Dependence of the porphyrogenic effect of 2,3,7,8-tetrachlorodibenzo(p)dioxin upon inheritance of aryl hydrocarbon hydroxylase responsiveness

Porphyrin-Induced Protein Oxidation and Aggregation as a Mechanism of Porphyria-Associated Cell Injury

Genetic porphyrias comprise eight diseases caused by defects in the heme biosynthetic pathway that lead to accumulation of heme precursors. Consequences of porphyria include photosensitivity, liver damage and increased risk of hepatocellular carcinoma, and neurovisceral involvement, including seizures. Fluorescent porphyrins that include protoporphyrin-IX, uroporphyrin and coproporphyrin, are photo-reactive; they absorb light energy and are excited to high-energy singlet and triplet states. Decay of the porphyrin excited to ground state releases energy and generates singlet oxygen. Porphyrin-induced oxidative stress is thought to be the major mechanism of porphyrin-mediated tissue damage. Although this explains the acute photosensitivity in most porphyrias, light-induced porphyrin-mediated oxidative stress does not account for the effect of porphyrins on internal organs. Recent findings demonstrate the unique role of fluorescent porphyrins in causing subcellular compartment-selective protein aggregation. Porphyrin-mediated protein aggregation associates with nuclear deformation, cytoplasmic vacuole formation and endoplasmic reticulum dilation. Porphyrin-triggered proteotoxicity is compounded by inhibition of the proteasome due to aggregation of some of its subunits. The ensuing disruption in proteostasis also manifests in cell cycle arrest coupled with aggregation of cell proliferation-related proteins, including PCNA, cdk4 and cyclin B1. Porphyrins bind to native proteins and, in presence of light and oxygen, oxidize several amino acids, particularly methionine. Noncovalent interaction of oxidized proteins with porphyrins leads to formation of protein aggregates. In internal organs, particularly the liver, light-independent porphyrin-mediated protein aggregation occurs after secondary triggers of oxidative stress. Thus, porphyrin-induced protein aggregation provides a novel mechanism for external and internal tissue damage in porphyrias that involve fluorescent porphyrin accumulation.

Porphyria cutanea tarda--when skin meets liver

Porphyria cutanea tarda (PCT) is the most frequent type of porphyria worldwide and results from a catalytic deficiency of uroporphyrinogen decarboxylase (UROD), the fifth enzyme in heme biosynthesis. At least two different types of PCT are currently distinguished: an acquired variant, also referred to as sporadic or type I PCT, in which the enzymatic deficiency is limited to the liver; and an autosomal dominantly inherited form, also known as familial or type II PCT, in which there is a decrease of enzymatic activity in all tissues. The cutaneous findings include increased photosensitivity, skin fragility, blistering, erosions, crusts, and miliae on the sun-exposed areas of the body. Additionally, hyperpigmentation, hypertrichosis, sclerodermoid plaques, and scarring alopecia might be observed. In patients with type I PCT, there is a significant association with liver disease that can be triggered by genetic and environmental factors, such as alcohol abuse, iron overload, haemochromatosis, polychlorinated hydrocarbons, and hepatitis C virus infection. The diagnosis of PCT can be made based on the skin symptoms, a characteristic urinary porphyrin excretion profile, and the detection of isocoproporphyrin in the feces. In red blood cells of individuals with type II PCT, UROD activity is decreased by approximately 50% due to heterozygous mutations in the UROD gene. Here we provide an update on clinical, diagnostic and therapeutic aspects of PCT, a disorder that affects both skin and liver.

Experimental hepatic uroporphyria induced by the diphenyl-ether herbicide fomesafen in male DBA/2 mice

Hepatic uroporphyria can be readily induced by a variety of treatments in mice of the C57BL strains, whereas DBA/2 mice are almost completely resistant. However, feeding of the protoporphyrinogen oxidase-inhibiting herbicide fomesafen (0.25% in the diet for 18 weeks) induced hepatic uroporphyria in male DBA/2N mice (liver porphyrin content up to 150 nmol/g, control animals 1 nmol/g), whereas fomesafen-treated male C57BL/6N mice displayed only a slight elevation of liver porphyrins (approximately 5 nmol/g). The profile of accumulated hepatic porphyrins in fomesafen-treated DBA/2N mice resembled the well-characterised uroporphyria induced by polyhalogenated aromatic hydrocarbons, while histological examination confirmed the presence of uroporphyria-specific cytoplasmic inclusions in the hepatocytes. Uroporphyrinogen decarboxylase activity decreased to about 30% of control values in fomesafen-treated DBA/2N mice; microsomal methoxyresorufin O-dealkylase activity was slightly reduced. The amount of CYP1A1 and CYP1A2 mRNA, as determined by real-time PCR, was not significantly changed; mRNA encoding the housekeeping 5-aminolevulinic acid synthase was elevated 10-fold. Total liver iron was slightly increased. A similar uroporphyria was induced by the herbicide formulation Blazer, containing a structurally related herbicide acifluorfen, when fed to DBA/2N mice at a dose corresponding to 0.25% of acifluorfen in the diet. Since DBA/2 mice are almost completely resistant to all well-characterised porphyrogenic chemicals, the results suggest the possible existence of a yet unknown mechanism of uroporphyria induction, to which the DBA/2 mouse strain is more sensitive than the C57BL strain.

Interspecies differences in cancer susceptibility and toxicity

One of the most complex challenges to the toxicologist represents extrapolation from laboratory animals to humans. In this article, we review interspecies differences in metabolism and toxicity of heterocyclic amines, aflatoxin B1, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), and related compounds, endocrine disrupters, polycyclic aromatic hydrocarbons, tamoxifen, and digitoxin. As far as possible, extrapolations to human toxicity and carcinogenicity are performed. Humans may be more susceptible to the carcinogenic effect of heterocyclic amines than monkeys, rats, and mice. Especially, individuals with high CYP1A2 and 3A4 activities and the rapid acetylator phenotype may be expected to have an increased risk. Striking interspecies variation in susceptibility to aflatoxin B1 carcinogenesis is known, with rats representing the most sensitive and mice the most resistant species, refractory to dietary levels three orders of magnitude higher than rats. An efficient conjugation with glutathione, catalyzed by glutathione S-transferase mYc, confers aflatoxin B1 resistance to mice. Extremely large interspecies differences in TCDD-induced toxicity are known. The guinea pig is the most susceptible mammal known, with an LD50 in the range 1-2 micrograms TCDD/kg, whereas the hamster is the most resistant species with an LD50 greater than 3000 micrograms/kg. A number of experts have pointed out to the fact that humans appear to be less sensitive to TCDD than most laboratory animals. Human exposure to background levels of TCDD is not likely to cause an incremental cancer risk. A clear cause--effect relationship has been shown between environmental endocrine-disrupting contaminants and adverse health effects in wildlife, whereas the effects seem to be less critical for humans. Studies on DNA adduct formation and metabolism of the nonsteroidal antiestrogen tamoxifen indicate that rats and mice are orders of magnitude more susceptible than humans.

Interaction between iron metabolism and 2,3,7,8-tetrachlorodibenzo-p-dioxin in mice with variants of the Ahr gene: a hepatic oxidative mechanism

The binding of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) with the aryl hydrocarbon (AH) receptor and subsequent changes in gene expression have been studied intensively, but the mechanisms by which these lead to toxicity are unclear. We investigated the influence of iron, previously implicated in TCDD-induced hepatic porphyria, in mice with alleles of Ahr that encode receptors with varied affinity for TCDD. The administration of iron to Ahrb-1 C57BL/6J (AH-responsive) mice before a single dose of TCDD (75 micrograms/kg) markedly potentiated not only the hepatic porphyria but also general hepatocellular damage and elevation of plasma hepatic enzymes. The formation of hydroxylated and peroxylated derivatives of uroporphyrins formed from uroporphyrinogen and the induction of a mu-glutathione transferase (GST) were consistent with the operation of an oxidative mechanism. In a comparison of C57BL/6J mice with Ahrb-2 BALB/c (AH-responsive) and Ahrd SWR and DBA/2 (AH-nonresponsive) mice, iron overcame the weak hepatic porphyria and toxicity responses in BALB/c and SWR strains but not in DBA/2. CYP1A isoforms are strongly implicated in the mechanism of porphyria, but activities were lowered by 20-30% with iron treatment, and a comparison of levels between strains did not fully account for the resistance of DBA/2 mice. Studies with the use of gel shift assays and cytosolic aconitase of the capacity of the iron regulatory protein controlling the translation of some iron metabolism proteins showed a significant difference between C57BL/6J and DBA/2 mice after the administration of TCDD. We conclude that iron potentiates both the hepatic porphyria and toxicity of TCDD in susceptible mice in an oxidative process with disturbance of iron regulatory protein capacity. Iron even overcomes the AH-nonresponsive Ahrd allele in the SWR strain but not in DBA/2 mice, which remain resistant.

Sensitivity of CYP1A1 mRNA inducibility by dioxin is the same in Cyp1a2(+/+) wild-type and Cyp1a2(-/-) null mutant mice

In mammals, the induction of experimental porphyria by halogenated aromatic hydrocarbons (HAHs) seems to be influenced by the levels of hepatic CYP1A2. The pharmacokinetics and relative rates of uptake and storage of HAHs in the liver are correlated with hepatic CYP1A2 concentrations. It is possible that these rates of HAH uptake and storage might affect the expression of other HAH-inducible genes. The differential inducibility of liver CYP1A1 mRNA by dioxin was therefore compared in Cyp1a2(+/+) wild-type mice, Cyp1a2(+/-) heterozygotes, and Cyp1a2(-/-) homozygous null mutants. Using doses of dioxin over eight orders of magnitude (from 10[-12] to 10[-4] g/kg), we could detect no differences in the sensitivity of CYP1A1 mRNA inducibility. These data indicate that the complete absence of the microsomal CYP1A2 enzyme has no measurable effect on hepatic expression of the Cyp1a1, gene, the only other known member of the mammalian CYP1A cytochrome P450 subfamily.

Uroporphyria induced by 5-aminolaevulinic acid alone in Ahrd SWR mice

In mice, depression of hepatic uroporphyrinogen decarboxylase (UROD) leading to porphyrin accumulation (uroporphyria) occurs with chlorinated ligands of the aryl hydrocarbon (AH) receptor especially after iron overload. However, in the absence of chlorinated ligands, iron itself will eventually cause uroporphyria, but this response is not associated with the Ahr genotype. These effects are potentiated by administration of the haem precursor 5-aminolaevulinate (ALA). The aim of this study was to investigate the effects of ALA alone. Prolonged administration of 2 mg ALA/mL in the drinking water to SWR mice also led to decarboxylase insufficiency (11% of control) and uroporphyria by 8 weeks, whereas DBA/2 mice did not show reduced enzyme activity. Both strains are considered AH nonresponsive and analysis of the Ahr gene using restriction fragment length polymorphism was consistent with SWR, like DBA/2, possessing the Ahrd allele. Exposure of isolated hepatocytes to ALA (150-500 microM) for up to 48 hr showed a significant accumulation of both uroporphyrin and coproporphyrin in the medium, which for uroporphyrin particularly was significantly greater with SWR than with DBA/2 cells. Basal in vivo CYP1A2 activity, measured as microsomal methoxyresorufin dealkylation, was significantly greater in SWR than in DBA/2 mice (1.3-fold), but it was unclear whether this was sufficient to explain the marked difference in sensitivities of the two strains. Despite SWR mice being AH nonresponsive, uroporphyria and decarboxylase depression after an initial iron overload and ALA for 3 weeks were greatly potentiated by a single dose (100 mg/kg) of hexachlorobenzene (a weak AH ligand). The results demonstrate that there is a genetic difference in mice independent of the Ahr genotype and response to iron, which influences the susceptibility to ALA-induced uroporphyria. Thus chemicals, iron and ALA can act independently, but also together, to cause porphyria in susceptible individuals.

Ah receptor involvement in mediation of pyruvate carboxylase levels and activity in mice given 2,3,7,8-tetrachlorodibenzo-p-dioxin

The arylhydrocarbon receptor (AhR) plays a central role in mediating 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) toxicity in animals. The investigations described here provide evidence that support a role for the AhR in TCDD-mediated pyruvate carboxylase (PC) level/activity reductions in mice. Pyruvate carboxylase plays a pivotal role in gluconeogenesis and in supplying carbon units for the citric acid cycle. Delivered ip in a corn oil carrier, TCDD suppresses PC activity/amount at doses as low as 1 microgram/kg in responsive C57BL/6J(Ahb/b) mice. Corn oil alone injected ip into mice at 4 mL/kg appears to be an inducer that increases the amount and activity of PC. However, TCDD suppresses this induction. In the Ahb/b mouse, PC levels and activity are reduced to 10% of control values at a dose of 75 micrograms/kg. A time-course experiment shows that the PC reductions are apparent within 16 hours post-TCDD exposure. Here we report investigations on the PC/TCDD response using a congenic C57BL/6J(Ahd/d) mouse strain having an AhR with a low affinity for TCDD. If the PC/TCDD response is AhR mediated, the congenic mouse strain (Ahd/d) would require much higher doses of TCDD to suppress PC. In the Ahd/d mice, we observe that an approximately 60-fold increase in TCDD dose is necessary to produce a PC/TCDD effect. We also find that in Ahd/d mice, corn oil does not induce an increase in PC activity/amounts, as reported for Ahb/b mice.

Genetic variation of iron-induced uroporphyria in mice

Iron overload causes inhibition of hepatic uroporphyrinogen decarboxylase (UROD) and uroporphyria in C57BL/10ScSn but not DBA/2 mice [Smith, Cabral, Carthew, Francis and Manson (1989) Int. J. Cancer 43, 492-496]. We have investigated the induction of uroporphyria in 12 inbred strains of mice 25 weeks after iron treatment (600 mg/kg) to determine if there was any correlation with the Ah locus. Under these conditions, inhibition of UROD occurred to varying degrees in Ahd mice (SWR and AKR) as well as nominally Ahb-1 (C57BL/6J, C57BL/10ScSn and C57BL/10-cc) and Ahb-2 strains (BALB/c and C3H/HeJ). Five other Ahb or Ahd strains (C57BL/Ks, A/J, CBA/J, LP and DBA/2) were unaffected. Thus there appeared to be no correlation with the Ah phenotype and this illustrated that some other variable inherited factors are involved. Comparisons between another susceptible strain, A2G, and the congenic A2G-hr/+strain (carrying the recessive hr gene) showed a modulating influence associated with the hr locus. In contrast with individual mice of inbred strains, which showed consistent responses to iron, those of the outbred MF1 strain showed a spectrum of sensitivities as might be expected for a heterogeneic stock. The rate of porphyria development was accelerated by administration of 5-aminolaevulinic acid (5-ALA) in the drinking water, but this did not overcome strain differences. Among four strains the order of susceptibility was SWR > C57BL/10ScSn > C57B1/6J > DBA/2 (the last strain was completely resistant). With degrees of iron loading greater than 600 mg of Fe/kg (1200-1800 mg of Fe/kg) C57BL/10ScSn mice (after 20 weeks) and SWR mice (after 5 weeks which included 4 weeks of 5-ALA treatment) had less inhibition of UROD and a lower uroporphyric response, showing that there was an optimum level of liver iron concentration. Studies on selected microsomal enzyme activities associated with cytochrome P-450 showed no correlation with the propensities of strains to develop porphyria. These activities included the NADPH-dependent oxidation of uroporphyrinogen I to uroporphyrin I.

Developmental and reproductive toxicity of dioxins and related compounds: cross-species comparisons

Developmental toxicity to TCDD-like congeners in fish, birds, and mammals, and reproductive toxicity in mammals are reviewed. In fish and bird species, the developmental lesions observed are species dependent, but any given species responds similarly to different TCDD-like congeners. Developmental toxicity in fish resembles "blue sac disease," whereas structural malformations can occur in at least one bird species. In mammals, developmental toxicity includes decreased growth, structural malformations, functional alterations, and prenatal mortality. At relatively low exposure levels, structural malformations are not common in mammalian species. In contrast, functional alterations are the most sensitive signs of developmental toxicity. These include effects on the male reproductive system and male reproductive behavior in rats, and neurobehavioral effects in monkeys. Human infants exposed during the Yusho and Yu-Cheng episodes, and monkeys and mice exposed perinatally to TCDD developed an ectodermal dysplasia syndrome that includes toxicity to the skin and teeth. Toxicity to the central nervous system in monkey and human infants is a potential part of the ectodermal dysplasia syndrome. Decreases in spermatogenesis and the ability to conceive and carry a pregnancy to term are the most sensitive signs of reproductive toxicity in male and female mammals, respectively.

Comparison of 2,3,7,8-tetrachlorodibenzo-p-dioxin-mediated hepatotoxicity in C57BL/6J and DBA/2J mice

The toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was examined by clinical chemistry and liver histopathology in Ah-responsive C57BL/6J (C57) and Ah-nonresponsive DBA/2J (DBA) mice. Hepatotoxicity was assessed at 1, 3, and 7 d following a single ip injection of TCDD at doses that maximally induce hepatic aryl hydrocarbon hydroxylase (AHH) activity (3 micrograms/kg for C57 and 30 micrograms/kg for DBA mice) and at doses approaching the LD50 (150 micrograms/kg for C57 and 600 micrograms/kg for DBA mice). Histological examination of liver sections was found to be a more sensitive detection method for TCDD-induced hepatic changes than clinical chemistry analyses. Dramatic differences in the development and type of liver injury were observed between TCDD-treated C57 and DBA mice. C57 mice given 3 micrograms TCDD/kg developed mild to moderate hepatic lipid accumulation in the absence of both inflammation and necrosis. Severe fatty change and mild inflammation and necrosis occurred in C57 mice that received 150 micrograms TCDD/kg. In contrast, DBA mice exposed to 30 micrograms TCDD/kg developed hepatocellular necrosis and inflammation without any fatty change. Only slight hepatic lipid accumulation occurred with some necrosis and inflammation in DBA mice given 600 micrograms TCDD/kg. The Ah locus may play a role in determining the sensitivity of C57 mice to the steatotic effects of TCDD.

The effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on the hepatic estrogen and glucocorticoid receptors in congenic strains of Ah responsive and Ah nonresponsive C57BL/6J mice

The present study examines the role of the Ah receptor in the effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on the binding capacity of the hepatic glucocorticoid (GC) and estrogen (E) receptors in female congenic C57BL/6J mice differing only at the Ah (aromatic hydrocarbon responsiveness) locus. The Ah locus is thought to encode the Ah receptor, which regulates the effects of TCDD and related compounds on cytochrome P450IA1 and appears to mediate most of the toxic effects of TCDD. The differences between Ah responsive (Ahb/b) and nonresponsive (Ahd/d) mice appear to reflect differences in the affinity of the Ah receptor in the two strains for ligands such as TCDD. Administration of a single oral dose of TCDD (30 micrograms/kg) to Ahb/b mice produced approximately a 30% decrease in the maximum binding capacities of both the hepatic GC and E receptors, as well as 50-fold induction of a P450IA1-mediated enzymatic activity, ethoxyresorufin-O-deethylase (EROD). Tyrosine aminotransferase (TAT) activity, which is mediated by the GC receptor, was also decreased approximately 30% by TCDD. Dose-response curves indicated that Ah responsive mice are 10-fold more sensitive to induction of EROD than Ah nonresponsive mice (ED50 1.6 vs 15 micrograms/kg), as would be expected for an effect mediated by the Ah receptor. Dose-response curves also indicated that there was a statistical difference in the responsiveness of the hepatic E receptor to TCDD in the two congenic strains of mice (p less than 0.01). Surprisingly, no significant differences in the dose-response curves for the effect of TCDD on hepatic GC receptor binding or TAT activity were observed in the two strains of mice in two separate experiments. These results indicate that the Ah receptor regulates the effects of TCDD on the binding of estrogen to the hepatic estrogen receptor, but suggest that the decrease in the binding capacity of the hepatic GC receptor does not appear to be mediated directly by the Ah locus.

Chlorinated biphenyls induce cytochrome P450IA2 and uroporphyrin accumulation in cultures of mouse hepatocytes

Previous enzymatic and immunological studies from this laboratory have indicated a critical role for cytochrome P450IA2-catalyzed uroporphyrinogen oxidation in the development of uroporphyria caused by halogenated aromatic hydrocarbons. To extend these studies, we investigated whether primary cultures of mammalian hepatocytes which are inducible for cytochrome P450IA2 are also inducible for chemically mediated uroporphyria. Hepatocytes were isolated from C57BL/6 mice and maintained on Matrigel, an extracellular matrix isolated from a mouse tumor. When these cultures were treated with 3,4,5,3',4',5'-hexachlorobiphenyl (HCB) and 5-aminolevulinic acid (ALA), they accumulated cytochrome P450IA2 as well as uroporphyrin (URO) and heptacarboxyporphyrin for up to 12 days. Cultures treated with ALA alone accumulated no P450IA2 and very little URO. Neither URO accumulation nor the level of P450IA2 was affected by addition of iron as the nitrilotriacetate complex. Other inducers of P450IA2 in vivo (3,4,5,3',4'-pentachlorobiphenyl, 3,4,3',4'-tetrachlorobiphenyl, and 3-methylcholanthrene) also increased P450IA2 in the cultures and caused URO accumulation in the presence of added ALA. The tetrachlorobiphenyl and methylcholanthrene caused these effects only when given repeatedly. Inducers of other forms of P450 failed to cause URO accumulation in the presence of ALA and iron. Cultures of hepatocytes from DBA mice (which are resistant to the uroporphyria in vivo) accumulated much less P450IA2 or URO when treated with HCB and ALA. These primary cultures of mammalian hepatocytes represent a new experimental model to investigate the role of cytochrome P450IA2 in the mechanism of chemically induced uroporphyria.

Structure-dependent induction of aryl hydrocarbon hydroxylase activity in C57BL/6 mice by 2,3,7,8-tetrachlorodibenzo-p-dioxin and related congeners: mechanistic studies

The time- and dose-dependent induction of murine hepatic microsomal aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) activities by five polychlorinated dibenzo-p-dioxin and dibenzofuran congeners showed that the order of induction potency was 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) greater than 2,3,7,8-tetrachlorodibenzofuran (TCDF) greater than 1,2,3,7,8-pentachlorodibenzo-p-dioxin (PCDD) greater than 1,2,3,7,8-pentachlorodibenzofuran (PCDF) greater than 2,3,7-trichlorodibenzo-p-dioxin (TrCDD). These structure-induction relationships were comparable to the structure-toxicity and competitive structure-receptor binding relationships previously reported for these compounds. However, using the corresponding radiolabeled congeners, the direct binding Kd values for dissociation of the cytosolic receptor-ligand complexes were 9.52, 7.96, 1.27, 3.10, and 8.31 nM for the 2,3,7,8-TCDD, 2,3,7,8-TCDF, 2,3,7-TrCDD, 1,2,3,7,8-PCDD, and 1,2,3,7,8-PCDF congeners and these data were clearly not structure dependent (i.e., similar to the structure-activity relationships). Some of the molecular properties for several radioligand-receptor complexes were similar; for example, the sedimentation coefficients for the cytosolic and nuclear receptor complexes varied from 8.8-10.4 S and 5.98-7.0 S, respectively, and the nuclear receptor complexes for all the radioligands eluted from a DNA-Sepharose column at salt concentrations of 0.27-0.29 M. Treatment of the mice with a maximum inducing dose of 2,3,7,8-[3H]TCDD resulted in a time-dependent formation of the nuclear receptor complex which was maximized between 16-24 hr and subsequently decreased up to 72 hr after initial exposure. In parallel studies, the nuclear receptor complex levels were determined 16 hr after treatment of the mice with different doses (2.25, 4.5, and 45 micrograms/kg) of all five radioligands. The results showed that at submaximal induction of the monooxygenase enzyme activities there was a linear correlation between the induced AHH or EROD activities (after 32 hr) and the corresponding nuclear receptor complex levels. It was also apparent from the data that the relative levels of nuclear receptor complex were structure dependent and this suggests that the transformation or activation of cytosolic receptor complexes may be a ligand structure-dependent process which correlates with the observed structure-activity relationships for 2,3,7,8-TCDD and related compounds.

Oxidative injury mediated by the hepatic cytochrome P-450 system in conjunction with cellular iron. Effects on the pathway of haem biosynthesis

1. Some polyhalogenated aromatic chemicals such as 2,3,7,8-tetrachloro-p-dioxin, brominated and chlorinated biphenyls, and hexachlorobenzene cause in humans, animals and hepatocyte systems a partial block in haem biosynthesis leading to accumulation and excretion of uroporphyrin, the oxidation product of the unstable biosynthetic intermediate uroporphyrinogen. 2. The involvement of reactive toxic metabolites of the halogenated chemicals has previously been suggested. The evidence presented in this paper supports a different mechanism involving chronic induction of the microsomal cytochrome P-450 system, mobilization of hepatocellular iron and associated oxidative stress. Besides oxidation of uroporphyrinogen to uroporphyrin, an inhibitor of uroporphyrinogen decarboxylase may also be formed. 3. Studies with iron-loaded mice and chicken embryo hepatocytes show that under appropriate conditions iron alone, or chemicals such as beta-naphthoflavone which induce the same cytochromes P-450 isozymes as do the chlorinated aromatics, will cause a similar uroporphyria. These findings provide an experimental model for the human disease porphyria cutanea tarda, sometimes occurring in patients with liver damage. 4. Experiments with rats and iron-loaded mice indicate that there may also be an association between the induction of uroporphyria and the development of liver tumours after administration of polyhalogenated aromatic chemicals.

Inhibition of uroporphyrinogen decarboxylase activity. The role of cytochrome P-450-mediated uroporphyrinogen oxidation

It was previously shown that uroporphyrinogen oxidation is catalysed by a form of cytochrome P-450 induced by 3-methylcholanthrene [Sinclair, Lambrecht & Sinclair (1987) Biochem. Biophys. Res. Commun. 146, 1324-1329]. We have now measured uroporphyrinogen oxidation and uroporphyrinogen decarboxylation simultaneously in 10,000 g supernatants from the livers of methylcholanthrene-treated mice and chick embryos incubated with an NADPH-generating system. We found that uroporphyrinogen oxidation is associated with inhibition of uroporphyrinogen decarboxylase activity. The decreased uroporphyrinogen decarboxylase activity was not due to depletion of substrate, since decarboxylase activity was not increased by a 2.6-fold increase in uroporphyrinogen. Uroporphyrinogen oxidation and the associated inhibition of decarboxylase activity were also observed with liver supernatant from methylcholanthrene-treated chick embryo; both actions required the addition of 3,3',4,4'-tetrachlorobiphenyl. Uroporphyrinogen oxidation catalysed by microsomes from a methylcholanthrene-treated mouse inhibited the uroporphyrinogen decarboxylase activity in the 100,000 g supernatant. Ketoconazole, an inhibitor of cytochrome P-450, prevented both uroporphyrinogen oxidation and the inhibition of uroporphyrinogen decarboxylation. The addition of ketoconazole to mouse supernatant actively oxidizing uroporphyrinogen inhibited the oxidation and restored decarboxylation. The latter finding suggested that a labile inhibitor was formed during the oxidation. These results suggest uroporphyrinogen oxidation may be important in the mechanism of chemically induced uroporphyria.

TCDD resistance is inherited as an autosomal dominant trait in the rat

In the present study, genetic crossings were performed between the most TCDD-susceptible (Long-Evans) and the most TCDD-resistant (Han/Wistar) rat strains. The F1 offspring were as resistant to TCDD as the Han/Wistar rats irrespective of the sex of their Han/Wistar parents. In test-cross and F2 progeny the distribution of resistant and susceptible phenotypes was consistent with inheritance regulated by 2 (possibly 3) autosomal genes displaying complete dominance, independent segregation, and an additive co-effect. These data show that, in contrast to earlier findings in mice, TCDD resistance seems to be the dominant trait in the rat. Moreover, the results challenge the current view that the Ah-locus is the exclusive determinant of TCDD sensitivity.

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)

Halogenated aromatic compounds, typified by the polychlorinated dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), biphenyls (PCBs), and diphenylethers (PCDEs), are industrial compounds or byproducts which have been widely identified in the environment and in chemical-waste dumpsites. Halogenated aromatics are invariably present in diverse analytes as highly complex mixtures of isomers and congeners and this complicates the hazard and risk assessment of these compounds. Several studies have confirmed the common receptor-mediated mechanism of action of toxic halogenated aromatics and this has resulted in the development of structure-activity relationships for this class of chemicals. The most toxic halogenated aromatic is 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and based on in vivo and in vitro studies the relative toxicities of individual halogenated aromatics have been determined relative to TCDD (i.e., toxic equivalents). The derived toxic equivalents can be used for hazard and risk assessment of halogenated aromatic mixtures; moreover, for more complex mixtures containing congeners for which no standards are available (e.g., bromo/chloro mixtures), several in vitro or in vivo assays can be utilized for hazard or risk assessment.

Biphasic response for hepatic microsomal enzyme induction by 2,3,7,8-tetrachlorodibenzo-p-dioxin in C57BL/6J and DBA/2J mice

The induction of the murine hepatic microsomal cytochrome P-450 monooxygenase system by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was studied over a wide range of doses, including those associated with acute toxicity. Studies were conducted in two inbred strains of mice which vary at the Ah receptor and at a number of other genetic loci. C57BL/6J mice possess a high-affinity Ah receptor and are responsive to enzyme inductive effects of TCDD, whereas DBA/2J mice do not possess a high-affinity receptor and are less responsive to TCDD. In a dose-response study, 7-ethoxyresorufin O-deethylase (EROD) activity appeared to be maximally induced in C57BL/6J and DBA/2J mice at 7 days following exposure to 3 and 30 micrograms of TCDD/kg respectively. Very similar results were reported previously for the induction of aryl hydrocarbon hydroxylase activity in these strains of mice. However, at higher doses of TCDD (at least 45 micrograms/kg for C57BL/6J and 300 micrograms/kg for DBA/2J), EROD activity was further increased (2-fold) from the apparent maximal (plateau) level, resulting in an unusual biphasic log dose-response relationship. EROD activity remained at these elevated rates in both strains for doses approaching and exceeding the respective LD50 values for each strain. To further characterize this biphasic induction phenomenon, cytochrome P-450 content, benzo[a]pyrene metabolism, and EROD and NADPH-cytochrome P-450 reductase activities were measured 1, 3 and 7 days after TCDD administration to C57BL/6J (3 and 150 micrograms/kg) and DBA/2J (30 and 600 micrograms/kg) mice. Maximal responses occurred in both strains at 3 days for all doses. In both strains, TCDD produced a dose-dependent increase in cytochrome P-450 content, EROD, and benzo[a]pyrene metabolism. Furthermore, a 2-fold induction of reductase activity was observed in each strain following exposure to the respective high doses. Induction of cytochrome P1-450 and P3-450 was also measured by Western immunoblot, using antisera raised against the homologous rat isozymes. In both strains, TCDD produced a dose-related increase in two protein-staining bands recognized by anti-P-450BNF-B (P1-450) and anti-P-450BNF/ISF-G (P3-450) respectively. The extended induction of hepatic microsomal monooxygenase activities at the respective high doses of TCDD appears to be due, in part, to increases in NADPH-cytochrome P-450 reductase activity and cytochromes P1-450 and P3-450 content. Significant alterations in the expression of the cytochrome P-450 monooxygenase system following exposure to high doses of TCDD may be associated, in part, with the delayed acute toxicity reported at this level of exposure.

2,3,7,8-Tetrachlorodibenzo-p-dioxin-induced porphyria in genetically inbred mice: partial antagonism and mechanistic studies

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) (233 nmol/kg) causes a significant increase of hepatic uroporphyrin, heptacarboxyporphyrin, and total porphyrins in female C57BL/6 mice, ovariectomized C57BL/6 mice, male C57BL/10 mice, and male C57BL/6 mice 3 weeks after treatment. In contrast, 6-methyl-1,3,8-trichlorodibenzofuran (MCDF) was inactive at a dose of 750 mumol/kg. Cotreatment of the mice with TCDD (233 mol/kg) plus MCDF (750 mumol/kg) resulted in partial antagonism of TCDD-induced hepatic porphyrin accumulation only in the female mice. Parallel studies in female C57BL/6 mice showed that the TCDD-induced porphyria was accompanied by the induction of hepatic microsomal aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) activities and the depression of uroporphyrinogen decarboxylase (UROD). MCDF (750 mumol/kg) did not significantly affect these enzymes. In the cotreatment studies (MCDF plus TCDD), MCDF partially antagonized TCDD-induced hepatic porphyrin accumulation but did not affect the levels of hepatic AHH, EROD, or UROD. These results indicate that other factors, in addition to the induction of cytochrome P450-dependent monooxygenases and depressed UROD activity, are important in TCDD-induced porphyria in C57BL/6 female mice.

Interaction of hexachlorobenzene with the receptor for 2,3,7,8-tetrachlorodibenzo-p-dioxin in vitro and in vivo. Evidence that hexachlorobenzene is a weak Ah receptor agonist

Hexachlorobenzene (HCB) produces hepatic porphyria and induces the hepatic cytochrome P450 isozymes P450c (P450IA1) and P450d (P450IA2) in rodents. These and other effects of HCB resemble those of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), which acts via its binding to the aromatic hydrocarbon (Ah) receptor. We therefore examined the ability of HCB to interact with this receptor in vitro and in vivo. HCB, at concentrations of 1 microM or higher, inhibited the specific binding of [3H]TCDD (0.3 nM) to the Ah receptor in vitro, whereas the solubility of [3H]TCDD was affected only at 100 microM HCB. The inhibition was competitive, with a KI of approximately 2.1 microM. In rats fed a diet containing 3000 ppm HCB for varying times (4 h to 7 days), the specific binding of [3H]TCDD in hepatic cytosol was reduced by up to 40%, as observed previously for known Ah receptor agonists. The decrease in [3H]TCDD specific binding in cytosol of HCB-treated rats was due principally to a decrease in the number of binding sites for [3H]TCDD rather than competition from residual HCB. As shown by immunoblotting and radioimmunoassay, HCB induced the cytochrome P450 isozymes P450c and P450d, which are regulated by the Ah receptor, as well as the phenobarbital-inducible isozymes P450b and P450e. Together these results indicate that HCB is a weak agonist for the Ah receptor, and suggest that some of its effects may be mediated by its interaction with this gene-regulatory protein.

Oxidation of uroporphyrinogen by methylcholanthrene-induced cytochrome P-450. Essential role of cytochrome P-450d

We have previously shown that uroporphyrinogen is oxidized to uroporphyrin by microsomes (microsomal fractions) from 3-methylcholanthrene-pretreated chick embryo liver [Sinclair, Lambrecht & Sinclair (1987) Biochem. Biophys. Res. Commun. 146, 1324-1329]. We report here that a specific antibody to chick liver methylcholanthrene-induced cytochrome P-450 (P-450) inhibited both uroporphyrinogen oxidation and ethoxyresorufin O-de-ethylation in chick-embryo liver microsomes. 3-Methylcholanthrene-pretreatment of rats and mice markedly increased uroporphyrinogen oxidation in hepatic microsomes as well as P-450-mediated ethoxyresorufin de-ethylation. In rodent microsomes, uroporphyrinogen oxidation required the addition of NADPH, whereas chick liver microsomes required both NADPH and 3,3',4,4'-tetrachlorobiphenyl. Treatment of rats with methylcholanthrene, hexachlorobenzene and o-aminoazotoluene increased uroporphyrinogen oxidation and P-450d, whereas phenobarbital did not increase either. The contribution of hepatic P-450c and P-450d to uroporphyrinogen oxidation and ethoxyresorufin O-de-ethylation in methylcholanthrene-induced microsomes was assessed by using specific antibodies to P-450c and P-450d. Uroporphyrinogen oxidation by methylcholanthrene-induced rat liver microsomes was inhibited up to 75% by specific antibodies to P-450d, but not by specific antibodies to P-450c. In contrast, ethoxyresorufin de-ethylation was inhibited only 20% by anti-P450d but 70% by anti-P450c. Methylcholanthrene-induced kidney microsomes which contain P-450c but non P-450d did not oxidize uroporphyrinogen. These data indicate that hepatic P-450d catalyses uroporphyrinogen oxidation. We suggest that the P-450d-catalysed oxidation of uroporphyrinogen has a role in the uroporphyria caused by hexachlorobenzene and other compounds.

The role of the Ah locus in hexachlorobenzene-induced porphyria. Studies in congenic C57BL/6J mice

The role of the Ah locus in hexachlorobenzene (HCB)-induced porphyria and the possible involvement of P-450 cytochromes P(1)450 and P(3)450 in the pathogenesis of this disease were investigated in two congenic strains of C57BL/6J mice that differ only at this locus. Female B6-Ahb mice (Ah receptor: approximately 30-70 fmol/mg of cytosolic protein) and B6-Ahd mice (Ah receptor: undetectable) were pretreated with iron (500 mg/kg) and then fed a diet containing 0 or 200 p.p.m. of HCB for up to 17 weeks. Mice from the two strains consumed similar amounts of HCB. Urinary excretion of porphyrins was increased after 7 weeks of HCB treatment in B6-Ahb mice, and after 15 weeks was over 200 times greater than that of mice given iron only. In B6-Ahd mice, porphyrin excretion did not begin to increase until after 13 weeks, and after 15 weeks was only six times greater than that of controls. Similar differences were seen in the 15-week hepatic porphyrin concentrations (B6-Ahb: 1110 +/- 393; B6-Ahd: 17.6 +/- 14.5; controls: approximately 0.20 nmol/g). Uroporphyrinogen decarboxylase (EC 4.1.1.37) activity was diminished by 70 and 20% in B6-Ahb B6-Ahd mice respectively after 15 weeks of treatment with HCB. Cytochromes P(1)450 and P(3)450 were measured in hepatic microsomes (microsomal fractions) by radioimmunoassay and immunoblotting, using antisera raised against the orthologous rat isoenzymes P450c and P450d. HCB induced small amounts of a protein recognized by anti-P450c (P(1)450) in B6-Ahd mice, but not in B6-Ahd mice. Relatively large amounts of a protein recognized by anti-P450d (P(3)450) were induced in both strains, but to a somewhat greater extent in the B6-Ahb mice. The hepatic accumulation of HCB at 15 weeks was greater in B6-Ahb than in B6-Ahd mice, in association with elevated hepatic lipid levels in the former strain. The results of this experiment indicate that the Ah locus influences the susceptibility of C57BL/6J mice to HCB-induced porphyria and are consistent with the suggestion that the sustained induction of P(3)450 and/or P(1)450 may be a causative factor in the development of this disease.

Hepatic uroporphyrin accumulation and uroporphyrinogen decarboxylase activity in cultured chick-embryo hepatocytes and in Japanese quail (Coturnix coturnix japonica) and mice treated with polyhalogenated aromatic compounds

The relationship between hepatic uroporphyrin accumulation and uroporphyrinogen decarboxylase (EC 4.1.1.37) activity was investigated in cultured chick-embryo hepatocytes, Japanese quail (Coturnix coturnix japonica) and mice that had been treated with polyhalogenated aromatic compounds. Chick-embryo hepatocytes treated with 3,3',4,4'-tetrachlorobiphenyl accumulated uroporphyrin in a dose-dependent fashion without a detectable decrease in uroporphyrinogen decarboxylase activity when either pentacarboxyporphyrinogen III or uroporphyrinogen III were used as substrates in the assay. Other compounds, such as hexachlorobenzene, parathion, carbamazepine and nifedipine, which have been shown previously to cause uroporphyrin accumulation in these cells, did not decrease uroporphyrinogen decarboxylase activity. Japanese quail treated with hexachlorobenzene for 7-10 days also accumulated hepatic uroporphyrin without any decrease in uroporphyrinogen decarboxylase activity. In contrast, hepatic uroporphyrin accumulation in male C57BL/6 mice treated with iron and hexachlorobenzene was accompanied by a 20-80% decrease in uroporphyrinogen decarboxylase activity, demonstrating that the assay used for uroporphyrinogen decarboxylase, using pentacarboxyporphyrinogen III as substrate, could detect decreased enzyme activity. Our results with chick hepatocytes and quail, showing uroporphyrin accumulation without a decrease in uroporphyrinogen decarboxylase activity, are consistent with a new two-stage model of the uroporphyria: initially uroporphyrinogen is oxidized by a cytochrome P-450-mediated reaction, followed in rodents by a progressive decrease in uroporphyrinogen decarboxylase activity.

Mechanism of PCB-induced porphyria and yusho disease

PCBs are known to be potent inducers of chemical porphyria. We studied the structure-activity relationship of synthetic PCBs as porphyrin inducers and found that 3,4,3',4'-tetrachlorobiphenyl, 3,4,3',4',5'-pentachlorobiphenyl, and 3,4,5,3',4',5'-hexachlorobiphenyl were the most active inducers. The structural requirement for potent porphyrinogenic activity of PCB isomers was the substitution of chlorine atoms at the para and meta positions. Isomers fulfilling this requirement had more highly conjugated and nearly coplanar conformations. In addition, it was demonstrated that inhibition of UROD by the most active porphyrin inducers occurred in vitro using purified enzyme. These findings could explain how porphyrinogenic PCBs, by primarily inhibiting UROD and hence depleting heme, ultimately increase ALAS synthesis. The outbreak of yusho disease in Japan (which was caused by PCB-contaminated rice oil) and a similar episode of food poisoning in Taiwan (which was also related to PCB contamination) were discussed, particularly with reference to urinary porphyrin levels and clinical response.

Effects of chlorinated organics on intermediates in the heme pathway and on uroporphyrinogen decarboxylase

Experimental porphyria induced by PHAHs is characterized by a progressive reduction in the activity of UROD. After intoxication with TCDD, the most porphyrogenic compound known to date, the liver was the principal site of action, as regards both porphyrin accumulation (mostly uroporphyrin) and the degree of enzyme impairment; the kidney was the site of the second greatest accumulation; the brain and erythrocytes were unaffected. Additional modifications of the heme pathway involved induction of the activity of ALAS and, at least in HCB-induced porphyria after iron pretreatment, may have involved reduced activity of uroporphyrinogen III cosynthetase. These changes can alter the amount and the isomeric composition of uroporphyrinogens and uroporphyrins present in the liver in a way that is likely to help reduce formation of coproporphyrinogen III in porphyric animals. As in the human syndrome porphyria cutanea tarda, iron administration increased porphyrin accumulation and the degree of reduction of UROD activity in mice fed HCB. Mice fed HCB also presented an activation of the type O form of XO. This activation was independent of tissue injury derived from the lipid peroxidation that was concomitant with iron administration. The increase in activity of the type O form of XO may be a characteristic feature of the liver damage found in PHAH intoxication and, in intoxicated animals, could be a source in the liver of oxidant species involved in the mechanism of UROD inactivation--if this inactivation is in fact due to an oxidative reaction.

Synthesis and aryl hydrocarbon receptor binding properties of radiolabeled polychlorinated dibenzofuran congeners

Microchlorination of 1,4,9[3H]dibenzofuran gave several polychlorinated dibenzofuran (PCDF) products and 2,3,7,8-[3H]tetrachlorodibenzofuran (TCDF), 1,2,3,7,8-[3H]pentachlorodibenzofuran (PeCDF), and 1,2,3,6,7,8-/1,2,3,4,7,8-hexachlorodibenzofuran (HCDF) of high specific activity (57, 34, and 32.5 Ci/mmol, respectively) were purified by preparative high-pressure liquid chromatography. These compounds were investigated as radioligands for the rat liver cytosolic aryl hydrocarbon (Ah) receptor protein. Like 2,3,7,8-[3H]tetrachlorodibenzo-p-dioxin (TCDD), the radiolabeled PCDF congeners exhibited saturable binding with the receptor protein and sucrose density gradient analysis of the radiolabeled ligand-receptor complexes gave specific binding peaks with comparable sedimentation profiles. The rank order of radioligand binding affinities (Kd values) was 2,3,7,8-TCDD greater than 2,3,7,8-TCDF greater than 1,2,3,6,7,8-HCDF greater than 1,2,3,7,8-PeCDF and the maximum difference in Kd values for the four radioligands was less than 13-fold (0.44-5.9 nM). The interactions of the PCDF radioligands with the cytosolic receptor all exhibited saturable binding curves and linear Scatchard plots and the slopes of their Hill plots were in the range 1.0-1.1, thus indicating that cooperativity was not a factor in these binding interactions. The relative stabilities and dissociation kinetics of the radioligand-receptor complexes were highly dependent on the structure of the radioligand. The dissociation curves of the 2,3,7,8-[3H]TCDD and PCDF receptor complexes were biphasic and this suggests that there may be a temporal shift in ligand binding affinities. However, the rates of dissociation did not correlate with the rank order of ligand binding affinities. The stabilities of the radioligand-receptor complexes were also dependent on the structures of the radioligands; for example, the 2,3,7,8-[3H]TCDD-receptor complex degraded more rapidly than the PCDF-receptor complex and these relative stabilities were clearly not related to the Kd values or the relative in vivo or in vitro biologic potencies of these halogenated aryl hydrocarbons.

Aroclor 1254 as a 2,3,7,8-tetrachlorodibenzo-p-dioxin antagonist: effects on enzyme induction and immunotoxicity

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) and Aroclor 1254 induced the cytochrome P-450 dependent monooxygenases, aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) in rat hepatoma H-4-II E cells and C57BL/6J mice. It has been proposed that both Aroclor 1254 and 2,3,7,8-TCDD induce these enzymes via a common mechanism which features initial binding to the aryl hydrocarbon (Ah) cytosolic receptor protein. The major difference between these compounds was the relative potency (i.e. 2,3,7,8-TCDD much greater than Aroclor 1254). Cotreatment of rat hepatoma H-4-II E cells or C57BL/6J mice with a dose of 2,3,7,8-TCDD which submaximally induces AHH and EROD and a dose of Aroclor 1254 which exhibited little or no induction activity resulted in significant antagonism of the induction effects of 2,3,7,8-TCDD. For example, cotreatment of C57BL/6J mice with 2,3,7,8-TCDD (15 nmol/kg) and Aroclor 1254 (25, 75 and 150 mumol/kg) resulted in up to 23% antagonism of AHH induction by 2,3,7,8-TCDD. Moreover, cotreatment with a higher dose of the 2,3,7,8-TCDD agonist (30 or 50 nmol/kg) partially reversed some of the antagonism by Aroclor 1254. In vivo antagonism was observed only at Aroclor 1254/2,3,7,8-TCDD molar ratios of 1667:1, 5000:1 and 10,000:1. Administration of 2,3,7,8-TCDD (3.72 nmol/kg) to C57BL/6J mice resulted in a 76% decrease in the splenic plaque forming cell response to sheep red blood cells. This T-cell mediated immunotoxic effect of 2,3,7,8-TCDD segregates with the Ah locus. In contrast, administration of 5, 15, 75 and 150 mumol/kg of Aroclor 1254 resulted in impairment of the immune response only at the highest dose level. However, cotreatment of mice with 2,3,7,8-TCDD (3.72 nmol/kg) and Aroclor 1254 (5, 15 or 75 mumol/kg) resulted in no significant decrease in the plaque forming cell response and complete protection from the immunotoxicity of 2,3,7,8-TCDD. Cotreatment of the mice with Aroclor 1254 (75 mumol/kg) and a higher dose of the 2,3,7,8-TCDD agonist resulted in partial reversal of the protective effects of Aroclor 1254. The in vitro and in vivo data suggest that within specific antagonist/agonist dose ratios, Aroclor 1254 can antagonize at least 2 Ah receptor-mediated effects of 2,3,7,8-TCDD, namely AHH induction and immunotoxicity.

Comparison of hexachlorobenzene-induced alterations of microsomal membrane composition and monooxygenase activity in male and female rats

The effect of hexachlorobenzene (HCB) on microsomal cytochromes P-450 and b5, monooxygenase activity and membrane composition was examined in male and female Fischer rats. Cytochrome P-450 was induced more in male than in female animals while cytochrome b5 was induced only in males. Analysis of patterns of induction of microsomal monooxygenases showed that aminopyrine-N-demethylase activity doubled in both sexes after treatment while aryl hydrocarbon hydroxylase activity was 16 times the control value in the females and 1.5 times in the males. After HCB treatment the phospholipid content of microsomal membranes per gram of liver was increased in both sexes while cholesterol was unchanged. Analysis of the phospholipids (PL) pattern showed that the percentage of sphingomyelin (SPH) decreased significantly (50% of the control value) while phosphatidylcholine (PC), phosphatidylinositol (PI) and phosphatidylethanolamine (PE) did not change. These changes resulted in a reduction of membrane microviscosity and indicate that HCB interferes with the biosynthesis of phospholipids containing choline. Free fatty acid (FFA) content also dropped in both sexes but females were more affected; free arachidonic acid rose in females. HCB induction of microsomal cytochromes and monooxygenases is thus accompanied by marked modifications of membrane composition. Comparing the 2 sexes, HCB showed more pronounced features of 'PB type' inducers in males.

Chemically-induced formation of an inhibitor of hepatic uroporphyrinogen decarboxylase in inbred mice with iron overload

An inhibitor of hepatic uroporphyrinogen decarboxylase (EC 4.1.1.37) was demonstrated in heat-treated extracts of livers from C57BL/10ScSn mice with iron overload after a single dose (100 mg/kg; 350 mumol/kg) of hexachlorobenzene (HCB). Inhibition was not due to accumulated uroporphyrin since this could be removed by a SEP-PAK C18 cartridge without affecting inhibitor activity. The presence of the inhibitor could be first demonstrated 2 weeks after mice received HCB and before major elevation of hepatic porphyrin levels. Maximum inhibitory potential was reached at about 8 weeks and was still detected 25 weeks after the chemical, thus paralleling the depression of enzyme activity reported previously [Smith, Francis, Kay, Greig & Stewart (1986) Biochem. J. 238, 871-878]. The inhibitor was not detected following treatment of mice with either iron or HCB alone or after the decarboxylase activity was destroyed in vitro by the combination of uroporphyrin and light. The formation of the inhibitor by inbred mouse strains nominally Ah-responsive (C57BL/6J, C57BL/10ScSn, BALB/c, C3H/HeJ, CBA/J and A/J) and Ah-nonresponsive (SWR, AKR, 129, SJL, LP and DBA/2) did not correlate fully with their reported Ah-phenotype. There was a correlation amongst the Ah-responsive strains only, with hepatic ethoxyphenoxazone de-ethylase activity induced in parallel experiments by treatment with beta-naphthoflavone. De-ethylase activity induced by HCB, however, was considerably less than that with beta-naphthoflavone, which has not been reported as porphyrogenic. Other polyhalogenated chemicals, such as 2,3,7,8-tetrachlorodibenzo-p-dioxin, 2,3,4,2',3',4'-hexachlorobiphenyl and hexabromobenzene, also caused the formation of the inhibitor of uroporphyrinogen decarboxylase.

Evidence for cytochrome P450-mediated oxidation of uroporphyrinogen by cell-free liver extracts from chick embryos treated with 3-methylcholanthrene

Cell-free preparations from liver of chick embryo treated with 3-methylcholanthrene catalyzed oxidation of uroporphyrinogen I in the presence of NADPH and 3,4,3',4'-tetrachlorobiphenyl. Extracts of untreated embryo liver or liver from embryo treated with glutethimide, a phenobarbital-like inducer of cytochrome P450 in this system, did not catalyse the oxidation. Direct involvement of cytochrome P450 was demonstrated by inhibition of the oxidation by CO, piperonyl butoxide and specific antisera to the methylcholanthrene-induced cytochrome P450. 2,4,2',4'-tetrachlorobiphenyl was inactive in the oxidation. These results may explain the role of induced cytochrome P450 in experimental uroporphyria. The oxidation may be useful as a simple assay for reactive O2 species.

Role of inhibition of uroporphyrinogen decarboxylase in PCB-induced porphyria in mice

The oral administration of 3,4,5,3',4',5'-hexachlorobiphenyl for 3 weeks to mice caused a marked accumulation of porphyrins in the liver of C57BL/6 and C57Bl/10 mice but not in the liver of ddY mice. The time course of induction of delta-aminolevulinic acid synthetase (ALA-S), cytochrome P-450, and mixed function oxidases and inhibition of uroporphyrinogen decarboxylase (URO-D) in the liver of C57BL/6 mice and ddY mice fed a diet containing 500 ppm of a commercial PCB (Kanechlor-500) were investigated to clarify the sole factor in inducing porphyria. The activity of URO-D in the liver of C57BL/6 mice was depressed approximately 80% at 3 weeks when a large amount of uroporphyrin accumulated. Male ddY mice showed only a slight increase in uroporphyrin accumulation in the liver and a moderate decrease of URO-D activity even at the 10th week. ALA-S, cytochrome P-450, and mixed function oxidases were induced in both strains of mice, although the magnitude of these inductions in C57BL/6 mice was greater than that in ddY mice. No differences were detected between the two strains in the content and gas chromatographic pattern of PCB remaining in liver cytosol (6 weeks). In addition there was no relationship between the time of onset of porphyria and that of the maximal induction of drug-metabolizing function in C57BL/6 mice. These results indicate that the development of porphyria is causally related to the inhibition of URO-D rather than the induction of drug-metabolizing function. The hypothesis that porphyria first develops when the ratio of hepatic URO-D and ALA-S activities decreases to less than 1.0 is presented.

Pleiotropic effect of the gene hairless on hepatotoxicity of 2, 3, 7, 8-tetrachlorodibenzo-p-dioxin in mice

Treatment of mice of the A2G-hr/+ congenic line with 2, 3, 7, 8-tetrachlorodibenzo-p-dioxin (TCDD) resulted in the development of hepatic porphyria over a period of 4 weeks. Female mice responded to a lesser extent than did males. The degree of porphyria in haired heterozygotes (hr/+) was less than in the corresponding hairless homozygotes (hr/hr) and the haired mice had lower resting metabolic rates than hairless mice. Adaptation of mice of either genotype to a 32-33 degrees C environment resulted in a decrease in resting metabolic rate and a reduction in hepatic porphyrin levels. Histologically-demonstrated necrotic changes in livers were accompanied by increased activity of alanine aminotransferase and sorbitol dehydrogenase in the plasma; however, there was no clear temporal trend in plasma enzyme levels. Elevated environmental temperature reduced the plasma alanine aminotransferase activity. The study provided evidence for a pleiotropic effect of variation at the hr locus being expressed in TCDD hepatotoxicity. Suggestions for mechanisms whereby the effect can be mediated through alterations in resting metabolic rate are made.

Mechanistic studies of the inhibition of hepatic uroporphyrinogen decarboxylase in C57BL/10 mice by iron-hexachlorobenzene synergism

Porphyria was induced in C57BL/10 mice with iron overload by a single oral dose (100 mg/kg) of hexachlorobenzene (HCB). Within 2 weeks hepatic uroporphyrinogen decarboxylase (EC 4.1.1.37) was inhibited, reaching a maximum (greater than 95%) at 6-8 weeks. There was no recovery by 14 weeks, despite a fall in liver HCB concentrations to only 6% of the day-3 value. The major rise in hepatic porphyrin levels occurred after 4 weeks and secondary inhibition of uroporphyrinogen synthase (EC 4.2.1.75) was inferred from the progressively greater proportion of uroporphyrin I present relative to the III isomer. Plasma alanine aminotransferase (EC 2.6.1.2) activity was also elevated. Although, in further studies, total microsomal cytochrome P-450 content and ethoxyphenoxazone de-ethylase activity reached a peak a few days after dosing and had declined significantly at the time of maximum inhibition of the decarboxylase, additional treatment of HCB-dosed mice with a cytochrome P1-450 inducer, beta-naphthoflavone, enhanced the inhibition, whereas piperonyl butoxide, an inhibitor of cytochrome P-450, partially protected. Uroporphyrinogen decarboxylase was not radiolabelled in vivo by [14C]HCB. There was no major difference in the ability to hydroxylate HCB between hepatic microsomes from induced C57BL/10 mice and those from the insensitive DBA/2 strain. By contrast, lipid peroxidation, in the presence of NADPH, was 8-fold greater in control C57BL/10 microsomes than in DBA/2 microsomes and was stimulated by iron treatment (although not by HCB). The results suggest that the inhibition of hepatic uroporphyrinogen decarboxylase is unlikely to be due to a direct effect of a metabolite of HCB but to another process requiring a specific cytochrome P-450 isoenzyme and an unknown iron species.

Intracellular location of the Ah receptor

The subcellular distribution of the Ah receptor from the mouse hepatoma line, Hepa-1, was investigated following cytochalasin B treatment and cell enucleation. Probing the resultant cytoplast and nucleoplast fractions with radiolabelled tetrachlorodibenzo-p-dioxin (TCDD) revealed the presence of a specifically bound peak of receptor only in the cytoplast fraction. However, the quantity of receptor recovered in these experiments was only 10-12% of the expected value. We therefore undertook an investigation to determine the fate of the Ah receptor in the presence of cytochalasin B. Incubation of Hepa-1 cells with this compound resulted in a rapid loss or inactivation of cytosolic binding activity with a concomitant decrease in the amount of receptor partitioned into the nucleus at all time periods examined. Control experiments indicated that cytochalasin B did not compete with TCDD for binding to the Ah receptor and furthermore, that its mechanism of action could not be attributed to a non-specific effect on all cytosolic proteins. The results obtained are discussed in relation to the proposed models for induction by the estrogen and glucocorticoid binding receptors.

Uroporphyrin accumulation produced by halogenated biphenyls in chick-embryo hepatocytes. Reversal of the accumulation by piperonyl butoxide

Cultures of chick-embryo hepatocytes were used to study the mechanism by which 3,4,3',4'-tetrachlorobiphenyl and 2,4,5,3',4'-pentabromobiphenyl cause accumulation of uroporphyrin. In a previous paper, an isoenzyme of cytochrome P-450 induced by 3-methylcholanthrene had been implicated in this process [Sinclair, Bement, Bonkovsky & Sinclair (1984) Biochem. J. 222, 737-748]. Cells treated with 3,4,3',4'-tetrachlorobiphenyl and 5-aminolaevulinate accumulated uroporphyrin and heptacarboxyporphyrin, whereas similarly treated cells accumulated protoporphyrin immediately after piperonyl butoxide was added. Piperonyl butoxide also restored haem synthesis as detected by incorporation of radioactive 5-aminolaevulinate into haem, and decrease in drug-induced 5-aminolaevulinate synthase activity. The restoration of synthesis of protoporphyrin and haem by piperonyl butoxide was not affected by addition of cycloheximide, indicating recovery was probably not due to protein synthesis de novo. Piperonyl butoxide also reversed uroporphyrin accumulation caused by 3,4,5,3',4',5'-hexachlorobiphenyl, mixtures of other halogenated biphenyls, lindane, parathion, nifedipine and verapamil. The effect of piperonyl butoxide was probably not due to inhibition of metabolism of these compounds, since the hexachlorobiphenyl was scarcely metabolized. Other methylenedioxyphenyl compounds, as well as ellipticine and acetylaminofluorene, also reversed the uroporphyrin accumulation caused by 3,4,3',4'-tetrachlorobiphenyl. SKF-525A (2-dimethylaminoethyl-2,2-diphenyl valerate) did not reverse the uroporphyrin accumulation caused by the halogenated biphenyls, but did reverse that caused by phenobarbital and propylisopropylacetamide. We conclude that the mechanism of the uroporphyrin accumulation cannot be due to covalent binding of activated metabolites of halogenated compounds to uroporphyrinogen decarboxylase.

Polychlorinated dibenzofurans as 2,3,7,8-TCDD antagonists: in vitro inhibition of monooxygenase enzyme induction

2,4,6,8- and 1,3,6,8-tetrachlorodibenzofuran (TCDF) competitively displace [3H]2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) from the rat cytosolic receptor protein and their EC50 values were 1.5 X 10(-6) and 1.25 X 10(-7) M, respectively. In contrast to their relatively high binding avidities these TCDF isomers were poor inducers of benzo[a]pyrene hydroxylase and ethoxyresorufin O-deethylase in rat hepatoma H-4-II E cells in culture (EC50 greater than 10(-5) M). Coadministration of different concentrations of 2,4,6,8- and 1,3,6,8-TCDF (10(-5), 10(-6) and 10(-7) M) with 2 X 10(-10) M, 2,3,7,8-TCDD (a dose which elicits 80% of the maximal induction response) resulted in significant decreases in the expected (additive) induction of benzo[a]pyrene hydroxylase and ethoxyresorufin O-deethylase by the mixture. Thus the partial agonists, 1,3,6,8- and 2,4,6,8-TCDF, antagonize the receptor-mediated enzyme induction activity of 2,3,7,8-TCDD presumably via competitive displacement of 2,3,7,8-TCDD from the receptor protein. In contrast, coadministration of 2,3,7,8-TCDF and 2,3,7,8-TCDD gave additive enzyme induction responses. The identification of the 2,3,7,8-TCDD antagonists represents a new class of halogenated aryl hydrocarbons.

The murine aromatic hydrocarbon responsiveness locus: a comparison of receptor levels and several inducible enzyme activities among recombinant inbred lines

The aromatic hydrocarbon responsiveness (Ah) locus has been correlated with genetic differences in the risk of drug toxicity, teratogenesis, chemical carcinogenesis, and mutagenesis. Hepatic cytosolic Ah receptor levels, 2-amino-5-chlorobenzoxazole (zoxazolamine) paralysis time following beta-naphthoflavone treatment and aryl hydrocarbon hydroxylase (AHH3, acetanilide 4-hydroxylase (Ac4H), and NAD(P)H:menadione oxidoreductase (NMOR)4, induction by 3-methylcholanthrene were studied in (a) the progenitors C57BL/6J (Ahb/Ahb) and DBA/2J (Ahd/Ahd) and 25 BXD recombinant inbred lines, (b) the progenitors C57BL/6N and C3H/HeN and 14 B6NXC3N recombinant inbred lines, and (c) the progenitors C57BL/6J and C3H/HeJ and 12 BXH recombinant inbred lines. The Ahb phenotype exhibits greater than 5 femtomole receptor/mg of cytosolic protein, less than or equal to 15 minutes zoxazolamine paralysis time, and twofold to 15-fold induction of these three hepatic enzyme activities; the Ahd phenotype exhibits less than or equal to 2 fmol receptor/mg protein, greater than 15 minutes zoxazolamine paralysis time, and less than 30% induction of these three activities. Among the BXD lines but especially among the B6NXC3N and BXH lines, high frequencies of recombination were found; the phenotype of each of the five parameters did not segregate with the phenotype of each of the other parameters in four or more recombinant lines. This report shows for the first time that AHH induction by 3-methylcholanthrene can occur in the Ahd phenotype mouse. These data underline the complexity of this genetic system when genes from C57BL/6 and DBA/2 are combined and particularly when genes from C57BL/6 and C3H/He inbred mouse strains are combined.

Distinction between octachlorostyrene and hexachlorobenzene in their potentials to induce ethoxyphenoxazone deethylase and cause porphyria in rats and mice

The potentials of octachlorostyrene (OCS) and hexachlorobenzene (HCB) to induce liver microsomal ethoxyphenoxazone deethylation (an indicator of induction of 3-methylcholanthrene and beta-naphthoflavone-like cytochrome P-450 monoxygenase activity) and cause porphyria in male C57BL/6 and C57BL/10 mice and female F344 rats were compared. Ethoxyphenoxazone deethylation was induced much more by HCB than by OCS in both of these strains of mice (although neither OCS nor HCB greatly induced deethylation in the DBA/2 strain). In rats ethoxyphenoxazone deethylase was induced 26-fold by HCB but only four-fold by OCS, whereas dealkylation of pentoxyphenoxazone (an indicator of phenobarbital-like induction) increased 43- and 36-fold, respectively. Both chemicals were poor inducers of dealkylation of pentoxyphenoxazone in mice. When fed HCB continuously but not when given OCS, C57BL/6 and C57BL/10 mice (both after pretreatment with iron) and F344 rats developed porphyria with a depression of hepatic uroporphyrinogen decarboxylase activity. The results illustrate that in these species OCS and HCB cannot be considered as equally efficient agents for inducing ethoxyphenoxazone deethylation or causing porphyria. If these effects are mediated through binding to the aromatic hydrocarbon responsiveness (Ah) receptor, HCB would appear to have a much greater affinity than OCS despite the face that neither chemical possesses a structure currently considered to be necessary for efficient binding.

Teratogenic potency of TCDD, TCDF and TCDD-TCDF combinations in C57BL/6N mice

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) and 2,3,7,8-tetrachlorodibenzofuran (TCDF) cause the same spectrum of fetal anomalies in C57BL/6N mice. Pregnant dams were treated with TCDD, TCDF and combinations of the 2 compounds on gestation day 10, and examined for maternal and fetal effects on day 18. The fetal kidneys were the most sensitive target for teratogenicity. The dose response for cleft palate induction fit the probit model for both compounds, suggesting that TCDD was approximately 30 times more potent than TCDF. The interaction between these 2 compounds was consistent with a model for additive toxicity.

Continued depression of hepatic uroporphyrinogen decarboxylase activity caused by hexachlorobenzene or 2,3,7,8-tetrachlorodibenzo-p-dioxin despite regeneration after partial hepatectomy

Hepatic uroporphyrinogen decarboxylase activity in male C57BL/10 mice was maintained in regenerated liver after recovery from two-thirds hepatectomy. In contrast, there was little increase in enzyme activity in regenerated liver from animals previously treated with hexachlorobenzene (HCB) or 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). These chemicals initially cause depression of uroporphyrinogen decarboxylase activity over a time much longer than the period allowed for regeneration. Estimation of HCB levels showed that there was only a small amount of redistribution to the liver during regrowth. The results demonstrate that HCB and TCDD induce either formation of a toxic metabolite or some other inhibitory process and that this can be sustained for a long period which delays recovery to the normal state.