Gene/Protein Disease Symptom Drug Enzyme Compound
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Query: EC:3.1.6.1 (sulfatase)
 3,205 document(s) hit in 31,850,051 MEDLINE articles (0.00 seconds)

Sodium/copper chlorophyllin (CHL) is a water-soluble derivative of chlorophyll that exhibits antimutagenic activity in several short-term genotoxicity assays and inhibits carcinogen-DNA binding in vivo. The effect of CHL pretreatment on the excretion of mutagens in the urine and feces of male Sprague-Dawley rats has been studied using the Salmonella mutagenicity assay. Animals were given 1 percent CHL in the drinking water for 2 days before administering a single dose of 2-amino-3-methylimidazo-[4,5-f]quinoline (IQ) by oral gavage. Rats pretreated with CHL had higher levels of mutagens in the urine and feces compared with animals given IQ alone; 48 hr after IQ administration, the total mutagenic dose excreted was < 4% in controls vs. 18% in rats given CHL. Mutagenicity required the presence of an activation system, was unaffected by treatment with beta-glucuronidase or arylsulfatase, and in both the urine and feces was accounted for by increased elimination of unmetabolized parent compound. The results support the view that CHL may operate in vivo as a "desmutagen" or interceptor molecule, interacting with IQ in the gut and tissues, and reducing carcinogen bioavailability.
Environ Mol Mutagen 1992
PMID:Chlorophyllin-enhanced excretion of urinary and fecal mutagens in rats given 2-amino-3-methylimidazo[4,5-f]quinoline. 139 10

Comparison of the mutagenicity of nine isomeric benzo(a)pyrenyl [B(a)P] phenols conjugated with either sulfate or glucuronide was carried out using strain Salmonella typhimurium TA98. Of the nine conjugates tested, only B(a)P-1-sulfate was mutagenic. Accordingly, the mutagenicity of B(a)P-1-sulfate was compared with that of B(a)P and 1-hydroxybenzo(a)pyrene [B(a)P-1-OH] in the presence and absence of rat lung S9 and Aroclor-induced liver S9 with and without an NADPH-generating system. B(a)P-1-sulfate was slightly mutagenic, whereas B(a)P and the 1-hydroxy derivative were nonmutagenic when S9 fractions and NADPH were omitted. Addition of induced liver S9 with NADPH caused mutagenicity with B(a) -1-OH greater than B(a)P greater than B(a)P-1-sulfate. B(a)P-1-sulfate was the only mutagenic species when lung S9 was added. This mutagenicity did not require NADPH. Sodium sulfite, an inhibitor of arylsulfatase, decreased the mutagenicity of B(a)P-1-sulfate. These data suggest that a unique mutagenic species is generated from B(a)P-1-sulfate via arylsulfatase in rat lung.
Environ Mol Mutagen 1992
PMID:Mutagenicity of benzo(a)pyrenyl-1-sulfate in the Ames test. 157 48

The metabolism of benzo(a)pyrene [B(a)P] to organic soluble and water soluble metabolites by transformable C3H10T1/2CL8 mouse embryo fibroblasts was studied as a function of time, B(a)P concentration, and cell density. The total formation of organic-soluble and water-soluble metabolites increased with incubation time from 4 to 48 h and with B(a)P concentration from 4 to 40 microM. As cell density increased, the metabolic rate decreased for organic-soluble and water-soluble products between 6,300 and 54,000 cells/cm2 probably due to decreases in B(a)P concentrations to values below saturation. Specific organic-soluble metabolites identified were B(a)P-pre-9,10-diols, B(a)P-9,10-diol, B(a)P-7,8-diol, B(a)P-3,6-quinone, B(a)P-3-phenol, and B(a)P-9-phenol. Water-soluble metabolites were subjected to enzymatic hydrolysis with beta-glucuronidase and aryl sulfatase to identify specific conjugated products. The sulfate conjugated metabolites identified were B(a)P-7,8-diol, B(a)P-pre-9,10-diols, B(a)P-9,10-diol, and B(a)P-3,6-quinone. The beta-glucuronic acid metabolites identified were B(a)P-pre-9,10-diols, B(a)P-3,6-quinone, and B(a)P-3-phenol. Patterns of metabolite formation rates are discussed as to their possible effect on morphological transformation rates in C3H10T1/2 cells with respect to incubation time and cell density.
Teratog Carcinog Mutagen 1986
PMID:Quantitative analysis of the metabolism of benzo(a)pyrene by transformable C3H10T1/2CL8 mouse embryo fibroblasts. 287 41

Di(2-ethylhexyl) terephthalate (DEHT) is a commercially produced chemical (Kodaflex DOTP) that is used as a general purpose, low-volatility plasticizer for polyvinyl chloride and other polymeric materials. Less than 30 million kilograms of DEHT are produced annually. DEHT is isomeric with di(2-ethylhexyl) phthalate (DEHP), a nongenotoxic rodent carcinogen whose mode of action has been suggested to derive from its ability to produce hepatocellular proliferation and/or hepatic peroxisome proliferation. Thus it is important to know the behavior of DEHT in genotoxicity assays in order to compare it with that of DEHP and other phthalate ester plasticizers. It is known from previously published studies that rats fed DEHT in the diet at 2,000 mg/kg produce urine that is negative in the Ames Salmonella bacterial mutagenicity assay in the presence and absence of induced rat liver S-9 and in the presence and absence of beta-glucuronidase/aryl sulfatase. Reported here are the results of direct testing of DEHT in the Ames plate incorporation assay, the Chinese hamster ovary/hypoxanthine guanine phosphoribosyl transferase (CHO/HGPRT) in vitro mammalian cell mutagenicity assay, and an in vitro chromosome aberrations assay using CHO cells. The results for mono(ethylhexyl) terephthalate (MEHT), a metabolite of DEHT, in the Ames Salmonella bacterial mutagenicity assay are also presented. All test results for both DEHT and MEHT were found to be negative, and it is therefore concluded that DEHT, like its isomeric relative DEHP, is not genotoxic.
Environ Mol Mutagen 1994
PMID:Genetic toxicology testing of di(2-ethylhexyl) terephthalate. 816 97

The production and storage of explosives has resulted in the environmental accumulation of the mutagen 2,4,6-trinitrotoluene (TNT). In order to characterize the production of mutagenic urinary metabolites, 6-week old male Fischer 344 rats were administered 75 mg of TNT/kg or DMSO vehicle by gavage. The animals were placed into metabolism cages, and urine was collected for 24 hr. Following filtration, metabolites in the urine were deconjugated with sulfatase and beta-glucuronidase and concentrated by solid phase extraction. The eluate was fractionated by reverse-phase high-performance liquid chromatography (HPLC) using acetonitrile/water, and the fractions, were solvent exchanged in DMSO by nitrogen evaporation. Each HPLC fraction was bioassayed in strains TA98, TA98NR, TA100, and TA100NR without metabolic activation using a microsuspension modification of the Salmonella histidine reversion assay. Fractions 3, 5-18, 21, 22, and 24-26 contained mutagens detected by strain TA98. In the nitroreductase-deficient strain TA98NR, some mutagenic activity was lost; however, fractions 3, 6, 9-11, 15, and 25 clearly contained direct-acting mutagens. Fewer fractions were positive in strain TA100 (9-16, 19, 20, and 25) with less activity observed in the nitroreductase deficient strain TA100NR (fractions 3, 12, 14, 15, and 25). Although some mutagenic activity coeluted with known TNT metabolite standards, there were still many unidentified mutagenic peaks.
Environ Mol Mutagen 1997
PMID:Mutagenicity of HPLC-fractionated urinary metabolites from 2,4,6-trinitrotoluene-treated Fischer 344 rats. 936 8

Due to its widespread use as a preemergent herbicide, alachlor has been detected as a groundwater contaminant. The procarcinogen, 2,6-dinitrotoluene (DNT), a by-product of the munitions industry and a precursor to polyurethane production, is found in the manufacturing waste stream. This study explores the effect of alachlor treatment on the bioactivation of DNT by examining urine mutagenicity, intestinal enzymes, and hepatic DNA adducts to detect changes in metabolism. Five-week-old male rats were treated daily by gavage with 50 mg/kg of alachlor for up to 5 weeks while control animals received an equal volume of peanut oil. At 1, 3, and 5 weeks following the initial alachlor dose, animals were administered p.o. 75 mg/kg DNT or DMSO. Urine was collected for 24 hr in metabolism cages. Following incubation with sulfatase and beta-glucuronidase, urines were individually concentrated by C-18 solid phase extraction, dried under N2, and prepared for bioassay in Salmonella typhimurium strain TA98 with and without metabolic activation. Urine from peanut oil- and alachlor-treated rots was not mutagenic. Even though calf thymus DNA-alachlor adducts formed in vitro, no hepatic DNA adducts were detected in vivo in these two treatment groups. Interestingly, a significant increase in excretion of mutagenic urine from DNT-treated rats was observed following 3 weeks of alachlor treatment in the absence of S9 (690 +/- 130 vs. 339 +/- 28 revertants/ml) which corresponded to increased DNT-related hepatic DNA adduct formation (5.90 +/- 0.88 adducts/10(8) nucleotides vs. 10.56 x +/- 0.59 adducts/10(8) nucleotides [relative adduct level (RAL)]). Elevation in the production of mutagenic urine from control and treated animals was linked to increases in intestinal nitroreductase and beta-glucuronidase activities; however, the only significant alachlor-related effects were an increase in small intestinal 1-week beta-glucuronidase and 5-week dehydrochlorinase activities. The increased urine mutagenicity and hepatic DNA adduct formation indicates that alachlor has a transient effect on DNT bioactivation that apparently is unrelated to intestinal bioactivation.
Environ Mol Mutagen 1998
PMID:Modulation of 2,6-dinitrotoluene genotoxicity by alachlor treatment of Fischer 344 rats. 958 66