Biomedical subjects

M Van den Berg

Publications and source records attributed to M Van den Berg.

At least 19 recordsLinked to original sources

PubMed2006

Determination of in vitro relative potency (REP) values for mono-ortho polychlorinated biphenyls after purification with active charcoal.

The TEF system for dioxin-like compounds has included assignment of TEF values for mono-ortho polychlorinated biphenyls (MO-PCBs). Small traces of aryl hydrocarbon receptor (AhR)-active impurities could result in artifactually higher relative potency (REP) values. MO-PCBs -105, -118, -156, and -167 were purified on an active charcoal column to remove AhR agonists that could be present as impurities. Activation or inhibition of AhR-dependent gene expression by purified MO-PCBs was studied in stably transfected cell lines (H1G1.1c3 mouse, H4G1.1c2 rat hepatoma), containing an AhR-responsive (AhR-EGFP) reporter gene. In addition, EROD activity was used as marker for CYP1A1 activity in these cell lines. MO-PCBs -105, -118, -156 induced AhR-EGFP expression in both rodent cell lines, with PCB-156 (10microM) being most effectively; inducing gene expression to approximately 27% of TCDD (mouse cells) and 62.5+/-3.4% (rat cells) of TCDD. This concurred with increased EROD activity in both cell lines to maxima of 20.5+/-1.5% and 68+/-3.2% of TCDD, respectively. No induction was observed for PCB-167. In the H1G1.1c3 mouse cells, PCB-105, -118 and -156 (10microM) significantly reduced TCDD-induced AhR-EGFP expression to 50.9+/-2.9%, 58.3+/-2.2% and 70.8+/-1.3% of TCDD. Reduced EROD activity was also observed, of 39.3+/-2.8%, 67+/-5% and 48.3+/-4% compared to TCDD. PCB-167 did not result in significant reduction. In rat cells, only PCB-156 resulted in significant decrease in TCDD-induced AhR-EGFP expression of 35%, suggesting species differences play a role. Our results suggest that purification of MO-PCBs is an essential step in determining accurate REP values, and could very likely lead to lower TEF values than those presently assigned by the WHO.

Animals↗

PubMed2006

Interactions of polybrominated diphenyl ethers with the aryl hydrocarbon receptor pathway.

Polybrominated diphenyl ethers (PBDEs) are brominated flame retardants that have been in use as additives in various consumer products. Structural similarities of PBDEs with other polyhalogenated aromatic hydrocarbons that show affinity for the aryl hydrocarbon receptor (AhR), such as some polychlorinated biphenyls, raised concerns about their possible dioxin-like properties. We studied the ability of environmentally relevant PBDEs (BDE-47, -99, -100, -153, -154, and -183) and the "planar" congener BDE-77 to bind and/or activate the AhR in stably transfected rodent hepatoma cell lines with an AhR-responsive enhanced green fluorescent protein (AhR-EGFP) reporter gene (H1G1.1c3 mouse and H4G1.1c2 rat hepatoma). 7-Ethoxyresorufin-O-deethylation (EROD) was used as a marker for CYP1A1 activity. Dose- and bromination-specific inhibition of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-induced responses was measured by their ability to inhibit the induction of AhR-EGFP expression and EROD activity. Individual exposure to these PBDEs did not result in any increase in induction of AhR-EGFP or CYP1A1 activity. The lower brominated PBDEs showed the strongest inhibitory effect on TCDD-induced activities in both cell lines. While the highest brominated PBDE tested, BDE-183, inhibited EROD activity, it did not affect the induction of AhR-EGFP expression. Similar findings were observed after exposing stably transfected human hepatoma (xenobiotic response element [XRE]-HepG2) cells to these PBDEs, resulting in a small but statically significant agonistic effect on XRE-driven luciferase activity. Co-exposure with TCDD resulted again in antagonistic effects, confirming that the inhibitory effect of these PBDEs on TCDD-induced responses was not only due to direct interaction at receptor level but also at DNA-binding level. This antagonism was confirmed for BDE-99 in HepG2 cells transiently transfected with a Gal4-AhR construct and the corresponding Gal4-Luc reporter gene. In addition, a chromatin immunoprecipitation assay further confirmed that BDE-99 could bind to the AhR and activate the AhR nuclear translocation and dioxin responsive element (DRE) binding in the context of the CYP1A1 promoter. However, the transactivation function of the BDE-99-activated AhR seems to be very weak. These combined results suggest that PBDEs do bind but not activate the AhR-AhR nuclear translocator protein-XRE complex.

Animals↗

PubMed2006

Recent developments in clinimetric instruments.

Assessment of impairment and function is essential in order to monitor joint status and evaluate therapeutic interventions in patients with haemophilia. The improvements in the treatment of haemophilia have required the development of more sensitive tools to detect the more minor dysfunctions that may now be apparent. This paper outlines some of the recent developments in this field. The Haemophilia Joint Health Score (HJHS) provides a systematic and robust measure of joint impairment. The MRI Scoring System has been designed to provide a comprehensive scoring system combining both progressive and additive scales. The Functional Independence Score for Haemophilia (FISH) has been developed to assess performance of functional activities and can be used in conjunction with the Haemophilia Activities List (HAL) which provides a self report measure of function. It is recommended that both measures are evaluated as these tools measure different constructs. Further refinement and testing of the psychometric properties of all of these tools is in progress. More widespread use of these tools will enable the sharing of data across the world so promoting best practice and ultimately enhancing patient care.

Activities of Daily Living↗

PubMed2004

Physical therapy and imaging outcome measures in a haemophilia population treated with factor prophylaxis: current status and future directions.

Routine infusions of factor VIII to prevent bleeding, known as prophylaxis, and other intensive therapies are being more broadly applied to patients with haemophilia. These therapies differ widely in replacement product usage, cost, frequency of venous access and parental effort. In order to address residual issues relating to recommendations, implementation, and evaluations of prophylaxis therapy in persons with haemophila, a multinational working group was formed and called the International Prophylaxis Study Group (IPSG). The group was comprised of haemophilia treaters actively involved in studies of prophylaxis from North America and Europe. Two expert committees, the Physical Therapy (PT) Working Group and the Magnetic Resonance Imaging (MRI) Working Group were organized to critically assess existing tools for assessment of joint outcome. These two committees independently concluded that the WFH Physical Examination Scale (WFH PE Scale) and the WFH X-ray Scale (WFH XR Scale) were inadequately sensitive to detect early changes in joints. New scales were developed based on suggested modifications of the existing scales and called the Haemophilia Joint Health Score (HJHS) and the International MRI Scales. The new scales were piloted. Concordance was measured by the intra-class correlation coefficient of variation. Reliability of the HJHS was excellent with an inter-observer co-efficient of 0.83 and a test-retest value of 0.89. The MRI study was conducted using both Denver and European scoring approaches; inter-reader reliability using the two approaches was 0.88 and 0.87; test-retest reliability was 0.92 and 0.93. These new PT and MRI scales promise to improve outcome assessment in children on early preventive treatment regimens.

Hemophilia A↗

PubMed2003

Heritability of cortisol levels: review and simultaneous analysis of twin studies.

Cortisol has a pivotal role in physical and mental health, but relatively few studies have paid attention to individual differences in cortisol levels and the etiology of these differences, in particular their possible genetic basis. In this article we review the existing literature on the heritability of cortisol levels. Most of the studies, which have been carried out in genetically informative samples, lack methodological consistency with regard to frequency and timing of sample collection. The circadian rhythm in cortisol levels was often not taken into account. A power analysis shows that none of these studies used adequate sample sizes to distinguish genetic from shared environmental influences as a cause for familial aggregation. Results of a simultaneous analysis of 5 comparable twin studies suggest a heritability of 62%. Hence, we conclude that, to understand the contribution of genetic and (shared) environmental influences to variation in basal cortisol levels, future studies should be designed more rigorously with strict collection and sampling protocols, sufficient sample size and repeated measures across multiple days.

Circadian Rhythm↗

PubMed1999

Effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin or 2,2',4,4',5,5'-hexachlorobiphenyl on vitamin K-dependent blood coagulation in male and female WAG/Rij-rats.

Newborns are susceptible to hemorrhages (hemorrhagic disease of the newborn or HDN) due to vitamin K deficiency. Induction of cytochrome P450 in the fetal liver by maternal anticonvulsant therapy such as phenobarbital or phenytoin is considered to be a major cause. An observed increase in late hemorrhagic disease (LHD) in breast fed neonates gave rise to the hypothesis that PCBs and dioxins, P450-inducing contaminants present in human milk, might effect vitamin K-dependent blood coagulation. This hypothesis was studied in rats. Administration of a single oral dose of 0.003, 0.03, 0.3, 3 or 30 nmol 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) per kg bodyweight or 0.75, 4, 20, 100 or 500 micromol 2,2',4,4',5,5'-hexachlorobiphenyl/kg bw (HxCB) to female and male rats resulted in dose-related reductions of the vitamin K-dependent coagulation factor VII. The highest factor VII reduction in female rats was 44%, observed after TCDD exposure. The Lowest Observed Adverse Effect Level (LOAEL) of TCDD on female factor VII levels was 0.3 nmol/kg bw (96 ng/kg). There was a significant inverse correlation between Factor VII levels and induction of hepatic ethoxyresorufin O-deethylating (EROD) activity, reflecting CYP1A1, and total P450 content. HxCB had no effect on female coagulation factors. In contrast, in male rats only exposure to HxCB, which induces mainly CYP2B1 and 2B2, decreased both coagulation factors dramatically up to 88%. The LOAEL of HxCB on factor VII in male rats was 100 micromol/kg bw (36 mg/kg). In general, effects on coagulation factors in male rats exceeded those in females. In addition, sex-dependent differences of TCDD and HxCB were observed on the hepatic vitamin K cycle enzyme activities in female and male rats. Vitamin K-dependent (gamma-glutamyl carboxylase activity was mainly induced in female rats; 2.3-fold in the highest dose group of TCDD. In male rats only vitamin K 2,3-epoxide reductase (KO-reductase) activity was induced 1.7-fold by the highest dose of HxCB. KO-reductase activity in female rats was also increased by TCDD, however, less pronounced than the carboxylase activity. Concluding, the hepatic vitamin K cycle still functions and is not blocked by TCDD or HxCB, thus explaining the observed reduction in factor VII. Finally, the possible role of P450 in vitamin K deficiency is discussed. Based on these results it is suggested to investigate the possible role of PCBs and dioxin-like compounds in LHD in more detail.

Animals↗

PubMed1998

Effects of some persistent halogenated environmental contaminants on aromatase (CYP19) activity in the human choriocarcinoma cell line JEG-3.

Effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 3,3',4,4',5-pentachlorobiphenyl (PCB126), a technical PCB mixture (Aroclor 1016), and a technical toxaphene mixture (Camphechlor) on aromatase (CYP19) activity were investigated in human choriocarcinoma JEG-3 cells. After 18 h incubation with TCDD, PCB126, Aroclor 1016 or toxaphene, ethoxyresorufin-O-deethylase (EROD), and aromatase activity were determined. To exclude serum effects, incubations were carried out with or without fetal calf serum in the medium. EROD activity was induced by both TCDD and PCB126 in the presence or absence of serum, which indicates that JEG-3 cells are responsive toward dioxin-like chemicals. Neither Aroclor 1016 nor toxaphene affected EROD activity in these cells. Calculated EC50 values for induction of EROD activity were 0.71 and 0.40 nM for TCDD, and 48 and 20 nM for PCB126 in presence or absence of serum, respectively. Incubation with TCDD or PCB126 with or without serum caused a concentration-dependent decrease in the aromatase activity of up to 4.9-fold. Calculated EC50 values for this effect were 52 pM and 13 nM for TCDD, and 75 and 48 nM for PCB126 in the presence and absence of serum, respectively. Aroclor 1016 and toxaphene had no effect on aromatase activity at concentrations up to 1.0 microM for Aroclor 1016 or 3.0 microM for toxaphene. These results show that aromatase activity can be decreased in a concentration dependent way within the same range where EROD activity is increased. In view of these results, possible effects of dioxin-like compounds on estrogen producing and androgen target cells should be studied in more detail.

Aroclors↗

PubMed1998

Toxic equivalency factors (TEFs) for PCBs, PCDDs, PCDFs for humans and wildlife.

An expert meeting was organized by the World Health Organization (WHO) and held in Stockholm on 15-18 June 1997. The objective of this meeting was to derive consensus toxic equivalency factors (TEFs) for polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs) and dioxinlike polychlorinated biphenyls (PCBs) for both human, fish, and wildlife risk assessment. Based on existing literature data, TEFs were (re)evaluated and either revised (mammals) or established (fish and birds). A few mammalian WHO-TEFs were revised, including 1,2,3,7,8-pentachlorinated DD, octachlorinated DD, octachlorinated DF, and PCB 77. These mammalian TEFs are also considered applicable for humans and wild mammalian species. Furthermore, it was concluded that there was insufficient in vivo evidence to continue the use of TEFs for some di-ortho PCBs, as suggested earlier by Ahlborg et al. [Chemosphere 28:1049-1067 (1994)]. In addition, TEFs for fish and birds were determined. The WHO working group attempted to harmonize TEFs across different taxa to the extent possible. However, total synchronization of TEFs was not feasible, as there were orders of a magnitude difference in TEFs between taxa for some compounds. In this respect, the absent or very low response of fish to mono-ortho PCBs is most noticeable compared to mammals and birds. Uncertainties that could compromise the TEF concept were also reviewed, including nonadditive interactions, differences in shape of the dose-response curve, and species responsiveness. In spite of these uncertainties, it was concluded that the TEF concept is still the most plausible and feasible approach for risk assessment of halogenated aromatic hydrocarbons with dioxinlike properties.

Animals↗

PubMed1995

Functional aspects of developmental toxicity of polyhalogenated aromatic hydrocarbons in experimental animals and human infants.

A scientific evaluation was made of functional aspects of developmental toxicity of polychlorinated biphenyls (PCBs), polychlorinated dibenzo-p-dioxins (PCDDs) and polychlorinated dibenzofurans (PCDFs) in experimental animals and in human infants. Persistent neurobehavioral, reproductive and endocrine alterations were observed in experimental animals, following in utero and lactational exposure to PCBs, PCDDs and PCDFs. The lowest observable adverse effect levels (LOAELs) for developmental neurobehavioral and reproduction endpoints, based on body burden of TCDD-toxic equivalents (TEQs) in animals, are within the range of current background human body burdens. Relatively subtle adverse effects on neurobehavioral development and thyroid hormone alterations have also been observed in infants and children exposed to background levels. Exclusive use of the toxic equivalency factor (TEF) approach may underestimate the risk of neurodevelopmental effects, because both Ah receptor dependent and independent mechanisms may be involved in these effects. The use of marker congeners and/or bioassays based on Ah receptor mediated mechanisms are rapid, low cost pre-screening alternatives for expensive and time consuming gas chromatographic-mass spectrometric analysis.

Animals↗

PubMed1995

Subchronic effects of 2,3,7,8-TCDD or PCBs on thyroid hormone metabolism: use in risk assessment.

Effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 3,3',4,4',5-pentachlorobiphenyl (PCB 126), or 2,3,3',4,4',5-hexachlorobiphenyl (PCB 156) on thyroid hormone metabolism were studied in 13-week feeding studies in female Sprague-Dawley rats. The diets were supplemented with the compounds tested at concentrations ranging from 0.2 to 20 micrograms/kg diet for TCDD, 7 to 180 micrograms/kg diet for PCB 126, or 1.2 to 12 mg/kg diet for PCB 156, respectively. Significant correlations were found for all three compounds between reductions in plasma total thyroxine (TT4) levels and inductions of the microsomal phase II enzyme UDP-glucuronosyltransferase by using T4 as a substrate (T4UGT). Furthermore, the coinduction of certain phase I and II isozymes, i.c., cytochrome P450 1A1 (CYP1A1) and UGT1A1, by these compounds, clearly suggests the involvement of an Ah receptor-mediated mechanism in the disturbance of thyroid hormone metabolism by these polyhalogenated aromatic compounds. These results provide a mechanistic base for the use of certain effects on thyroid hormone metabolism by polyhalogenated aromatic compounds in risk assessment. By using these effects, potencies of PCB 126 and PCB 156 relative to TCDD ranged from 0.008 to 0.1 for PCB 126, and from 0.00007 to 0.004 for PCB 156, respectively. These values correspond very well with relative potencies of PCB 126 and PCB 156 by using some other well-known Ah receptor-mediated toxic and biochemical parameters.

Animals↗

PubMed1995

Induction of cytochrome P450 isoenzymes after toxicokinetic interactions between 2,3,7,8-tetrachlorodibenzo-p-dioxin and 2,2',4,4',5,5'-hexachlorobiphenyl in the liver of the mouse.

One group of male C57BL/6J mice received a single oral dose of 1 nmol 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)/kg. Six other groups received single oral doses of 100, 300, or 1000 mumol 2,2',4,4',5,5'-hexachlorobiphenyl (HxCB)/kg, alone or in combination with 1 nmol/kg TCDD. Liver deposition of both compounds was studied at Day 3 after dosage. Hepatic CYP1A1 and CYP1A2 protein levels and related 7-ethoxyresorufin-O-deethylation (EROD) and acetanilide 4-hydroxylation (ACOH) activities were also studied. A significant increase in the hepatic deposition of TCDD was observed in all three mixed dose groups but TCDD did not influence hepatic HxCB deposition. TCDD did increase both CYP1A1 and CYP1A2 protein levels. In the HxCB-treated groups, CYP1A2 levels were also increased in a dose-dependent way but CYP1A1 levels were not increased. CYP1A2 activities (ACOH), but not protein levels, in the TCDD groups cotreated with HxCB were higher than those in the group treated with TCDD alone. CYP1A1-dependent EROD activity and CYP1A2-dependent ACOH activity were induced in all treated dose groups. It is concluded that the present results do not confirm a direct role of CYP1A2 induction in the increase of hepatic TCDD levels by HxCB cotreatment in the mixed HxCB/TCDD dose groups. However, in this aspect, the discrepancy between CYP1A2 activities and protein levels remains to be explained.

Animals↗

PubMed1995

Subchronic dose-response study of 2,3,7,8-tetrachlorodibenzo-p-dioxin in female Sprague-Dawley rats.

Toxic and biochemical potencies of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) were studied in a 13-week feeding study in female Sprague-Dawley rats. The diets were supplemented with 0, 0.2, 0.4, 0.7, 5, or 20 micrograms TCDD/kg diet. The estimated daily intakes were calculated to be 0, 14, 26, 47, 320, or 1024 ng TCDD/kg body wt/day. At the end of the study, TCDD concentrations were measured in liver and adipose tissue. The lowest estimated daily intake that caused an increase in liver weight was 320 ng TCDD/kg/day, while an intake of 47 ng TCDD/kg/day resulted in a decrease in plasma thyroid hormone concentrations and a decrease in body weight gain. Decreases in relative thymus weights, loss of hepatic retinoids, and induction of CYP1A1 and CYP1A2 activities were already found at 14 ng/kg/day, the lowest dose used. Therefore, 95% confidence limits for the no-effect levels (CNELs) were calculated from the corresponding dose-response relationships by using sigmoidal curve fittings (Hill, Weibull, and a Logistic model) and a probability level of p < 0.05. For increases in CYP1A1 and CYP1A2 activities, the right critical values for the CNELs ranged from 0.7 to 4 ng TCDD/kg/day (Hill and Weibull). Based on hepatic TCDD residue levels, these right critical values for the CNELs ranged from 0.06 to 0.4 ng TCDD/g liver (wet weight) (Hill and Weibull). The CNELs in this study agree very well with the no-observed-adverse-effects levels as reported before in chronic, carcinogenicity, and reproductive studies with rats and TCDD, i.e., 1 ng/kg/day.

Animals↗

PubMed1995

The effects of 2,2',4,4',5,5'-hexachlorobiphenyl cotreatment on the disposition of 2,3,7,8-tetrachlorodibenzo-p-dioxin in mice.

Two groups of C57BL/6J mice received a single oral dose of 1 nmol/kg 2,3,7,8-[3H]tetrachlorodibenzo-p-dioxin (TCDD) alone or in combination with 300 mumol/kg 2,2',4,4',5,5'-hexachlorobiphenyl (HxCB). The disposition of TCDD in liver, fat, skin, spleen, lung and blood was studied at days 3, 7, 13 and 34 after dosage. HxCB cotreatment increased hepatic TCDD levels and, consequently, significant increases of the liver/fat distribution ratio were observed. HxCB cotreatment did not significantly affect TCDD levels in fat or other tissues. The elimination rates of TCDD were not influenced by HxCB cotreatment in any of the tissues. It is concluded that HxCB cotreatment alters the body distribution of TCDD in mice but does not influence the elimination rate of TCDD.

Adipose Tissue↗

PubMed1995

Hyperhomocysteinaemia and endothelial dysfunction in young patients with peripheral arterial occlusive disease.

Hyperhomocysteinaemia, defined as an abnormally high plasma homocysteine concentration after an oral methionine load, is common in young (< or = 50 years) patients with peripheral arterial occlusive disease. It is thought to predispose to atherosclerosis by injuring the vascular endothelium. Treatment with pyridoxine and/or folic acid may lower plasma homocysteine levels. In mildly hyperhomocysteinaemic patients with peripheral arterial occlusive disease, we studied the effect of daily treatment with pyridoxine (250 mg) plus folic acid (5 mg) on homocysteine metabolism (i.e. plasma concentrations in the fasting state and after methionine loading, in 48 patients) and on endothelial function (in 18 patients). Endothelial function was estimated as the plasma concentrations of the endothelium-derived proteins, von Willebrand factor (vWF), thrombomodulin (TM), and tissue-type plasminogen activator (tPA). At baseline, fasting homocysteine levels were above normal in 24 of the 48 patients (50%); post-load levels, by definition, were above normal in 100% of patients. After 12 weeks of treatment, fasting and post-load levels were normal in 98 and 100% of patients, respectively. Endothelial function was assessed in 18 patients who completed 1 year of treatment. At baseline, median vWF (235%) and TM (57.1 ng mL-1) levels were above normal. At follow-up, vWF levels had decreased to 170% (P = 0.01) and TM levels had decreased to 49 ng mL-1 (P = 0.04). tPA levels were normal at baseline and did not change. Endothelial dysfunction is present in young patients with peripheral arterial occlusive disease and hyperhomocysteinaemia. Pyridoxine plus folic acid treatment normalizes homocysteine metabolism in virtually all patients, and appears to ameliorate endothelial dysfunction.

Adult↗

PubMed1994

Comparative genomic hybridization as a tool to define two distinct chromosome 12-derived amplification units in well-differentiated liposarcomas.

Well-differentiated liposarcomas (WDLPS) are frequently characterized by a near-diploid karyotype with supernumerary ring and/or giant rod-shaped marker chromosomes. We have shown, using fluorescence in situ hybridization (FISH) and molecular strategies, that these markers contain chromosome 12-derived sequences. Here we report the analysis of six WDLPS for the presence of amplified DNA segments by means of the recently developed comparative genomic hybridization (CGH) strategy. Two distinct chromosome 12-derived amplification units could be identified in all tumors examined, one located in the q14-q15 region as expected, the second unexpectedly mapping to q21.3-q22. Our results indicate that the concerted amplification of these two distinct regions on the long arm of chromosome 12 may be a consistent characteristic of WDLPS. These amplifications are most likely directly related to the presence of supernumerary ring and/or giant marker chromosomes in this group of soft tissue tumors.

Cell Differentiation↗

PubMed1994

Toxic potency of 2,3,3',4,4',5-hexachlorobiphenyl relative to and in combination with 2,3,7,8-tetrachlorodibenzo-p-dioxin in a subchronic feeding study in the rat.

Interactive effects on toxicity and biochemical parameters were studied between 2,3,3',4,4',5-hexachlorobiphenyl (PCB 156) and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in a 13-week feeding study of female Sprague-Dawley rats. The diets were supplemented with PCB 156 (1.2, 6, or 12 mg/kg), with TCDD (5 micrograms/kg), or with combinations of both compounds. Estimated daily intake of 365 micrograms/kg body wt/day (6 mg/kg diet group) of PCB 156 caused a decrease in body weight gain, thymic atrophy, liver enlargement, a loss in hepatic retinoids, induction of CYP2B activity, and a decrease in plasma thyroxine concentrations. At an estimated daily intake of 81 micrograms PCB 156/kg body wt/day CYP1A1 and CYP1A2 activities were induced. Compared to a simultaneous subchronic feeding study with TCDD a toxic equivalency factor (TEF) between 0.00004 and 0.001 was estimated for PCB 156 with respect to the mentioned effects. Antagonistic effects were found between TCDD and PCB 156 for CYP2B activity and hepatic retinol levels. These effects concurred with a PCB 156 dose-dependent decrease in hepatic TCDD levels. Hepatic PCB 156 levels were found to be increased at the 1.2-mg PCB 156/kg dose group in coadministration with TCDD. In conclusion, at least part of the antagonistic effects between PCB 156 and TCDD observed have a toxico-kinetic base. Furthermore, the magnitude of the antagonistic effects may be neglected in comparison with the uncertainty in the TEF value. Therefore, the interactive effects found between PCB 156 and TCDD may have no implications for the additivity of the TEF concept.

Animals↗

PubMed1994

Toxic potency of 3,3',4,4',5-pentachlorobiphenyl relative to and in combination with 2,3,7,8-tetrachlorodibenzo-p-dioxin in a subchronic feeding study in the rat.

Toxic and biochemical potencies of 3,3',4,4',5-pentachlorobiphenyl (PCB 126) were studied relative to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in a 13-week feeding study in female Sprague-Dawley rats. To study possible interactive effects the combinations of both compounds were administered. The diets were supplemented with PCB 126 (7, 50, or 180 micrograms/kg diet), with TCDD (0.4 or 5 micrograms/kg diet), or with combinations of both compounds. An estimated daily intake of 0.47 micrograms PCB 126/kg body weight/day caused thymic atrophy, a dramatic loss in hepatic retinoids, and a marked induction in CYP1A1 and CYP1A2 activities. At a daily intake of 3.18 micrograms PCB 126/kg body weight/day a decrease in body weight gain, liver enlargement, and plasma thyroid hormone concentrations occurred. Based on a simultaneous subchronic feeding study with TCDD, a toxic equivalency factor range between 0.01 and 0.1 was estimated for PCB 126 for the mentioned effects. Antagonism was found between TCDD and PCB 126 for hepatic retinol levels and CYP1A2 activity. At the same time, TCDD and PCB 126 liver residue levels were slightly decreased by coadministration. However, these antagonistic effects occurred at maximum induction levels of CYP1A1 and CYP1A2, which are not likely to occur at levels relevant for humans.

Acetanilides↗

PubMed1994

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

This article reviews the present state of the art regarding the toxicokinetics and metabolism of polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs). The absorption, body distribution, and metabolism can vary greatly between species and also may depend on the congener and dose. In biota, the 2,3,7,8-substituted PCDDs and PCDFs are almost exclusively retained in all tissue types, preferably liver and fat. This selective tissue retention and bioaccumulation are caused by a reduced rate of biotransformation and subsequent elimination of congeners with chlorine substitution at the 2,3,7, and 8 positions. 2,3,7,8-Substituted PCDDs and PCDFs also have the greatest toxic and biological activity and affinity for the cytosolic arylhydrocarbon (Ah)-receptor protein. The parent compound is the causal agent for Ah-receptor-mediated toxic and biological effects, with metabolism and subsequent elimination of 2,3,7,8- substituted congeners representing a detoxification process. Congener-specific affinity of PCDDs and PCDFs for the Ah-receptor, the genetic events following receptor binding, and toxicokinetics are factors that contribute to the relative in vivo potency of an individual PCDD or PCDF in a given species. Limited human data indicate that marked species differences exist in the toxicokinetics of these compounds. Thus, human risk assessment for PCDDs and PCDFs needs to consider species-, congener-, and dose-specific toxicokinetic data. In addition, exposure to complex mixtures, including PCBs, has the potential to alter the toxicokinetics of individual compounds. These alterations in toxicokinetics may be involved in some of the nonadditive toxic or biological effects that are observed after exposure to mixtures of PCDDs or PCDFs with PCBs.

Animals↗