Hepatic Microsomal Ethoxyresorufin O-deethylase Activity Research Articles

Catalytic and immunochemical detection of hepatic and extrahepatic microsomal cytochrome P450 1A1 (CYP1A1) in white-sided dolphin ( Lagenorhynchus acutus)

We have characterized microsomal systems and measured the levels of microsomal cytochrome P450 1A1 (CYP1A1) and ethoxyresorufin-O-deethylase (EROD) activity in multiple internal organs of male and female white-sided dolphin ( Lagenorhynchus acutus) from the northwest Atlantic Ocean. Internal organs were sampled within 24 h of death, sometimes in a period of hours, collection times which are significantly less than usually seen for marine mammals. Tissue autolysis, as assessed by histological analysis of liver, was minimal to none in all individuals. Total P420 did not correlate with time from death to sampling, suggesting that it is a poor indicator of P450 degradation in cetacean tissues where perfusion is not practical. The total hepatic microsomal P450 content, cytochrome b5 content, and NADPH-cytochrome c (P450) reductase (CPR) activity averaged 0.29 nmol mg −1, 0.12 nmol mg −1, and 238 nmol mg −1 min −1, respectively. Microsomal CPR activity in liver was higher than that in lung and kidney, and was higher than that reported in liver of most other cetacean species. Immunodetected CYP1A1 content was low in all organs, less than 3 pmoles CYP1A equivalents mg −1. EROD activity ranged from 9 to 376 pmoles mg −1 min −1 and was greater in liver than in other tissues. Hepatic microsomal EROD activity and CYP1A1 content did not correlate. However, hepatic EROD activity, but not CYP1A1 protein content, was well correlated with both total PCB and Σmono- ortho PCB concentrations in blubber. Length, as a proxy for age, did not correlate with hepatic EROD activity or CYP1A1 protein levels, and sex did not influence the relationship between EROD and contaminant concentrations. We cannot easily control for the extent of tissue degradation in cetacean studies nor do we have a complete history of these animals. Therefore, other factors such as degradation or hormonal state may have a role in the observed relationships. Yet, as in other mammals, hepatic tissues appear to be a major site of CYP1A1 expression and probably of biotransformation of CYP1A substrates in white-sided dolphin. The expression of an EROD catalyst in liver likely reflects induction by PCBs, but the P450 enzyme catalyzing hepatic EROD activity in these whales may not be CYP1A1.

Biomarker response and health of polychlorinated biphenyl‐ and chlordane‐contaminated paddlefish from the Ohio River Basin, USA

AbstractFifty paddlefish (Polyodon spathula) collected from two sites on the Ohio River and from one site on the Cumberland River, USA, were examined to determine gonad polychlorinated biphenyl (PCB) and chlordane concentrations, amounts of plasma sex steroids (testosterone and estradiol), hepatic microsomal ethoxyresorufin‐O‐deethylase (EROD) activity, and the presence of immunoreactive cytochrome P450 1A (CYP1A) protein. Percent hatch and liver, spleen, and kidney histology were also determined. Gonad PCB and chlordane concentrations were significantly higher in Ohio River paddlefish than in Cumberland River paddlefish. Gonad PCB and chlordane concentration and gonad percent lipid were correlated in Ohio River paddlefish. Five of 10 Ohio River egg samples exceeded the Food and Drug Administration's action limit for chlordane (0.30 μg/g). Polychlorinated biphenyl congener‐specific analysis detected predominantly the tetra‐, penta‐, and hexachlorobiphenyls in paddlefish testes. Plasma testosterone levels were significantly lower in males collected from the upper Ohio River site than those collected from the lower part of the river. There was no measurable hepatic microsomal EROD activity in any of the 50 paddlefish collected from the three sites. Western blotting analysis confirmed that a rabbit antitrout CYP1A1 IgG antibody did not recognize a CYP1A protein in paddlefish liver microsomes. Percent hatch was not significantly different in eggs collected from the Cumberland (88–96%) and Ohio Rivers (90–95%). Histological analysis of liver, spleen, and kidney detected the presence of hepatic steatosis and hemosiderosis, splenic lymphoid cell depletion, and hyperplasia of interrenal and chromaffin tissues. Immunosuppression, hepatic metabolic disorders, and altered neuroendocrine function may be occurring in Ohio River paddlefish. Results presented here suggest that organochlorine exposure may be jeopardizing the long‐term health of Ohio River paddlefish and that additional investigation of contaminant effects on immune system function and hormone levels in paddlefish is warranted.

Toxicity of 2,4,4'-trichlorobiphenyl in rats following 90-day dietary exposure.

The toxicity of 2,4,4'-trichlorobiphenyl (PCB 28) was investigated in rats after a 90-d dietary exposure. Groups of 10 male and 10 female weanling Sprague-Dawley rats were administered PCB 28 in the diet at 0, 0.05, 0.50, 5.0, or 50.0 ppm for 13 wk. Growth rate and food consumption were not affected by treatment, and no clinical signs of toxicity were observed. Mottled liver was noted in both control and PCB-treated males, but was found with increased incidence in the highest treatment group. Increased urinary ascorbic acid and hepatic microsomal ethoxyresorufin O-deethylase activity were observed in the 50.0 ppm group of both sexes. The vitamin A content in liver, lung, and kidney was not significantly affected by treatment. Analysis of brain biogenic amines showed a decreased dopamine concentration in the substantia nigra region of female rats receiving 0.5 ppm PCB 28 and higher doses. Female rats appeared to be more sensitive than males to the neurochemical effects of PCB 28. Dose-dependent histologic changes were observed in the thyroid and liver, with biologically significant changes occurring at 5.0 ppm and above. Based on these data, the no observable-adverse-effect level (NOAEL) for this PCB congener was considered to be 0.5 ppm in diet or 36 micrograms/kg body weight/d.

Persistent Alterations in Regional Brain Glial Fibrillary Acidic Protein and Synaptophysin Levels Following Pre- and Postnatal Polychlorinated Biphenyl Exposure

Pregnant Wistar WU rats were exposed to 0, 5, and 25 mg of the commercial polychlorinated biphenyl (PCB) mixture Aroclor 1254 per kilogram of body weight on Days 10 to 16 of gestation. Pregnant rats were sacrificed on Gestation Day 20 to observe effects on fetal body and brain weights. Male and female offspring were sacrificed on Postnatal Days 21 and 90 (PND21 and PND90, respectively) and examined for treatment-related effects on neurochemical parameters. The concentrations of the neuronal and glial cell markers, synaptophysin and glial fibrillary acidic protein (GFAP), were measured in diverse brain regions from the offspring using immunochemical techniques. The level of calcineurin (a calmodulin-regulated protein phosphatase) activity was measured in cerebellar homogenates. In addition, ethoxyresorufinO-deethylase (EROD) activity was determined in hepatic microsomes as a measure of a well-characterized response to PCB exposure in experimental animals. The major alterations of GFAP levels following maternal PCB treatment were significant increases in the lateral olfactory tract (LOT) and the cerebellum (CB) and significant decreases in the brain stem (BS) of the offspring on PND21 and 90. Synaptophysin levels were significantly decreased relative to controls in the LOT, prefrontal cortex, and striatum of the offspring on PND90. In the BS, synaptophysin levels were significantly decreased relative to controls in male and female weanlings on PND21 and males on PND90; however, significant increases were observed in the BS of females on PND90. No effect of maternal PCB treatment was observed on levels of GFAP and synaptophysin in the dorsal hippocampus on PND21 and 90. Due to analytical restrictions statistical comparisons of GFAP levels were limited to examining the effect of maternal PCB treatment per brain region per sex per time point. Calcineurin activity was decreased in the female CB on PND21, but a significant increase in activity was observed in the female CB on PND90. No effect of maternal PCB treatment was observed on the cerebellar calcineurin activity in male offspring on PND21 and 90. EROD activity was highly induced in maternal microsomes from both PCB treatment groups, but only slightly induced in fetal hepatic microsomes. On PND21 weanling hepatic microsomal EROD activity was highly induced following gestational and lactational PCB exposure; however, on PND90 EROD activity was unaffected by maternal PCB treatment in male offspring and significantly decreased in female offspring. The results of the present study indicate that gestational and lactational exposure to the commercial PCB mixture results in long-term alterations in a neuronal and glial cell markers in specific brain regions of rats. These marker proteins may be useful for determining the strucure–activity relationships in PCB-induced developmental neurotoxicity.

Biological effects of polychlorinated dibenzo‐p‐dioxins, dibenzofurans, and biphenyls in double‐crested cormorant chicks (phalacrocorax auritus)

The present project assessed the effect of environmental contamination with polychlorinated dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), and biphenyls (PCBs) on hepatic microsomal ethoxyresorufin O-deethylase (EROD) activities and morphological parameters in matched double-crested cormorant (Phalacrocorax auritus) hatchlings from egg clutches chosen for chemical analysis. Double-crested cormorant eggs were collected from five colonies across Canada, with differing levels of contamination. Levels of contamination expressed in sum of 2,3,7,8-tetrachlorodibenzo-p-dioxin-toxic equivalents (TCDD-toxic equivalents or TEQ, ng/kg egg; mean +/- SEM) were: Saskatchewan, 250 +/- 50; Chain Islands, 672 +/- 73; Christy Islet, 276 +/- 14; Crofton, 131, n = 1; and Lake Ontario, 1606 +/- 118. In the hatchlings, hepatic EROD activities (pmol/min/mg protein; mean +/- SEM) were: Saskatchewan, 283 +/- 42; Chain Islands, 516 +/- 98; Christy Islet, 564 +/- 91; Crofton, 391 +/- 52; and Lake Ontario, 2250 +/- 156. Hepatic microsomal EROD activity (pmol/min/mg protein) regressed positively on TEQ (r2 = .69; p < .00005; n = 25). Yolk weight (g) regressed negatively on TEQ (r2 = .44; p = .00005). Wing length (mm) regressed negatively on PCB-169 (r2 = .28; p = .007). Monospecific antibodies raised against rat cytochrome P-450 1A1 recognized a protein in the hepatic microsomes of the double-crested cormorant, and also in those of the great blue heron (Ardea herodias), using immunoblotting. The intensity of the stained band increased with increased EROD activity, supporting the assumption that ethoxyresorufin is a suitable substrate for avian cytochrome P-450 1A1. These results validate the use of avian hepatic microsomal EROD activity as an index of cytochrome P-450 1A1 induction by environmental levels of polychlorinated aromatic hydrocarbons and as a useful screening tool to determine the extent of exposure to such chemicals. Furthermore, the induction of cytochrome P-450 1A1 observed in the cormorant indicates that the Ah receptor-mediated process, by which TCDD and related chemicals exert many of their toxicities, has been activated.

Immunosuppressive effects of highly chlorinated biphenyls and diphenyl ethers on T-cell dependent and independent antigens in mice

The dose-dependent effects of 2,2′,3,3′,4,4′,5,5′,6-nonachlorobiphenyl (nonaCB), 2,2′,3,3′,4,4′,5,6,6′-nonaCB, 2,2′,3,3′,4,5,5′6,6′-nonaCB and decaCB on the suppression of the splenic plaque-forming cell (PFC) response to the T-cell-dependent antigen, sheep red blood cells (SRBCs) and the T-cell-independent antigen, trinitrophenyl-lipopoccharide (TNP-LPS), were determined in genetically inbred mice. In addition, the induction of hepatic microsomal ethoxyresorufin O-deethylase (EROD) activity was also measured. The highly chlorinated biphenyls suppressed the splenic PFC response to SRBCs in C57BL/6 and DBA/2 mice and were relatively more active in the former strain. The C57BL/6 mice are more responsive to aryl hydrocarbon (Ah) receptor agonists than DBA/2 mice and these data support a possible role for the Ah receptor in mediating this response. However, previous studies with polychlorinated biphenyls (PCBs) indicate that congeners with 3 or 4 ortho-chloro substituents are inactive as Ah receptor agonists and this was consistent with the minimal induction of hepatic microsomal EROD activity by the highly chlorinated biphenyls in both strains of mice. Thus, the results suggest that the inhibition of the splenic PFC response to SRBCs observed in this study was primarily an Ah receptor-independent response. Some of the highly chlorinated diphyenyl ethers namely decachlorodiphenyl ether and 2,2′,3,3′,4,4′,5,6,6′-nonachlorodiphenyl ether, inhibited the antigenic response to TNP-LPS in C57 BL/6 mice. The results indicate that the suppression of the TNP-LPS-mediated immune response may be a more reliable indicator of the Ah receptor-dependent immunotoxicity of halogenated hydrocarbons.

Immunotoxic potencies of polychlorinated biphenyl (PCB), dibenzofuran (PCDF) and dibenzo- p-dioxin (PCDD) congeners in C57BL/6 and DBA/2 mice

The dose-dependent effects of a single acute exposure of 2,3,7,8-tetrachlorodibenzo- p-dioxin (TCDD), 2,3,4,7,8-pentachlorodibenzofuran (PeCDF), 1,2,3,7,9-PeCDF, 1,3,6,8-tetrachlorodibenzofuran (TCDF), 3,3′,4,4′,5-pentachlorobiphenyl (pentaCB), and 3,3′,4,4′,5,5′-hexaCB on the suppression of the splenic plaque-forming cell (PFC) response to the T-cell-independent antigen trinitrophenyl-lipopolysaccharide were determined in C57BL/6 and DBA/2 mice. In addition, the induction of hepatic microsomal ethoxyresorufin O-deethylase (EROD) activity was also measured in these animals. 2,3,7,8-TCDD and 2,3,4,7,8-PeCDF were the most immunotoxic congeners in both strains of mice and with the exception of the latter congener, the ED 50 values for each compound were lower in the C57BL/6 than the DBA/2 mice. 2,3,7,8-TCDD induced hepatic microsomal EROD activity in both strains of mice whereas the other congeners were considerably less active or inactive as inducers. The results of this study demonstrated that for the halogenated aromatic hydrocarbons the immunotoxic response was a more sensitive indicator of exposure than the induction of CYP1A1 activity. The rank order for the immunotoxic potencies of the chlorinated aromatic compounds used in this study was 2,3,7,8-TCDD ≈ 2,3,4,7,8-PeCDF > 3,3′,4,4′,5-pentaCB ≈ 3,3′,4,4′,5,5′-hexaCB > 1,2,3,7,9-PeCDF > 1,3,6,8-TCDF. The order of activity for these congeners was similar for other Ah receptor-mediated responses and these results coupled with the differential responsiveness of the C57BL/6 and DBA/2 mice confirms the role of aryl hydrocarbon (Ah) receptor in mediating the suppression of this T-cell-independent response.

The effect of 6-nitro-1,3,8-trichlorodibenzofuran as a partial estrogen in the female rat uterus

Administration of 6-nitro-1,3,8-trichlorodibenzofuran (6-NCDF) caused a dose- and time-dependent increase in uterine wet weight and cytosolic and nuclear estrogen receptor (ER) and progesterone receptor (PR) levels in immature female Sprague-Dawley rats. These estrogenic effects persisted for up to 96 or 144 hr after initial administration of 6-NCDF and could be observed at a dose as low as 2 μmol/kg. In contrast, 6-NCDF (25 μmol/kg) did not increase rat uterine peroxidase activity or epidermal growth factor (EGF) receptor binding activity. 2,3,7,8-Tetrachlorodibenzo- p-dioxin (TCDD), which exhibits a broad spectrum of antiestrogenic effects in the female rat uterus, inhibited the 17β-estradiol-induced increase in uterine wet weights, cytosolic and nuclear ER and PR levels, peroxidase activity, and EGF receptor binding activity. In contrast, 2,3,7,8-TCDD inhibited the uterotropic effects caused by 6-NCDF but did not affect the 6-NCDF-induced uterine ER and PR levels. 6-NCDF is a weak inducer of hepatic microsomal ethoxyresorufin O-deethylase activity and competitively binds to the aryl hydrocarbon (Ah) receptor but not the PR or ER. Thus both 6-NCDF and 2,3,7,8-TCDD, two ligands which bind to the Ah receptor, exhibit both partial estrogenic and antiestrogenic properties and serve as useful models for delineating the complex biochemical interactions between the ER and Ah receptor signal transduction pathways.

Indium selectively increases the cytochrome P-450 dependent O-dealkylation of coumarin derivatives in male mice

Indium pretreatment of rats and mice has been reported to decrease the concentration of cytochrome P-450, thereby reducing the activity of some cytochrome P-450 dependent enzymatic reactions. The present study reveals that pretreatment of C57Bl/6JHan mice of both sexes with one s.c. dose of 120 mg of In2(SO4)3.5 H2O per kg of body weight decreases the concentration of cytochrome P-450 to about 65% of control levels. Neither cytochrome b5 nor NADPH-cytochrome P-450 reductase is affected. Hepatic microsomal ethoxyresorufin O-deethylase activity declines to about 75% of control values. In contrast, with coumarin substrates, a sex dependence in the direction of change is observed: in female mice indium decreases the activity to about 75%, whereas in males it enhances the activity to 140%. Moreover, with 7-(methoxy-14C)coumarin as substrate, indium-pretreated male mice exhale about 180% and females about 65% of 14CO2 compared to the corresponding controls. A close correlation between the in vivo and in vitro effects of indium on the metabolism of the coumarin derivatives is suggested. After isolation and purification of cytochrome P-450, SDS-PAGE indicates in indium-pretreated male mice an intensification of a 48.5 kDa protein band which is decreased in females. Immunological studies using antibodies raised against control female cytochrome P-450 show cross reactivity among all microsomes used in these experiments. High percentages of inhibition occur in microsomes with high molecular activity towards coumarin derivatives. The in vitro kinetics of antibody-inhibited O-deethylation of 7-ethoxycoumarin seems to obey a non- or partial-competitive type of inhibition. Indium pretreatment of mice produces sex-dependent effects on the metabolism of coumarin derivatives.

Maternal hepatic effects of 1,2,4,5-tetrachlorobenzene in the rat

1,2,4,5-Tetrachlorobenzene (TCB) is an industrial intermediate used in the production of 2,4,5-trichlorophenoxyacetic acid. This herbicide contains trace quantities of 2,3,7,8-tetrachlorodibenzo- p-dioxin (TCDD). Because of possible maternal hepatic or reproductive effects of this uncharged, low-molecular weight, lipophilic chlorinated benzene 0, 30, 100, 300, and 1000 mg/kg/day of TCB was orally administered to rats on Days 9, 10, 11, 12, and 13 of gestation and the animals were sacrified on Day 14 of pregnancy. No maternal deaths were recorded and body weight gain was significantly decreased only in the 1000 mg/kg/day group. Maternal liver weight, liver to body weight ratio, and hepatic microsomal protein content were unaffected by TCB treatment. Although Day 14 NADPH-cytochrome c reductase activity was not affected, the maternal hepatic microsomal cytochrome P-450 content was significantly increased by administration of 1000 mg/kg/day of TCB. Microsomal N-demethylation of aminopyrine was slightly increased from 2.4 to 3.4 and 3.5 nmole/mg protein/min at doses of 300 and 1000 mg/kg TCB. However, maternal hepatic microsomal ethoxyresorufin O-deethylase activity was greatly increased from 14 to 30, 40, 50, and 49 pmole/mg protein/min in pregnant rats administered 0, 30, 100, 300, and 1000 mg/kg/day TCB. The microsomal rates of p-nitrophenol and phenolphthalein glucuronidation in vitro were not increased by TCB administration. The maternal hepatic microsomal enzyme induction observed after TCB administration to pregnant rats suggests the presence both cytochrome P-450 and P-448 inducers in the sample of 1,2,4,5-tetrachlorobenzene used.

Maternal hepatic and embryonic effects of 1,2,3,4-tetrachlorobenzene in the rat

To assess possible maternal hepatic and reproductive effects of this uncharged, low molecular weight, lipophilic chlorinated benzene 0, 100, 300 and 1000 mg/kg/day of 1,2,3,4-tetrachlorobenzene (TCB) was orally administered to pregnant rats on days 9–13 of gestation and the animals were killed on day 14 of pregnancy. Phenobarbital and ß-naphthoflavone were administered to other pregnant rats as positive hepatic controls. Maternal mortality ( sol7 19 rats ) was increased and body weight gain was greatly decreased in the 1000 mg/kg/day TCB group. Liver to body weight ratio and hepatic microsomal protein content were unaffected by any TCB treatment. On day 14 maternal NADPH-cytochrome c reductase activity was increased at 1000 mg/kg/day, while the maternal hepatic microsomal cytochrome P-450 content was significantly induced by both 300 and 1000 mg/kg/day of TCB. Microsomal N-demethylation of aminopyrine was increased from 2.6 to 4.0 amd 4.5 nmol/mg protein/min at doses of 300 and 1000 mg/kg TCB, respectively. However, maternal hepatic microsomal ethoxyresorufin O-deethylase activity was not consistently increased by TCB. Hepatic glutathione S-transferase activity towards 1,2-dichloro-4-nitrobenzene was increased only by the 1000 mg/kg/day TCB treatment. The rate of microsomal p-nitrophenol and phenolphthalein glucuronidation was increased by TCB administration. Embryonic growth was adversely affected by TCB treatment. Yolk sac diameter, embryonic crown-rump length, and head length were all decreased by treatment with 300 mg/kg/day TCB. This TCB treatment did not significantly elevate the number of dead or abnormal embryos.