» Articles » PMID: 11713002

Differential Effects of Two Lots of Aroclor 1254 on Enzyme Induction, Thyroid Hormones, and Oxidative Stress

Overview
Date 2001 Nov 20
PMID 11713002
Citations 6
Authors
Affiliations
Soon will be listed here.
Abstract

Aroclor 1254 is a commercial mixture of polychlorinated biphenyls (PCBs), which is defined as being 54% chlorine by weight. However, the congener composition varies from lot to lot. Two lots which have been used in toxicity studies, 124-191 and 6024 (AccuStandard), were analyzed for their congener composition. Lot 6024 has approximately 10 times the dioxin toxic equivalents (TEQ) of lot 124-191. The purpose of this study was to determine if the difference in the TEQ of the two lots explains the different in vivo responses seen on a weight basis. Male Long-Evans rats (70 days old) were treated orally with a single dose of 0-1,000 mg/kg of each lot. Hepatic ethoxy-, methoxy-, and pentoxyresorufin O-deethylase (EROD, MROD, and PROD, respectively) activities as well as serum thyroxine (T(4)) concentrations and measures of oxidative stress were determined 4 days after treatment. Results, on a weight basis, indicate that lot 6024 led to a greater induction of EROD, MROD, and PROD but not total T(4) reduction. The differences in TEQ between the lots explained the differential induction of EROD and MROD but did not account for the induction of PROD nor decreases in T(4). PROD induction is not due to dioxin-like congeners, whereas the decrease in serum T(4) levels may involve multiple mechanisms. Effects on the antioxidants ascorbic acid and uric acid were seen only at the highest mass dose for both lots and were not explained by the difference in TEQ. These results illustrate that the differences in the TEQ explain the differences in the strict dioxin-like effects (EROD, MROD induction), but the non-dioxin-like congeners cause other effects that are not associated with the aryl hydrocarbon receptor (e.g., PROD). In addition, supra-additive effects also occur in the mixture (T(4), oxidative stress). Thus, current results demonstrate that overall toxicity cannot be predicted on the basis of the TEQ values. It is also critical that the lot number is reported in studies conducted with Aroclor 1254 because the congener composition and therefore the effects observed can be very different.

Citing Articles

Concentration dependence of human and mouse aryl hydrocarbon receptor responsiveness to polychlorinated biphenyl exposures: Implications for aroclor mixtures.

Shi H, Hardesty J, Jin J, Head K, Falkner K, Cave M Xenobiotica. 2019; 49(12):1414-1422.

PMID: 30991879 PMC: 6764862. DOI: 10.1080/00498254.2019.1566582.


Accidental exposure to polychlorinated biphenyls (PCB) in waste cargo after heavy seas. Global waste transport as a source of PCB exposure.

Budnik L, Wegner R, Rogall U, Baur X Int Arch Occup Environ Health. 2013; 87(2):125-35.

PMID: 23292295 DOI: 10.1007/s00420-012-0841-x.


Differential effects of polychlorinated biphenyl congeners on serum thyroid hormone levels in rats.

Martin L, Klaassen C Toxicol Sci. 2010; 117(1):36-44.

PMID: 20573785 PMC: 2923289. DOI: 10.1093/toxsci/kfq187.


Perinatal exposure to polychlorinated biphenyls differentially affects cerebellar development and motor functions in male and female rat neonates.

Nguon K, Baxter M, Sajdel-Sulkowska E Cerebellum. 2005; 4(2):112-22.

PMID: 16035193 DOI: 10.1080/14734220510007860.


Assessing human polychlorinated biphenyl contamination for epidemiologic studies: lessons from patterns of congener concentrations in Canadians in 1992.

Gladen B, Doucet J, Hansen L Environ Health Perspect. 2003; 111(4):437-43.

PMID: 12676596 PMC: 1241425. DOI: 10.1289/ehp.5858.


References
1.
Zoeller R, Dowling A, Vas A . Developmental exposure to polychlorinated biphenyls exerts thyroid hormone-like effects on the expression of RC3/neurogranin and myelin basic protein messenger ribonucleic acids in the developing rat brain. Endocrinology. 1999; 141(1):181-9. DOI: 10.1210/endo.141.1.7273. View

2.
Cheek A, Kow K, Chen J, McLachlan J . Potential mechanisms of thyroid disruption in humans: interaction of organochlorine compounds with thyroid receptor, transthyretin, and thyroid-binding globulin. Environ Health Perspect. 1999; 107(4):273-8. PMC: 1566512. DOI: 10.1289/ehp.99107273. View

3.
Slezak B, Hatch G, DeVito M, Diliberto J, Slade R, Crissman K . Oxidative stress in female B6C3F1 mice following acute and subchronic exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Toxicol Sci. 2000; 54(2):390-8. DOI: 10.1093/toxsci/54.2.390. View

4.
Kodavanti P, Kannan N, Yamashita N, Ward T, Burgin D, Tilson H . Differential effects of two lots of aroclor 1254: congener-specific analysis and neurochemical end points. Environ Health Perspect. 2001; 109(11):1153-61. PMC: 1240477. DOI: 10.1289/ehp.011091153. View

5.
Babior B, Kipnes R, Curnutte J . Biological defense mechanisms. The production by leukocytes of superoxide, a potential bactericidal agent. J Clin Invest. 1973; 52(3):741-4. PMC: 302313. DOI: 10.1172/JCI107236. View