Literature DB >> 24234532

Individual PCBs as predictors for concentrations of non and mono-ortho PCBs in human milk.

M van den Berg1, T L Sinnige, M Tysklind, A T Bosveld, M Huisman, C Koopmans-Essenboom, J G Koppe.   

Abstract

32 Dutch human milk samples were analyzed for PCBs with either HRGC-ECD or HRGC-LRMS in the NCI mode. Samples were collected from three different locations in The Netherlands: Amsterdam, Rotterdam and Groningen. Quantitatively, no differences could be observed between the three localities, while in addition the congener specific pattern showed a striking similarity for all individual samples. Only principal component analysis revealed slight individual differences. Based on similarities in the PCB profiles, linear relationships were calculated between 2,3'4,4',5-PnCB (#118) or 2,2'4,4'5,5'HxCB (#153) and the most relevantnon andmonoortho PCBs exhibiting dioxinlike activity. These PCBs included 2,3,3',4,4'-PnCB (#105), 3,3',4,4'5-PnCB (#126) 2,3,3',4,4',5-HxCB (#156), 2,3,3',4,4',5'-HxCB (#157), 2,3',4,4',5,5'-HxCB (#167) and 3,3',4,4',5'5-HxCB (#169).Good linear relationships were observed between individual PCBs. Based on the results of this study, PCB #118 can be used to predict concentrations of the PCBs #105 and #126. PCB #153 can be used as a predictor for the PCBs #156, #157, #167 and #169, but also for the total toxic equivalencies (TEQs) ofnon andmonoortho PCBs present in human milk. This method using certain PCBs as predictors for other toxicological relevant congeners, can be useful and cost effective, e.g. for epidemiological studies. However, before applied a number of conditions should be met. These are: 1) A stable composition of the PCB matrix should be established. 2) A possible time dependent change in composition of the matrix should first be excluded when used over different time periods.

Entities:  

Year:  1995        PMID: 24234532     DOI: 10.1007/BF02986720

Source DB:  PubMed          Journal:  Environ Sci Pollut Res Int        ISSN: 0944-1344            Impact factor:   4.223


  9 in total

1.  Organochlorine contaminants in arctic marine food chains: identification, geographical distribution and temporal trends in polar bears.

Authors:  R J Norstrom; M Simon; D C Muir; R E Schweinsburg
Journal:  Environ Sci Technol       Date:  1988-09       Impact factor: 9.028

Review 2.  Comparative toxicology and mechanism of action of polychlorinated dibenzo-p-dioxins and dibenzofurans.

Authors:  S H Safe
Journal:  Annu Rev Pharmacol Toxicol       Date:  1986       Impact factor: 13.820

Review 3.  Polychlorinated biphenyls (PCBs), dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), and related compounds: environmental and mechanistic considerations which support the development of toxic equivalency factors (TEFs).

Authors:  S Safe
Journal:  Crit Rev Toxicol       Date:  1990       Impact factor: 5.635

Review 4.  Polychlorinated biphenyls (PCBs): environmental impact, biochemical and toxic responses, and implications for risk assessment.

Authors:  S H Safe
Journal:  Crit Rev Toxicol       Date:  1994       Impact factor: 5.635

5.  Teratogenicity of three polychlorinated dibenzofurans in C57BL/6N mice.

Authors:  L S Birnbaum; M W Harris; E R Barnhart; R E Morrissey
Journal:  Toxicol Appl Pharmacol       Date:  1987-09-15       Impact factor: 4.219

6.  Coplanar PCBs in human milk in the province of Québec, Canada: are they more toxic than dioxin for breast fed infants?

Authors:  E Dewailly; J P Weber; S Gingras; C Laliberté
Journal:  Bull Environ Contam Toxicol       Date:  1991-10       Impact factor: 2.151

Review 7.  The toxicokinetics and metabolism of polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs) and their relevance for toxicity.

Authors:  M Van den Berg; J De Jongh; H Poiger; J R Olson
Journal:  Crit Rev Toxicol       Date:  1994       Impact factor: 5.635

8.  The relative contribution of individual polychlorinated biphenyls (PCBs), polychlorinated dibenzo-p-dioxins (PCDDs) and polychlorinated dibenzo-p-furans (PCDFs) to toxic equivalent values derived for bulked human adipose tissue samples from Wales, United Kingdom.

Authors:  R Duarte-Davidson; S J Harrad; S Allen; A S Sewart; K C Jones
Journal:  Arch Environ Contam Toxicol       Date:  1993-01       Impact factor: 2.804

9.  [Concentration of PCDDs, PCDFs and coplanar PCBs in breast milk of Yusho patients and normal subjects].

Authors:  T Matsueda; T Iida; H Hirakawa; K Fukamachi; H Tokiwa; J Nagayama
Journal:  Fukuoka Igaku Zasshi       Date:  1993-05
  9 in total
  2 in total

1.  Genetic variation in the CYP1A1 gene is related to circulating PCB118 levels in a population-based sample.

Authors:  Lars Lind; Johanna Penell; Anne-Christine Syvänen; Tomas Axelsson; Erik Ingelsson; Andrew P Morris; Cecilia Lindgren; Samira Salihovic; Bert van Bavel; P Monica Lind
Journal:  Environ Res       Date:  2014-06-11       Impact factor: 6.498

2.  Spatial and temporal trends of the Stockholm Convention POPs in mothers' milk -- a global review.

Authors:  Johan Fång; Elisabeth Nyberg; Ulrika Winnberg; Anders Bignert; Åke Bergman
Journal:  Environ Sci Pollut Res Int       Date:  2015-04-26       Impact factor: 4.223

  2 in total

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