Evaluation of the Presence of Mutagenic Dyes in Sediments from Cristais River

Azo dyes are largely used by coloring textiles and can contaminate the aquatic environment, including the sediment, through their release through effluent discharges. In this work the presence of mutagenic azo dyes was evaluated using Thin Layer Chromatography in sediment samples of the Cristais River upstream and downstream of an azo dye processing plant discharge area. Mutagenicity of the sediment samples was also analyzed using the Salmonella/microsome assay with the strain YG1041 in the presence and absence of S9. Extracts of benthic organisms collected in the same area were analyzed for the presence of dyes. The dyes CI Disperse Blue 373 and CI Disperse Orange 37 as well as three unknown fluorescent compounds were detected only in the sediment samples collected downstream of the industrial discharge. Activity was detected with the Salmonella assay in the three samples analyzed but higher values were obtained after the azo dye processing plant when compared to the reference site. This effect could be partially explained by the presence of the mutagenic dyes detected, considering their mutagenic potencies. No dyes were found in the extracts of the organisms. Further studies should be performed to evaluate the fate and effects of these dyes in the sediment and in the aquatic community and their potential to be transferred to the water column.     

Mutagenic and carcinogenic potential of a textile azo dye processing plant effluent that impacts a drinking water source

Recently a textile azo dye processing plant effluent was identified as one of the sources of mutagenic activity detected in the Cristais River, a drinking water source in Brazil [G.A. Umbuzeiro, D.A. Roubicek, C.M. Rech, M.I.Z. Sato, L.D. Claxton, Investigating the sources of the mutagenic activity found in a river using the Salmonella assay and different water extraction procedures, Chemosphere 54 (2004) 1589-1597]. Besides presenting high mutagenic activity in the Salmonella/microsome assay, the mutagenic nitro-aminoazobenzenes dyes CI Disperse Blue 373, CI Disperse Violet 93, and CI Disperse Orange 37 [G.A. Umbuzeiro, H.S. Freeman, S.H. Warren, D.P. Oliveira, Y. Terao, T. Watanabe, L.D. Claxton, The contribution of azo dyes in the mutagenic activity of the Cristais river, Chemosphere 60 (2005) 55-64] as well as benzidine, a known carcinogenic compound [T.M. Mazzo, A.A. Saczk, G.A. Umbuzeiro, M.V.B. Zanoni, Analysis of aromatic amines in surface waters receiving wastewater from textile industry by liquid chromatographic with eletrochemical detection, Anal. Lett., in press] were found in this effluent. After approximately 6 km from the discharge of this effluent, a drinking water treatment plant treats and distributes the water to a population of approximate 60,000. As shown previously, the mutagens in the DWTP intake water are not completely removed by the treatment. The water used for human consumption presented mutagenic activity related to nitro-aromatics and aromatic amines compounds probably derived from the cited textile processing plant effluent discharge [G.A. Umbuzeiro, D.A. Roubicek, C.M. Rech, M.I.Z. Sato, L.D. Claxton, Investigating the sources of the mutagenic activity found in a river using the Salmonella assay and different water extraction procedures, Chemosphere 54 (2004) 1589-1597; G.A. Umbuzeiro, H.S. Freeman, S.H. Warren, D.P. Oliveira, Y. Terao, T. Watanabe, L.D. Claxton, The contribution of azo dyes in the mutagenic activity of the Cristais river, Chemosphere 60 (2005) 55-64]. Therefore, it is important to evaluate the possible risks involved in the human consumption of this contaminated water. With that objective, one sample of the cited industrial effluent was tested for carcinogenicity in the aberrant crypt foci medium-term assay in colon of Wistar rats. The rats received the effluent in natura through drinking water at concentrations of 0.1%, 1%, and 10%. The effluent mutagenicity was also confirmed in the Salmonella/microsome assay with the strains TA98 and YG1041. There was an increased number of preneoplastic lesions in the colon of rats exposed to concentrations of 1% and 10% of the effluent, and a positive response for both Salmonella strains tested. These results indicate that the discharge of the effluent should be avoided in waters used for human consumption and show the sensitivity of the ACF crypt foci assay as an important tool to evaluate the carcinogenic potential of environmental complex mixtures.     

Mutagenicity of benzidine and benzidine-congener dyes and selected monoazo dyes in a modified Salmonella assay

We have evaluated the mutagenic activity of a series of diazo compounds derived from benzidine and its congeners o-tolidine, o-dianisidine and 3,3'-dichlorobenzidine as well as several monoazo compounds. The test system used was a modification of the standard Ames Salmonella assay in which FMN, hamster liver S9 and a preincubation step are used to facilitate azo reduction and detection of the resulting mutagenic aromatic amines. All of the benzidine and o-tolidine dyes tested were clearly mutagenic. The o-dianisidine dyes except for Direct Blue 218 were also mutagenic. Direct Blue 218 is a copper complex of the mutagenic o-dianisidine dye Direct Blue 15. Pigment Yellow 12, which is derived from 3,3'-dichlorobenzidine, could not be detected as mutagenic, presumably because of its lack of solubility in the test reaction mixture. Of the monoazo dyes tested, methyl orange was clearly mutagenic, while C.I. Acid Red 26 and Acid Dye (C.I. 16155; often referred to as Ponceau 3R) had marginal to weak mutagenic activity. Several commercial dye samples had greater mutagenic activity with the modified test protocol than did equimolar quantities of their mutagenic aromatic amine reduction products. Investigation of this phenomenon for Direct Black 38 and trypan blue showed that it was due to the presence of mutagenic impurities in these samples. The modified method used appears to be suitable for testing the mutagenicity of azo dyes, and it may also be useful for monitoring the presence of mutagenic or potentially carcinogenic impurities in otherwise nonmutagenic azo dyes.     

Decolorization and removal of textile and non-textile dyes from polluted wastewater and dyeing effluent by using potato (Solanum tuberosum) soluble and immobilized polyphenol oxidase

Celite bound potato polyphenol oxidase preparation was employed for the treatment of wastewater/dye effluent contaminated with reactive textile and non-textile dyes, Reactive Blue 4 and Reactive Orange 86. The maximum decolorization was found at pH 3.0 and 4.0 in case of Reactive Blue 4 and Reactive Orange 86, respectively. Immobilized potato polyphenol oxidase was significantly more effective in decolorizing the individual dye and complex mixtures of dyes as compared to soluble enzyme. The absorption spectra of the treated and untreated dye mixture and dyeing effluent exhibited a marked difference in the absorption value at various wavelengths. The polluted water contaminated with an individual dye or mixtures of dyes treated with soluble and immobilized potato polyphenol oxidase resulted in the remarkable loss in total organic carbon.     

Decolorization Screening of Synthetic Dyes by Anaerobic Methanogenic Sludge Using a Batch Decolorization Assay

The nonspecific ability of anaerobic sludge bacteria obtained from cattle dung slurry was investigated for 17 different dyes in a batch assay system using sealed serum vials. Experiments using Reactive Violet 5 (RV 5) showed that sludge bacteria could effectively decolorize solutions having dye concentrations up to 1000 mg l⁻¹ with a decolorization efficiency of above 75% during 48 h of incubation. Headspace gas composition of anaerobic batch systems for varying dye concentration revealed that lower concentrations of RV 5 (upto 500 mg l⁻¹) were found to be stimulatory to the methanogenic activity of sludge bacteria. However at higher dye concentrations, the headspace gas composition was found to be similar to batch assay controls without dye, indicating that dye at higher concentrations was inhibitory to methanogenic bacteria of sludge. The optimum inoculum and incubation temperature for maximum decolorization of RV 5 was found to be 9.0 g l⁻¹(in terms of total solids) and 37°C, respectively. Of sixteen other dyes tested, nine (Reactive Black 5, Reactive Blue 31, Reactive Blue 28, Reactive Red HE8B, Reactive Yellow, Reactive Golden Yellow, Mordant Orange, Novatic Olive R S/D & Navilan Yellow GL) were decolorized with more than 88% efficiency; three (Orange II, Navy Blue HER & Novatic Blue BC S/D) were decolorized with about 50–65% efficiency, whereas other three dyes (Procion Orange H2R, Procion Brilliant Blue HGR & Novatic Blue BC S/D) were decolorized with less than 40% efficiency. Though Ranocid Fast Blue was decolorized with about 92.5% efficiency, this was merely due to sorption, whereas the other dyes were decolorized due to biotransformation.     

The significance of azo-reduction in the mutagenesis and carcinogenesis of azo dyes

Azo dyes are widely used in textile, printing, cosmetic, drug and food-processing industries. They are also used extensively in laboratories as either biological stains or pH indicators. The extent of such use is related to the degree of industrialization. Since intestinal cancer is more common in highly industrialized countries, a possible connection may exist between the increase in the number of cancer cases and the use of azo dyes. Azo dyes can be reduced to aromatic amines by the intestinal microflora. The mutagenicity of a number of azo dyes is reviewed in this paper. They include Trypan Blue, Ponceau 3R, Pinceau 2R, Methyl Red, Methyl Yellow, Methyl Orange, Lithol Red, Orange I, Orange II, 4-Phenylazo-Naphthylamine, Sudan I, Sudan IV, Acid Alizarin Violet N, Fast Garnet GBC, Allura Red, Ponceau SX, Sunset Yellow, Tartrazine, Citrus Red No. 2, Orange B, Yellow AB, Carmoisine, Mercury Orange, Ponceau S, Versatint Blue, Phenylazophenol, Evan's Blue and their degraded aromatic amines. The significance of azo reduction in the mutagenesis and carcinogenesis of azo dyes is discussed.     

Mutagenicity test of dyes used in cosmetics with the Salmonella/mammalian-microsome test.

37 dyes including 3 anthraquinone, 22 azo; 5 xanthene, 5 fluorandiol, and 2 thioindigo dyes, were tested for mutagenic potential with the Salmonella/mammalian-microsome test. Two frame-shift histidine mutants (TA1537 and TA98) and two base-pair substituted histidine mutants (TA1535 and TA100) of Salmonella typhimurium were employed. Both the spot test and the plate-incorporation assay indicated that one azo dye, D&C Orange No. 17, was mutagenic with three of the bacterial test strains. The mutagenic response of D&C Orange No. 17 was depressed by the addition of the microsomal fractions from rat livers. Of the chemicals used to synthesize D&C Orange No; 17 was depressed by the addition of the microsomal fractions from rat livers. Of the chemicals used to synthesize D&C Orange No. 17, beta-naphthol was not mutagenic but 2,4-dinitroaniline was mutagenic to the same Salmonella strains as D&C Orange No. 17 . Dimethyl sulfoxide extracts of lipsticks of similar formula but without D&C Orange No. 17 were tested in the plate incorporation assay. Only those containing D&C Orange No. 17 were mutagenic and the dye was mutagenic at concentrations consumed in normal daily use.     

Isolation of the mutagenic and DNA adduct-inducing components from a commercial preparation of HC blue 1 using Salmonella (TA98) bioassay-directed HPLC fractionation.

In the present study we report the separation of the mutagenic impurities from the nitrophenylenediamine hair dye HC Blue 1. This was accomplished by bioassay-directed HPLC fractionation, using Salmonella strain TA98 and reverse phase HPLC analysis. The mutagenic fraction eluted between 80 and 90% methanol, whereas the HPLC fraction containing the parent compound HC Blue 1 eluted with 30% methanol and was non-mutagenic. 100% of the mutagenic activity applied to the column was recovered in fractions that did not possess the blue color of HC Blue 1. Also, HPLC-purified HC Blue 1 did not form DNA adducts (32P-postlabeling) in Salmonella strain TA98. On the other hand, commercial HC Blue 1 and the mutagenic fraction derived from commercial HC Blue 1 (HPLC-isolated) gave similar DNA-adduct profiles that consisted of 7 adducts. DNA adduction was examined concomitantly with mutagenicity and toxicity studies on the HC Blue 1 samples in TA98. The data indicated that, in Salmonella, both the mutagenicity and DNA adduction of commercial HC Blue 1 are due to impurities and not the parent compound.     

Mutagenicity of selected sulfonated azo dyes in the Salmonella/microsome assay: use of aerobic and anaerobic activation procedures

A selection of 16 sulfonated azo dyes of both the monoazo type and diazo dyes based on benzidine, o-tolidine and o-dianisidine were assayed for mutagenicity in Salmonella typhimurium strains TA98 and TA100 employing both aerobic and anaerobic preincubation procedures. 3 food dyes, FD & C Red No. 40 and Yellows No. 5 and No. 6 were non-mutagenic in all tests. 5 dyes were mutagenic with aerobic treatment (trypan blue, Pontacyl Sky Blue 4BX, Congo Red, Eriochrome Blue Black B, dimethylaminoazobenzene) and 6 were mutagenic aerobically with riboflavin and cofactors (Deltapurpurin, trypan blue, Pontacyl Sky Blue 4BX, Congo Red, methyl orange, Ponceau 3R). Anaerobic preincubation involving enzymatic reduction of the dyes led to a different pattern of mutagenicity, with trypan blue giving much enhanced mutagenicity; Eriochrome Blue Black B, Pontacyl Sky Blue 4BX, Deltapurpurin and Congo Red exhibiting similar activity to aerobic preincubation; and methyl orange and Ponceau 3R yielding no mutagenicity. The results are interpreted with respect to an hypothesis involving partial reduction of the azo bond under differing degrees of aerobiosis via azo-anion radicals and hydrazo intermediates.     

Biodegradation of azo and phthalocyanine dyes by Trametes versicolor and Bjerkandera adusta

Eighteen fungal strains, known for their ability to degrade lignocellulosic material or lignin derivatives, were screened for their potential to decolorize commercially used reactive textile dyes. Three azo dyes, Reactive Orange 96, Reactive Violet 5 and Reactive Black 5, and two phthalocyanine dyes, Reactive Blue 15 and Reactive Blue 38, were chosen as representatives of commercially used reactive dyes. From the 18 tested fungal strains only Bjerkandera adusta, Trametes versicolor and Phanerochaete chrysosporium were able to decolorize all the dyes tested. During degradation of the nickel-phthalocyanine complex, Reactive Blue 38, by B. adusta and T. versicolor respectively, the toxicity of this dye to Vibrio fischeri was significantly reduced. In the case of Reactive Violet 5, a far-reaching detoxification was achieved by treatment with B. adusta. Reactive Blue 38 and Reactive Violet 5 were decolorized by crude exoenzyme preparations from T. versicolor and B. adusta in a H₂O₂-dependent reaction. Specific activities of the exoenzyme preparations with the dyes were determined and compared to oxidation rates by commercial horseradish peroxidase. Received: 3 February 1997 / Received revision: 9 April 1997 / Accepted: 13 April 1997     

Decolorization and degradation of Disperse Blue 79 and Acid Orange 10, by Bacillus fusiformis KMK5 isolated from the textile dye contaminated soil

The release of azo dyes into the environment is a concern due to coloration of natural waters and due to the toxicity, mutagenicity and carcinogenicity of the dyes and their biotransformation products. The dye degrading bacterial strain KMK 5 was isolated from the textile dyes contaminated soil of Ichalkaranji, Maharashtra, India. It was identified as Bacillus fusiformis based on the biochemical and morphological characterization as well as 16S rDNA sequencing. KMK 5 could tolerate and degrade azo dyes, Disperse Blue 79 (DB79) and Acid Orange 10 (AO10) under anoxic conditions. Complete mineralization of DB79 and AO10 at the concentration of 1.5g/l was observed within 48h. This degradation potential increased the applicability of this microorganism for the dye removal.     

Developing azo and formazan dyes based on environmental considerations: Salmonella mutagenicity

In previous papers, the synthesis and chemical properties of iron-complexed azo and formazan dyes were reported. It was shown that in certain cases iron could be substituted for the traditionally used metals such as chromium and cobalt, without having an adverse effect on dye stability. While these results suggested that the iron analogs were potential replacements for the commercially used chromium and cobalt prototypes, characterization of potentially adverse environmental effects of the new dyes was deemed an essential step in their further development. The present paper provides results from using the Salmonella/mammalian microsome assay to determine the mutagenicity of some important commercial metal complexed dyes, their unmetallized forms, and the corresponding iron-complexed analogs. The study compared the mutagenic properties of six unmetallized azo dyes, six commercial cobalt- or chromium-complexed azo dyes, six iron-complexed azo dyes, six unmetallized formazan dyes, and six iron-complexed formazan dyes. The results of this study suggest that the mutagenicity of the unmetallized dye precursors plays a role in determining the mutagenicity of the iron-complexes. For the monoazo dye containing a nitro group, metal complex formation using iron or chromium decreased or removed mutagenicity in TA100; however, little reduction in mutagenicity was noted in TA98. For the formazan dye containing a nitro group, metal-complex formation using iron increased mutagenicity. Results varied for metal-complexes of azo and formazan dyes without nitro groups, but in general, the metal-complexed dyes based on mutagenic ligands were also mutagenic, while those dyes based on nonmutagenic ligands were nonmutagenic.     

Toxic genetic effects of flunitrazepam

The mutagenic activity of Flunitrazepam, the active ingredient of the drug Rohypnol, has been investigated by using the Salmonella/microsome mutagenicity test. A dose-related mutagenic effect was observed on Salmonella typhimurium strain TA 100 either in the absence or in the presence of a rat liver microsomal fraction (S9) as in vitro metabolic activation system. By adopting a modification of the Salmonella test, the mutagenicity of urines from rats or patients treated with the drug was evaluated. In these cases mutagenic activity was detected toward the Salmonella strains TA 98 and TA 100 both in presence and in absence of the metabolic activation system. The data indicate that Flunitrazepam and/or its urinary metabolites can induce both base-pair substitutions or frame-shift point mutations.     

Azo reduction of trypan blue to a known carcinogen by a cell-free extract of a human intestinal anaerobe.

The azo reductase activity of a cell-free extract of Fusobacterium sp. 2 is characterized using trypan blue as a substrate. Either chemical reduction of this dye with sodium hydrosulfite or reduction by the cell-free extract produces a mutagenic product, o-tolidine. The o-tolidine is mutagenic in the Ames Salmonella/mammalian-microsome mutagenicity test when activated by a rat liver S9 preparation.     

Comparison of static and shake culture in the decolorization of textile dyes and dye effluents byPhanerochœte chrysosporium

Decolorization of several dyes (Red HE-8B, Malachite Green, Navy Blue HE-2R, Magenta, Crystal Violet) and an industrial effluent with growing cells ofPhanerochœte chrysosporium in shake and static culture was demonstrated. All the dyes and the industrial effluent were decolorized to some extent with varying percentages of decolorization (20–100%). The rate of decolorization was very rapid with Red HE-8B, an industrial dye. Decolorization rates for all the dyes in static condition were found to be less than the shake culture and also dependent on biomass concentration.     

Identification of a new mutagen, 4,4'-diamino-3,3'-dichloro-5-nitrobiphenyl, in river water flowing through an industrial area in Wakayama, Japan

3,3'-Dichlorobenzidine (DCB), which has been assigned as a possible carcinogen to humans (Group 2B) by IARC, is produced as a raw material in the manufacture of polymers and dye intermediates. In our previous paper, we identified DCB as an indirect-acting mutagenic constituent in the water concentrates from the Waka River, which flows through an industrial area in Wakayama, Japan. In this study, we have identified a novel mutagen in the water samples from the Waka River. Organic chemicals in the river water were adsorbed to blue rayon at the site where effluents from chemical plants and a sewage plant were discharged into the river. The adsorbate was highly mutagenic in Salmonella YG1024 in the presence and absence of S9 mix, inducing 440,000 and 170,000 revertants/g blue rayon equivalent, respectively. Two mutagenic fractions, which accounted for 18% and 12% of the total mutagenicity of the water concentrate in YG1024 with S9 mix, were separated by HPLC with a reversed-phase column following Sephadex LH20 column chromatography. Both fractions were further separated by HPLC using reversed-phase columns. On the basis of spectral analysis and co-chromatography using an authentic chemical standard, one mutagen in the former fraction was identified as DCB and one mutagen in the latter fraction was deduced to be a novel chemical, a 5-nitro derivative of DCB (5-nitro-DCB; 4,4'-diamino-3,3'-dichloro-5-nitrobiphenyl). 5-Nitro-DCB showed strong mutagenicity in YG1024 especially with S9 mix, inducing 24,200 revertants/microg. 5-Nitro-DCB was detected in water concentrates in the range from less than detection limit to 6.9 microg/g of blue rayon. DCB was also detected in the range from 13.2 to 104 micro/g of blue rayon. These results demonstrate that Waka River water might be continually contaminated with the indirect-acting mutagens DCB and 5-nitro-DCB as major mutagenic constituents of the river water.     

Mutagenicity of adsorbates to a copper-phthalocyanine derivative recovered from municipal river water

Blue cotton, bearing a covalently bound copper-phthalocyanine derivative capable of adsorbing polycyclic aromatic hydrocarbons (PAHs) over 3 rings, was applied to recover mutagens from the Katsura River which is a tributary of the Yodo River. The Ames Salmonella/microsome assay with TA98 and TA100 of the blue cotton concentrate recovered from the river water demonstrated indirect mutagenicity toward TA98. The subfractions separated by Sephadex G-25 gel chromatography also showed direct mutagenicity in strains YG1021 and YG1024, the nitroreductase- and O-acetyltransferase-overproducing derivatives of TA98; this activity was greatly increased by the addition of S9 mix, especially in YG1024. However, these subfractions were less mutagenic with TA98NR or TA98/1,8-DNP6, regardless of whether S9 mix was present or not. The behaviors of these mutagenic activities therefore suggested that frameshift mutagens of both directly mutagenic nitroarenes and indirectly mutagenic aminoarenes were present in the blue cotton concentrate from the river water.     

Mutagenesis in Salmonella after metabolic activation of carcinogenic azo dyes and their isomers by liver S9 from rats, mice and hamsters

The mutagenicities of 3'-methyl-N,N-dimethyl-4-aminoazobenzene (3'-Me-DAB) and 3'-CH2OH-DAB, potent hepatocarcinogens, activated by rat-liver S9 were compared with those of their isomers (2'- or 4'-substituted DAB) and with those obtained with liver S9 from mice, hamsters and man. All 6 aminoazo dyes showed positive mutagenicity on both strains TA98 and TA100 in the presence of liver S9 from rats pretreated with polychlorinated biphenyls (PCB) whereas 3'-Me-DAB and 3'-CH2OH-DAB were negative in the presence of S9 from other organs of rats and human liver. 3'-Me-DAB and 3'-CH2OH-DAB also showed negative or only a weak mutagenicity in the presence of liver S9 from non-treated animals. Treatment of the muta-carcinogens by liver S9 from PCB-treated mice or hamsters exerted mutagenicity on TA98, but less than that seen with rat-liver S9. The activity of 3'-Me-DAB in the presence of female rat-liver S9 was lower than that obtained with the male. Thus a specificity in the aminoazo dye carcinogenesis in regard to species, sex and organ was also observed in the mutagenic effects of 3'-Me-DAB on Salmonella.     

Mutagenicity testing of some commonly used dyes.

Seventeen commonly used dyes and 16 of their metabolites or derivatives were tested in the Salmonella-mammalian microsome mutagenicity test. Mutagens active with and without added Aroclor-induced rat liver microsome preparations (S9) were 3-aminopyrene, lithol red, methylene blue (USP), methyl yellow, neutral red, and phenol red. Those mutagenic only with S9 activation were 4-aminopyrazolone, 2,4-dimethylaniline, N,N-dimethyl-p-phenylenediamine, methyl red, and 4-phenyl-azo-1-naphthylamine. Orange II was mutagenic only without added S9. Nonmutagenic azo dyes were allura red, amaranth, ponceau R, ponceau SX, sunset yellow, and tartrazine. Miscellaneous dyes not mutagenic were methyl green, methyl violet 2B, and nigrosin. Metabolites of the azo dyes that were not mutagenic were 1-amino-2-naphthol hydrochloride, aniline, anthranilic acid, cresidine salt, pyrazolone T,R-amino salt (1-amino-2-naphthol-3,6-disulfonic disodium salt), R-salt, Schaeffer's salt (2-naphthol-6-sulfonic acid, sodium salt), sodium naphthionate, sulfanilamide, and sulfanilic acid. 4-Amino-1-naphthalenesulfonic acid sodium salt was also not mutagenic. Fusobacterium sp. 2 could reductively cleave methyl yellow to N,N-dimethyl-p-phenylenediamine which was then activated to a mutagen.     

The presence of genotoxic and bioactive components in indigo dyed fabrics--a possible health risk?

Extracts of pure cotton and jeans fabrics were tested for mutagenicity in Salmonella typhimurium strains TA98 and TA100. The vat dye indigo, technical grade as well as 98% and greater than 99.5% pure, was also tested for mutagenicity. Synthetic indigo, indirubin and isatin were tested for TCDD receptor affinity in competition experiments in vitro. The mutagenicity of the extracts was associated with the cotton denim and nondyed cotton gave only marginal effects. The mutagenicity of the indigo dyed fabrics was dependent on type and treatment of the fabrics. Extracts of both bleached and nonbleached jeans gave mutagenic effects on TA98 +/- S9 and TA100 +/- S9. The greatest effects were seen in the presence of S9. Bleaching gave an additional increase in the mutagenicity in the absence of S9. Normal washing of the fabrics after bleaching reduced the mutagenicity. Synthetic indigo of technical grade or 98% pure showed mutagenic effects, especially on TA98 + S9. Further purification to 99.5% reduced the mutagenicity to 24 revertants/mg (6.2 rev/mu mole). Considering the amount of indigo in the extracts and its low mutagenicity, the genotoxicity of jeans extracts must be caused by other unknown components. However, indigo showed a high (Kd = 1.9 nM) affinity for the Ah or TCDD receptor. Indigo can therefore still be a potential health risk either by eliciting toxic effects of other compounds or by being a nongenotoxic carcinogen. The worldwide use of jeans with a possible exposure of a large population to genotoxic and biologically active components emphasizes the need for a more thorough characterization of these effects.