Lebensm Unters Forsch       Date:  1989-10

2.  Multivariate statistical approach to a data set of dioxin and furan contaminations in human milk.

Authors:  G U Lindström; M Sjöström; S E Swanson; P Fürst; C Krüger; H A Meemken; W Groebel
Journal:  Bull Environ Contam Toxicol       Date:  1988-05       Impact factor: 2.151

  2 in total
  16 in total

Review 1.  Dioxin effects on neonatal and infant thyroid function: routes of perinatal exposure, mechanisms of action and evidence from epidemiology studies.

Authors:  Sara Mariasole Giacomini; Lifang Hou; Pier Alberto Bertazzi; Andrea Baccarelli
Journal:  Int Arch Occup Environ Health       Date:  2005-10-11       Impact factor: 3.015

2.  Genome-Wide Analysis of Salicylate and Dibenzofuran Metabolism in Sphingomonas Wittichii RW1.

Authors:  Edith Coronado; Clémence Roggo; David R Johnson; Jan Roelof van der Meer
Journal:  Front Microbiol       Date:  2012-08-23       Impact factor: 5.640

3.  Congener-specific levels of dioxins and dibenzofurans in U.S. food and estimated daily dioxin toxic equivalent intake.

Authors:  A Schecter; J Startin; C Wright; M Kelly; O Päpke; A Lis; M Ball; J R Olson
Journal:  Environ Health Perspect       Date:  1994-11       Impact factor: 9.031

4.  Analysis of breast milk to assess exposure to chlorinated contaminants in Kazakhstan: sources of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) exposures in an agricultural region of southern Kazakhstan.

Authors:  K Hooper; T Chuvakova; G Kazbekova; D Hayward; A Tulenova; M X Petreas; T J Wade; K Benedict; Y Y Cheng; J Grassman
Journal:  Environ Health Perspect       Date:  1999-06       Impact factor: 9.031

Review 5.  Mechanisms underlying Children's susceptibility to environmental toxicants.

Authors:  E M Faustman; S M Silbernagel; R A Fenske; T M Burbacher; R A Ponce
Journal:  Environ Health Perspect       Date:  2000-03       Impact factor: 9.031

Review 6.  Breast Milk Monitoring Programs (BMMPs): world-wide early warning system for polyhalogenated POPs and for targeting studies in children's environmental health.

Authors:  K Hooper
Journal:  Environ Health Perspect       Date:  1999-06       Impact factor: 9.031

7.  PCDD/PCDF indoor exposure in day-care centers and PCDD/PCDF blood concentrations of female employees.

Authors:  S von Manikowsky; H Sagunski; O Päpke; K R Fabig; H Neus; M Schümann; K Spannhake; W Karmaus; N Osius; B Zier
Journal:  Environ Health Perspect       Date:  1998-04       Impact factor: 9.031

8.  PCDDs, PCDFs, and PCBs in human blood in relation to consumption of crabs from a contaminated Fjord area in Norway.

Authors:  H R Johansen; J Alexander; O J Rossland; S Planting; M Løvik; P I Gaarder; W Gdynia; K S Bjerve; G Becher
Journal:  Environ Health Perspect       Date:  1996-07       Impact factor: 9.031

Review 9.  Comparisons of estimated human body burdens of dioxinlike chemicals and TCDD body burdens in experimentally exposed animals.

Authors:  M J DeVito; L S Birnbaum; W H Farland; T A Gasiewicz
Journal:  Environ Health Perspect       Date:  1995-09       Impact factor: 9.031

10.  Dietary exposure to polychlorinated biphenyls and dioxins from infancy until adulthood: A comparison between breast-feeding, toddler, and long-term exposure.

Authors:  S Patandin; P C Dagnelie; P G Mulder; E Op de Coul; J E van der Veen; N Weisglas-Kuperus; P J Sauer
Journal:  Environ Health Perspect       Date:  1999-01       Impact factor: 9.031

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