Mutagenicity of benzotrichloride and related compounds.

Benzotrichloride (BTC), benzal chloride (BDC), benzyl chloride (BC) and benzoyl chloride (BOC) were surveyed for their mutagenicity in microbial systems such as rec-assay using Bacillus subtilis and reversion assays using E. coli WP2 and Ames Salmonella TA strains with or without metabolic activation in vitro. BTC and BDC required metabolic activation for their mutagenic activities in several strains of E. coli and Salmonella. The mutagenic metabolites of these compounds may not have been produced by hydrolysis. BC was weakly mutagenic without metabolic activation. Only BOC exhibited no mutagenic activity in the detection procedures used. The mutagenic metabolite of BTC might be very unstable under our experimental conditions. The strain E. coli WP2 try hcr was more sensitive than E. coli B/r WP2 try (hcr+) with regard to the mutagenicity of BTC.     

Microbial oxidation of dehydroepiandrosterone and related compounds.

The oxidation of dehydroepiandrosterone (DHEA), 4-androstene-3, 17-dione, and estrone with Streptomyces roseochromogenes NRRL B-1233 was studied. The oxidation products were isolated and identified as as 16alpha-hydroxy-DHEA, 16alpha-hydroxy-4-androstene-3,17-dione and 16alpha-hydroxyestrone. The yields of these three products were 85%, 41% and 18%, respectively. This indicates the substrate stereospecificity of 16alpha-hydroxylase of the organism. An interrelationship between cell growth and the formation of 16alpha-hydroxylated steroid was observed in any case. For formation of 16alpha-hydroxy-DHEA, 16alpha-hydroxylase showed good activity at DHEA concentration of 3.47 x 10(-4)M. In the case of DHEA, 16alpha-hydroxy-4-androstene-3,17-dione and 5-androstene-3beta, 16alpha, 17beta-triol were obtained after the yield of 16alpha-hydroxy-DHEA reached the maximum yield for about 30 hr. The oxidation pathway of DHEA is discussed.     

Antioxidant effects of dopamine and related compounds.

The antioxidant and free radical scavenging effects of dopamine, noradrenaline, tyramine, and tyrosine were investigated and compared with alpha-tocopherol. The antioxidant effect of dopamine and its related compounds on peroxidation of linoleic acid were in the order of dopamine > alpha-tocopherol = tyramine > tyrosine > noradrenaline as measured by the thiocyanate method. These amine compounds had reducing power, and a scavenging effect on reactive oxygen species, i.e., superoxide anion and hydroxyl radical. The results for reducing power and scavenging effect of these amine compounds had a similar trend as their inhibition of linoleic acid peroxidation. The antioxidant activity of these amine compounds in soybean oil was also evaluated by the Rancimat method. The induction time to reach 100 meq/kg peroxide value (POV) of soybean oil for dopamine, alpha-tocopherol, tyramine, tyrosine, noradrenaline, and control were 9.0, 8.2, 8.0, 6.4, 4.6, and 4.3 h, respectively. The antioxidant efficacy of amine compounds seems to be correlated with the numbers of hydroxy groups and their position on the phenolic ring.     

Mutagenicity testing of imidazole and related compounds.

Ames tests have been performed with imidazole and its principal metabolites, hydantoin and hydantoic acid. N-Acetyl-imidazole, a potential metabolite resulting from the action of intestinal bacteria, and histamine, a structurally related compound which is widely distributed in mammalian tissues, have also been tested. Imidazole and histamine were also tested in the UDS assay in primary rat hepatocytes, while imidazole alone was tested in the M2-C3H mouse fibroblast malignant transformation assay. Imidazole gave consistently negative results in the Ames test, the UDS assay and the transformation assay. The three metabolites of imidazole, namely hydantoin, hydantoic acid and N-acetyl-imidazole, all gave negative results in the Ames test. Histamine gave no evidence of mutagenic activity in the Ames test or of genotoxicity in the UDS assay. These results indicate that imidazole and its metabolites are unlikely to present a mutagenic or carcinogenic hazard.     

Infrared and Raman spectra of phosphatidyl-ethanolamine and related compounds.

Infrared and Raman spectra of phosphatidylethanolamine from Escherichia coli, L-alpha-glycero-phosphorylethanolamine and 0-phosphorylethanolamine were obtained. Most of the bands were assigned to each vibrational mode based on the N deuteration effect, comparison of the intensity in the infrared and Raman spectra and the depolarization degree measurement in the Raman spectra. The spectra of phosphatidylethanolamine can be interpreted by assuming that the molecule takes the dipolar ionic structure both in non-polar solvent and in solid.     

Microbial breakdown of halogenated aromatic pesticides and related compounds.

Considerable progress has been made in the last few years in understanding the mechanisms of microbial degradation of halogenated aromatic compounds. Much is already known about the degradation mechanisms under aerobic conditions, and metabolism under anaerobiosis has lately received increasing attention. The removal of the halogen substituent is a key step in degradation of halogenated aromatics. This may occur as an initial step via reductive, hydrolytic or oxygenolytic mechanisms, or after cleavage of the aromatic ring at a later stage of metabolism. In addition to degradation, several biotransformation reactions, such as methylation and polymerization, may take place and produce more toxic or recalcitrant metabolites. Studies with pure bacterial and fungal cultures have given detailed information on the biodegradation pathways of several halogenated aromatic compounds. Several of the key enzymes have been purified or studied in cell extracts, and there is an increasing understanding of the organization and regulation of the genes involved in haloaromatic degradation. This review will focus on the biodegradation and biotransformation pathways that have been established for halogenated phenols, phenoxyalkanoic acids, benzoic acids, benzenes, anilines and structurally related halogenated aromatic pesticides. There is a growing interest in developing microbiological methods for clean-up of soil and water contaminated with halogenated aromatic compounds.     

Comparative effects of ammonia and related compounds on poliovirus.

The abilities of ammonia and related compounds to inactivate poliovirus were compared. Compounds virucidal at pH 9.5 had the following order of activities: ethylamine greater than propylamine, dimethylamine, methylamine greater than ammonia greater than 2-methoxyethylamine.     

Induction of sporulation by inhibitory purines and related compounds.

Sporulation of Bacillus subtilis can be induced, in the presence of excess ammonia, glucose and phosphate, by many purine derivatives under conditions of partial growth inhibition. Some of the compounds are known inhibitors of purine nucleotide synthesis. For most compounds the effect is counteracted by adenine and guanine. Partial growth inhibition by amethopterin (methotrexate) causes sporulation in the absence of purines but not in their presence. Unable to induce sporulation at any concentration are inhibitors of DNA, RNA, and protein synthesis as well as base or amino acid analogs that are incorporated into these polymers.     

Comparative effects of ammonia and related compounds on poliovirus.

The abilities of ammonia and related compounds to inactivate poliovirus were compared. Compounds virucidal at pH 9.5 had the following order of activities: ethylamine greater than propylamine, dimethylamine, methylamine greater than ammonia greater than 2-methoxyethylamine.     

Synthesis and antitumoral activities of marine ent-chromazonarol and related compounds.

Efficient syntheses of ent-isozonarol (6a), ent-isozonarone (7a) and ent-chromazonarol (8) from (-)-sclareol (12) are described. 6a and 7a show a significative antitumoral activity.     

Synthesis of prumycin and related compounds

Prumycin (1) and related compounds have been synthesized from benzyl 2-(benzyloxycarbonyl)amino-2-deoxy-5,6-O-isopropylidene-β-d-glucofuranoside (4). Benzoylation of 4, followed by deisopropylidenation, gave benzyl 3-O-benzoyl-2-(benzyloxycarbonyl)amino-2-deoxy-β-d-glucofuranoside (6), which was converted, via oxidative cleavage at C-5–C-6 and subsequent reduction, into the related benzyl β-d-xylofuranoside derivative (7). Benzylation of 3-O-benzoyl-2-(benzyloxycarbonyl)-amino-2-deoxy-d-xylopyranose (8), derived from 7 by hydrolysis, afforded the corresponding derivatives (9, 11) of β- and α-d-xylopyranoside, and compound 7 as a minor product. Treatment of benzyl 3-O-benzoyl-2-(benzyloxycarbonyl)amino-2-deoxy-4-O-mesyl-β-d-xylopyranoside 10, formed by mesylation of 9, with sodium azide in N,N-dimethylformamide gave benzyl 4-azido-3-O-benzoyl-2-(benzyloxy-carbonyl)amino-2,4-dideoxy-α-l-arabinopyranoside (13), which was debenzoylated to compound 14. Selective reduction of the azide group in 14, and condensation of the 4-amine with N-[N-(benzyloxycarbonyl)-d-alaninoyloxy]succinimide, gave the corresponding derivative (15) of 1. Reductive removal of the protecting groups of 15 afforded 1. Prumycin analogs were also synthesized from compound 14. Evidence in support of the structures assigned to the new derivatives is presented.     

Metabolism of camphors and related compounds

1. The metabolism of (+/-)-norcamphor, (+)-camphor, (-)-camphor, (+)-epicamphor, (+/-)-camphorquinone, (+/-)-camphane-2,5-dione and camphane was investigated in rabbits. All the compounds except camphane-2,5-dione increased the content of glucuronide in the urine. 2. (+/-)-Norcamphor was reduced to endo-norborneol; (+)-camphor, contrary to expectation, was reduced to (+)-borneol, as well as being hydroxylated to (+)-5-endo-hydroxycamphor and (+)-3-endo-hydroxycamphor, 5-endo-hydroxycamphor being the predominant product. (+)-Epicamphor was reduced mainly to (+)-epiborneol; (+/-)-camphorquinone gave 3-endo-hydroxycamphor and 2-endo-hydroxyepicamphor, the former being the major metabolite. (+/-)-Camphane-2,5-dione was reduced to 5-endo-hydroxycamphor. Camphane was hydroxylated to borneol and epiborneol, the latter predominating. 3. An explanation of these findings is given in terms of steric hindrance and thermodynamic stability. 4. The possibility was investigated that NADH was involved in the reductions.