Carcinogenic azo dyes. XI. Analysis of biliary and urinary metabolities of 3'-methyl-4-(methylamino)azobenzene in rat

Hepatic binding proteins translocating azo dye carcinogen metabolites from cytoplasm into nucleus in rats

When liver cytosol prepared from rats administered [(14)C]-3'-Methyl-N,N-dimethyl-4-aminoazobenzene was subjected to Sephadex gel chromatography, four peaks of radioactivity containing proteins (Peak-I-IV) and one peak devoid of protein (Peak-V) were obtained. Translocation of azo dye metabolites from these various cytosolic fractions into nucleus was studied in an in vitro system and a maximum of about 10% of the radioactivity associated with a particular cytosolic fraction (Peak-II) could translocate into the nuclei. Radioactivity (%) translocated did not increase upon addition of excess nuclei. Passage of this protein fraction through an immobilized protease column reduced the azo dye metabolite translocation by 65%, concomitant with the degradation of proteins. Translocation was not observed with protein-free metabolites extracted from this cytosolic fraction; addition of proteins corresponding to peak-II from normal rat liver cytosol significantly restored the metabolite translocation. This observation suggests that specific cytosolic proteins are involved in the translocation of azo dye carcinogen metabolites from liver cytoplasm into the nucleus. When the liver cytosolic proteins corresponding to this fraction (Peak-II) were iodinated with (125)I-iodine and incubated with purified nuclei, translocation of three specific proteins into nucleus was observed as seen by SDS-PAGE and fluorography of nuclear proteins. Covalent binding of azo dye metabolites to DNA was not observed when cytosolic peak-II fraction containing azo dye metabolites was incubated with isolated liver DNA instead of liver nuclei. This suggests that the interaction of azo dye metabolites with nuclear macromolecules necessitate further prior processing which actually may occur in the nucleus.

Hepatic vectorial transport of xenobiotics

The vectorial transport of xenobiotics across the hepatocyte is mediated by various transport and transfer proteins that differ in ligand specificity and function. The influx of xenobiotics from the blood across the sinusoidal membrane of the hepatocyte can occur through passive or active transport processes. Once in the cell, xenobiotics can be sequestered by intracellular transfer proteins that prevent refluxing of the chemical back through the sinusoidal membrane. Transfer proteins may also facilitate the localization of the xenobiotics within the cell to sites of metabolism (i.e., the endoplasmic reticulum) or elimination (i.e., the canalicular membrane). Intracellular transfer proteins include glutathione S-transferases, fatty acid-binding proteins, and 3 alpha-hydroxysteroid dehydrogenase. Intracellular nuclear transfer proteins have also been identified that facilitate the transfer of chemical carcinogens from the cytoplasm into the cell nucleus. Several active transport proteins exist on the canalicular membrane of the hepatocyte that mediate the efflux of chemicals from the cell into the biliary canaliculus. Xenobiotic efflux proteins include the multispecific organic anion transporter, that eliminates xenobiotics that have undergone conjugation with glutathione, glucuronic acid, and possibly sulfate; and, P-glycoprotein, an active transporter that actively effluxes a variety of structurally diverse xenobiotics. Induction of P-glycoprotein by the amplification of its gene has been identified as a major cause of resistance of tumor cells to the toxicity of a variety of anti-cancer drugs. The hepatic induction of P-glycoprotein may also contribute to acquired resistance of organisms to environmental toxicants. Continued elucidation of xenobiotic transport and transfer processes at the cellular levels will significantly advance our understanding of processes involved in xenobiotic toxicity and acquired resistance to chemical toxicity.

Protein binding, nuclear translocation and biliary secretion of metabolites of 3'-methyl-N,N-dimethyl-4-aminoazobenzene during hepatocarcinogenesis in rats

1. The hepatic content, biliary excretion, cytosolic protein binding and nuclear translocation of metabolites of i.v. administered 14C-3'-methyl-N,N-dimethyl-4-aminoazobenzene (3'-methyl-DAB) were investigated in rats at various stages of 2-acetamidofluorene (AAF)-induced hepatocarcinogenesis. 2. At nodular and post-nodular stages biliary excretion of radioactive metabolites was decreased, although hepatic content of radioactivity was similar to controls not dosed with AAF. The secretion in bile of a major azo dye binding protein was also decreased at these stages. 3. Binding of dye metabolites to cytosolic proteins was decreased by 40% at nodular and post-nodular stages compared to controls. 4. Translocation in vitro of dye metabolites from cytosol to nucleus at nodular and post-nodular stages was 40% less than that of controls. Since specific soluble proteins control translocation from cytosol into the nucleus (and bile), this decreased binding of metabolites may explain the diminished translocation of carcinogen metabolites into the nucleus.

Metabolism of azo dyes: implication for detoxication and activation

Azo dyes are consumed and otherwise utilized in varying quantities in many parts of the world. Such widely used chemicals are of great concern with regard to their potential toxicity and carcinogenic properties. Their metabolism has been studied extensively and is significant for detoxication and metabolic activation. Both oxidative and reductive pathways are involved in these processes. The majority of azo dyes undergo reduction catalyzed by enzymes of the intestinal microorganisms and/or hepatic enzymes including microsomal and soluble enzymes. The selectivity of substrate and enzyme may to a large extent be determined by the oxygen sensitivity of reduction since a normal liver is mainly aerobic in all areas, whereas the microorganisms of the lower bowel exist in an anaerobic environment. However, it should be pointed out that the pO2 of centrilobular cells within the liver is only a fraction that of air, where pO2 = 150 torr. Therefore, an azo dye reduction experiment performed aerobically may not be an accurate predictor of reductive metabolism in all areas of the liver. Many of the azo dyes in common use today have highly charged substituents such as sulfonate. These resist enzymic attack and for the most part are poorly absorbed from the intestinal tract, providing poor access to the liver, the major site of the mixed-function oxidase system. Lipophilic dyes, such as DAB, which are often carcinogenic, readily access oxidative enzymes and are activated by both mixed-function oxidase and conjugating systems. Reduction of the carcinogenic dyes usually leads to loss of carcinogenic activity. By contrast, most of the highly charged water-soluble dyes become mutagenic only after reduction. Even then, most of the fully reduced amines required oxidative metabolic activation. An outstanding example is the potent human bladder carcinogen benzidine, which derives from the reduction of several azo dyes. Many problems regarding mutagenic and carcinogenic activation remain to be solved. At the present time, it is apparent that both oxidative and reductive pathways yield toxic products. Toxicologic assessment of azo dyes must consider all pathways and particularly the oxygen sensitivity of azoreduction. This is critical in the treatment of waste from chemical plants where there is a great need for soil bacteria which catalyze reduction aerobically. Consideration of secondary pathways are also of great concern. For example, azoreduction of carcinogenic dyes such as DAB removes carcinogenic activity although oxidative metabolism of the primary amines yield mutagenic products. Such apparent dilemmas must be dealt with when considering metabolism/toxicity relationships for azo dyes.

Purification and characterization of a novel abundant protein in rat bile that binds azo dye metabolites and copper

Following intravenous administration to rats of the azo dye hepatocarcinogen 3'-methyl-N,N-dimethyl-4-aminoazo-[14C]benzene, 60-70% of the injected dose was recovered in bile in 2 h. Approximately 10% of bile radioactivity was trichloroacetic acid-precipitable, not extracted by n-butanol and non-dialyzable. Sodium dodecyl sulfate-polyacrylamide gel electrophoresis of bile followed by fluorography revealed two major and several minor proteins to which radiolabelled azo dye metabolites were bound; one of these major proteins (50 kDa) was purified from bile and shown to be homogeneous by SDS-polyacrylamide gel electrophoresis, isoelectric focusing (pI 7) under denaturing conditions and N-terminal analysis. The protein (MBP) comprises 15% of the total bile protein. Amino acid analysis revealed a preponderance of acidic and hydrophobic amino acids. The absorption spectrum of the native protein had a major peak at 280 nm and minor peaks at 345, 400, 600 and 650 nm. The fluorescence spectrum showed a major excitation maxima at 285 and 350 nm and corresponding emission maxima at 345 and 440 nm. Atomic absorption spectroscopy revealed 5 atoms of Cu per mol protein. Approximately 90% of the Cu was EPR silent. MBP did not react with antisera directed against rat serum IgA, albumin or ceruloplasmin; nor did these proteins react against antisera to MBP. Seven distinct peptide bands ranging from 5 to 18 kDa were obtained when MBP was subjected to CNBr cleavage and the digests were analyzed by SDS-polyacrylamide gel electrophoresis. The [14C]-Me-DAB derived radioactivity was present in only two of the peptides, indicating specific binding sites for azodye metabolites.

A review of the genotoxicity of food, drug and cosmetic colours and other azo, triphenylmethane and xanthene dyes

The genetic toxicology of the major dyestuffs used in foods, drugs and cosmetics has been reviewed. Published data for azo, triphenylmethane and xanthene dyes from short-term assays for muta-carcinogenicity have been summarized and discussed according to usage, current and previous worldwide legislative status. Certain other synthetic food dyes, commercial mixtures, natural and polymeric colourants as well as a section on aminoazobenzene and its derivatives have been included. Genotoxicity has been discussed with reference to structural chemistry, levels of exposure, absorption and metabolism and to epidemiological information. The extent of agreement between data from different tests and correlations with animal cancer assays have been considered. Synthetic dyes from the 3 major structural classes exhibit genotoxicity, whilst only 2 natural colours have proved active. Activity may be due to the presence of certain functional groups, notably nitro- and amino-substituents which are metabolized to ultimate electrophiles that may be stabilized by electronic interaction with aryl rings. Metabolic processes such as azo-reduction may be activating or detoxifying. the low but significant correlation between animal carcinogenicity and short-term test data may be increased with further screening, especially involving chromosome assays. It is suggested that a human cancer hazard may exist where significant quantities of finished benzidine dye samples are handled. Such risks from exposures to other colours and the possibility of human germ-line mutation induction by dyestuffs cannot be meaningfully assessed.