Literature DB >> 6719458

Investigation of the potential for binding of Di(2-ethylhexyl) phthalate (DEHP) and Di(2-ethylhexyl) adipate (DEHA) to liver DNA in vivo.

A von Däniken, W K Lutz, R Jäckh, C Schlatter.   

Abstract

It was the aim of this investigation to determine whether covalent binding of di(2-ethylhexyl) phthalate (DEHP) to rat liver DNA and of di(2-ethylhexyl) adipate (DEHA) to mouse liver DNA could be a mechanism of action contributing to the observed induction of liver tumors after lifetime feeding of the respective rodent species with high doses of DEHP and DEHA. For this purpose, DEHP and DEHA radiolabeled in different parts of the molecule were administered orally to female rats and mice, respectively, with or without pretreatment for 4 weeks with 1% unlabeled compound in the diet. Liver DNA was isolated after 16 hr and analyzed for radioactivity. The data were converted to a covalent binding index, CBI = (micromoles of substance bound per mole of DNA nucleotides)/(millimoles of substance applied per kilogram body weight), in order to allow a quantitative comparison also with other carcinogens and noncarcinogens. Administration of [14C]carboxylate-labeled DEHP to rats resulted in no measurable DNA radioactivity. The limit of detection, CBI less than 0.02 was about 100 times below the CBI of compounds where an observable tumor-inducing potential could be due to genotoxicity. With [14C]- and [3H]DEHP labeled in the alcohol moiety, radioactivity was clearly measurable in rat liver DNA. HPLC analysis of enzyme-degraded or acid-hydrolyzed DNA revealed that the natural nucleosides or purine bases were radiolabeled whereas no radioactivity was detectable in those fractions where the carcinogen-modified nucleoside or base adducts are expected. The respective limits of detection were at 0.07 and 0.04 CBI units for the 14C and 3H labels, respectively. The experiments with [14C]- and [3H]DEHA, labeled in the alcohol moiety and administered to mice, revealed a minute radioactivity of less than 50 dpm/mg liver DNA, too little to allow a nucleoside analysis to determine that fraction of the radioactivity which had been incorporated via biosynthesis. Expressed in the CBI units, values of 0.05 to 0.15 for 14C and 0.01 to 0.12 for 3H resulted. Determination of the level of 14CO2 expiration revealed a linear correlation with the specific activity of DNA. Experiments with 2-ethyl[1-14C]hexanol performed with both rats and mice allowed the conclusion that most if not all DEHA radioactivity in mouse liver DNA was due to biosynthetic incorporation. A maximum possible true DNA binding by DEHA must be below CBI 0.01.(ABSTRACT TRUNCATED AT 400 WORDS)

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Year:  1984        PMID: 6719458     DOI: 10.1016/0041-008x(84)90089-9

Source DB:  PubMed          Journal:  Toxicol Appl Pharmacol        ISSN: 0041-008X            Impact factor:   4.219


  11 in total

1.  Quantitative evaluation of DNA binding data for risk estimation and for classification of direct and indirect carcinogens.

Authors:  W K Lutz
Journal:  J Cancer Res Clin Oncol       Date:  1986       Impact factor: 4.553

2.  Peroxisome proliferation due to di (2-ethylhexyl) adipate, 2-ethylhexanol and 2-ethylhexanoic acid.

Authors:  Y Keith; M C Cornu; P M Canning; J Foster; J C Lhuguenot; C R Elcombe
Journal:  Arch Toxicol       Date:  1992       Impact factor: 5.153

3.  Morphological transformation and catalase activity of Syrian hamster embryo cells treated with hepatic peroxisome proliferators, TPA and nickel sulphate.

Authors:  S O Mikalsen; I Holen; T Sanner
Journal:  Cell Biol Toxicol       Date:  1990-01       Impact factor: 6.691

4.  Promoting activity of di(2-ethylhexyl)phthalate in rat liver foci bioassay.

Authors:  D Oesterle; E Deml
Journal:  J Cancer Res Clin Oncol       Date:  1988       Impact factor: 4.553

5.  Identification of a peroxisome proliferator-responsive element upstream of the gene encoding rat peroxisomal enoyl-CoA hydratase/3-hydroxyacyl-CoA dehydrogenase.

Authors:  B Zhang; S L Marcus; F G Sajjadi; K Alvares; J K Reddy; S Subramani; R A Rachubinski; J P Capone
Journal:  Proc Natl Acad Sci U S A       Date:  1992-08-15       Impact factor: 11.205

6.  Peroxisome proliferation due to di(2-ethylhexyl) phthalate (DEHP): species differences and possible mechanisms.

Authors:  C R Elcombe; A M Mitchell
Journal:  Environ Health Perspect       Date:  1986-12       Impact factor: 9.031

7.  Comparative pharmacokinetics and subacute toxicity of di(2-ethylhexyl) phthalate (DEHP) in rats and marmosets: extrapolation of effects in rodents to man.

Authors:  C Rhodes; T C Orton; I S Pratt; P L Batten; H Bratt; S J Jackson; C R Elcombe
Journal:  Environ Health Perspect       Date:  1986-03       Impact factor: 9.031

8.  Investigation of the potential for binding of di(2-ethylhexyl) phthalate (DEHP) to rat liver DNA in vivo.

Authors:  W K Lutz
Journal:  Environ Health Perspect       Date:  1986-03       Impact factor: 9.031

9.  Comparison of hepatic peroxisome proliferative effect and its implication for hepatocarcinogenicity of phthalate esters, di(2-ethylhexyl) phthalate, and di(2-ethylhexyl) adipate with a hypolipidemic drug.

Authors:  J K Reddy; M K Reddy; M I Usman; N D Lalwani; M S Rao
Journal:  Environ Health Perspect       Date:  1986-03       Impact factor: 9.031

10.  The tumour promoter 12-O-tetradecanoylphorbol-13-acetate increases the activities of some peroxisome-associated enzymes in in vitro cell culture.

Authors:  J R Lillehaug; R K Berge
Journal:  Br J Cancer       Date:  1986-01       Impact factor: 7.640

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