Degradation of halogenated aliphatic compounds by the ammonia- oxidizing bacterium Nitrosomonas europaea.

Suspensions of Nitrosomonas europaea catalyzed the ammonia-stimulated aerobic transformation of the halogenated aliphatic compounds dichloromethane, dibromomethane, trichloromethane (chloroform), bromoethane, 1,2-dibromoethane (ethylene dibromide), 1,1,2-trichloroethane, 1,1,1-trichloroethane, monochloroethylene (vinyl chloride), gem-dichloroethylene, cis- and trans-dichloroethylene, cis-dibromoethylene, trichloroethylene, and 1,2,3-trichloropropane, Tetrachloromethane (carbon tetrachloride), tetrachloroethylene (perchloroethylene), and trans-dibromoethylene were not degraded.     

Degradation pathways of trichloroethylene and 1,1,1-trichloroethane by Mycobacterium sp. TA27

We analyzed the kinetics and metabolic pathways of trichloroethylene and 1,1,1-trichloroethane degradation by the ethane-utilizing Mycobacterium sp. TA27. The apparent Vmax and Km of trichloroethylene were 9.8 nmol min(-1) mg of cells(-1) and 61.9 microM, respectively. The apparent Vmax and Km of 1,1,1-trichloroethane were 0.11 nmol min(-1) mg of cells(-1) and 3.1 microM, respectively. 2,2,2-trichloroethanol, trichloroacetic acid, chloral, and dichloroacetic acid were detected as metabolites of trichloroethylene. 2,2,2-trichloroethanol, trichloroacetic acid, and dichloroacetic acid were also detected as metabolites of 1,1,1-trichloroethane. The amounts of 2,2,2-trichloroethanol, trichloroacetic acid, chloral, and dichloroacetic acid derived from the degradation of 3.60 micromol trichloroethylene were 0.16 micromol (4.4%), 0.11 micromol (3.1%), 0.02 micromol (0.6%), and 0.02 micromol (0.6%), respectively. The amounts of 2,2,2-trichloroethanol, trichloroacetic acid and dichloroacetic acid derived from the degradation of 1.73 micromol 1,1,1-trichloroethane were 1.48 micromol (85.5%), 0.22 micromol (12.7%), and 0.02 micromol (1.2%), respectively. More than 90% of theoretical total chloride was released in trichloroethylene degradation. Chloral and 2,2,2-trichloroethanol were transformed into each other, and were finally converted to trichloroacetic acid, and dichloroacetic acid. Trichloroacetic acid and dichloroacetic acid were not degraded by strain TA27.     

Influence of acetone on the severity of the liver injury induced by haloalkane mixtures.

Acetone potentiation of haloalkane-induced liver injury is a well-known phenomenon. Acetone-treated rats challenged with a trichloroethylene-CCl4 mixture exhibit a more sever liver injury than that predicted by the addition of the single potentiating effects of each. The purpose of the present study was to determine if acetone exerted similar interactions with other haloalkane mixtures. The testing protocol used was designed and performed to allow categorization of interactions occurring among two or three agents. Rats were treated (p.o.) with corn oil or acetone (10.2 mmol/kg) and were administered (i.p.) 18 h later 1,1-dichloroethylene (0.6 mmol/kg), trichloroethylene (5.6 mmol/kg), tetrachloroethylene (19.6 mmol/kg), 1,1,1-trichloroethane (10.0 mmol/kg), 1,1,2-trichloroethane (1.1 mmol/kg), 1,1,2,2-tetrachloroethane (1.0 mmol/kg), CHCl3 (6.2 mmol/kg), CCl4 (1.0 mmol/kg), or a mixture of two haloalkanes (all 28 combinations were tested). Liver injury was assessed 24 h later using plasma alanine aminotransferase activity and a quantitative histological evaluation. In corn oil pretreated rats, the hepatotoxic responses observed for the 28 mixtures were additive for 26 of 28 mixtures and supra-additive for 2 of 28, whereas in acetone-pretreated rats the responses observed were additive for 17 of 28, infra-additive for 10 of 28, and supra-additive for 1 of 28. Mixtures containing 1,1,1-trichloroethane or tetrachloroethylene resulted only in no change in toxicity or infra-additivity. Increased toxic responses (additivity and supra-additivity) were observed with certain binary mixtures containing CCl4, CHCl3, 1,1,2-trichloroethane, or 1,1-dichloroethylene.(ABSTRACT TRUNCATED AT 250 WORDS)     

Complete transformation of 1,1,1-trichloroethane to chloroethane by a methanogenic mixed population

A methanogenic mixed population in a packed-bed reactor completely transformed 1,1,1-trichloroethane (10 μM) to chloroethane by a cometabolic process. Chloroethane was not further transformed. Acetate and methanol served as electron donors. Complete transformation of 1,1,1-trichloroethane to chloroethane only occurred when sufficient electron donor was fed into the reactor. Otherwise, besides chloroethane, 1,1-dichloroethane was also found as a product. The products of 1,1,1-trichloroethane transformation also depended on the type of electron donor present. With acetate, the degree of dechlorination was higher, i.e. more 1,1,1-trichloroethane was transformed to chloroethane than with methanol. In an enrichment culture obtained from the reactor contents, 1,1,1-trichloroethane was only transformed to 1,1-dichloroethane and was not further metabolized. Methanol, acetate, formate, ethanol, 2-propanol, trimethylamine and H₂, but not dimethylamine and methylamine, served as electron donors for 1,1,1-trichloroethane transformation by this enrichment culture. Both nitrate and nitrite inhibited 1,1,1-trichloroethane transformation; while nitrate completely inhibited 1,1,1-trichloroethane dechlorination, some conversion did occur in the presence of nitrite. The product(s) of this conversion remain unknown, since no chlorinated hydrocarbons were detected. Received: 19 June 1998 / Received revision: 14 September 1998 / Accepted: 17 September 1998     

Polyethylene glycol-modified hemin having peroxidase activity in organic solvents

Hemin, having two carboxyl groups, was coupled with monomethoxypolyethylene glycol, PEG, through the ester bond formed with carbodiimide. The PEG-modified hemin was readily soluble not only in neutral aqueous solution but also in organic solvents. Its absorption spectrum in 1,1,1-trichloroethane showed a sharp Soret band at 398 nm. The modified hemin catalyzed the peroxidase-reaction in organic solvent and in aqueous solution using hydrogen peroxide or peroxidized linolenic acid as hydrogen acceptor and o-phenylene diamine as hydrogen donor. The activity of PEG-hemin in 1,1,1-trichloroethane was greater than that in an aqueous solution; k1 values in 1,1,1-trichloroethane were 2.3 X 10(3) M-1 sec-1 with hydrogen peroxide and 7.0 X 10(2) M-1 sec-1 with peroxidized linolenic acid, and the value in an aqueous solution was 3.0 X 10 M-1 sec-1 with hydrogen peroxide.     

Urinary excretion of mercapturates as a biological indicator of exposure to electrophilic agents

The urinary excretion of mercapturates was followed photometrically in individuals exposed to styrene, a mixture of aromatic hydrocarbons, butadiene, vinyl chloride, 1,1,1-trichloroethane, trichloroethylene, tetrachloroethylene, 1,1,1-trifluoro-2-bromo-2-chloroethane (Halothane), ethylene oxide, epichlorhydrin, bis(chloromethyl)-ether, N-methylacrylamide, dimethylformamide, nitrosamines or cis-platinum and in groups of controls, smokers and nonsmokers, males and females, the residents of city P, industrial town V.M. and mountain village S. The increase in the urinary excretion of mercapturates was found in individuals exposed to styrene, aromatic hydrocarbons, dimethylformamide, 1,1,1-trichloroethane, and in smokers. In groups of controls, the lowest mercapturate concentrations were detected in the urine samples of nonsmokers from the mountain village S. where the degree of air pollution due to motor vehicle emissions was lowest at the time of investigation.     

Potentiation of the hepatotoxic responses to chemicals in alloxan-diabetic rats.

Alloxan diabetes enhances the hepatotoxic response of male rats to chloroform and 1, 1, 2-trichloroethane, but not to trichloroethylene nor 1, 1, 1-trichloroethane. Insulin treatment partially protects the animals against the alloxan-induced enhancement of chloroform hepatotoxicity. Alloxan diabetes also enhances the hepatotoxic response to galactosamine but not to beryllium nor alpha-naphthylisothiocyanate.     

Propionicicella superfundia gen. nov., sp. nov., a chlorosolvent-tolerant propionate-forming, facultative anaerobic bacterium isolated from contaminated groundwater

A novel strain, designated as BL-10(T), was characterized using a polyphasic approach after isolation from groundwater contaminated by a mixture of chlorosolvents that included 1,1,2-trichloroethane, 1,2-dichloroethane, and vinyl chloride. Stain BL-10(T) is a facultatively anaerobic bacterium able to ferment glucose to form propionate, acetate, formate, lactate, and succinate. Fermentation occurred in the presence of 1,2-dichloroethane and 1,1,2-trichloroethane at concentrations to at least 9.8 and 5.9 mM, respectively. Cells are Gram-positive, rod-shaped, non-motile, and do not form spores. Oxidase and catalase are not produced and nitrate reduction did not occur in PYG medium. Menaquinone MK-9 is the predominant respiratory quinone and meso-diaminopimelic acid is present in the cell wall peptidoglycan layer. Major cellular fatty acids are C(15:0), iso C(16:0), and anteiso C(15:0). Genomic DNA G + C content is 69.9 mol%. Phylogenetic analysis based on 16S rRNA gene sequence comparisons showed strain BL-10(T) to fall within the radiation of genera Propionicimonas and Micropruina. On the basis of the results obtained in this study, it is proposed that strain BL-10(T) should be classified as a novel taxon, for which the name Propionicicella superfundia gen. nov., sp. nov. is proposed. The type strain of Propionicicella superfundia is BL-10(T) (=ATCC BAA-1218(T), =LMG 23096(T)).     

Evaluation of dynamic headspace with gas chromatography/mass spectrometry for the determination of 1,1,1-trichloroethane, trichloroethanol, and trichloroacetic acid in biological samples

A sensitive and reproducible method is described for the analysis of trichloroacetic acid in urine and 1,1,1-trichloroethane in blood using dynamic headspace GC/MS. Samples were analyzed using the soil module of a modified purge and trap autosampler to facilitate the use of disposable purging vessels. Coefficients of variation were below 3.5% for both analytes, and response was linear in the range of 0.01-7.0 microg/ml for trichloroacetic acid and 0.9 ng/ml-2.2 microg/ml for 1,1,1-trichloroethane. Attempts at using dynamic headspace for the analysis of trichloroethanol in urine were unsuccessful.     

Effects of tumor promoters,genotoxic carcinogens and hepatocytotoxins on mouse hepatocyte intercellular communication

Intercellular communication via gap junctions may be an important mechanism of cellular growth control. Tumor promoters can inhibit intercellular communication between cultured cells, while genotoxic carcinogens apparently lack this capability. The inhibition of intercellular communication by tumor promoters may be an essential mechanism by which tumor promotion occurs in vivo. In this study, the liver tumor promoters phenobarbital, lindane (1,2,3,4,5,6-hexachlorocyclohexane, -isomer), DDT (1,1-Bis[4-chlorophenyl],-2,2,2-trichloroethane), Aroclor 1254 (a polychlorinated biphenyl mixture) and dieldrin inhibited intercellular communication between male B6C3F1 mouse hepatocytes in primary culture. Intercellular communication was detected as the passage of [5-³H]uridine nucleotides from pre-labelled donor hepatocytes to non-labelled recipient heptocytes. Mouse hepatocyte intercellular communication was also inhibited by the skin tumor promoter TPA (12-0-tetradecanoyl phorbol-13-acetate), but not by the bladder tumor promoter saccharin. The genotoxic hepatocarcinogens dimethylnitrosamine, diethylnitrosamine, benzo[a]pyrene and 2-acetylaminofluorene, and the hepatocytotoxins bromobenzene, acetaminophen, carbon tetrachloride, chloroform and methotrexate had no effect on mouse hepatocyte intercellular communication at non-cytotoxic levels. These results suggest that the ability to inhibit mouse hepatocyte intercellular communication is an effect specific to tumor promoters.Abbreviations DDT 1,1-Bis[4-chlorophenyl]-2,2,2-trichloroethane - FBS fetal bovine serum - LDH lactate dehydrogenase - TCA trichloroacetic acid - TPA 12-0-tetradecanoyl-phorbol-13-acetate     

Characterization of a newly isolatedcis-1,2-dichloroethylene and aliphatic compound-degrading bacterium,Clostridium sp. strain KYT-1

Acis-1,2-dichloroethylene (cis-DCE)-degrading anaerobic bacterium,Clostridium sp. strain KYT-1, was isolated from a sediment sample collected from a landfill site in Nanji-do, Seoul, Korea. The KYT-1 strain is a gram-positive, endospore-forming, motile, rod-shaped anaerobic bacterium, of approximately 2.5∼3.0 μm in length. The degradation ofcis-DCE is closely related with the growth of the KYT-1 strain, and it was stopped when the growth of the KYT-1 strain became constant. Although the pathway ofcis-DCE degradation by strain KYT-1 remains to be further elucidated, no accumulation of the harmful intermediate, vinyl chloride (VC), was observed during anaerobiccis-DCE degradation. Strain KYT-1 proved able to degrade a variety of volatile organic compounds, including VC, isomers of DCE (1,1-dichloroethylene,trans-1,2-dichloroethylene, andcis-DCE), trichloroethylene, tetrachloroethylene, 1,2-dichloroethane, 1,1,1-trichloroethane, and 1,1,2-trichloroethane. Strain KYT-1 degradedcis-DCE at a range of temperatures from 15 to 37°C, with an optimum at 30°C, and at a pH range of 5.5 to 8.5, with an optimum at 7.0.     

Agarose-chymotrypsin as a catalyst for peptide and amino acid ester synthesis in organic media

Summary Chymotrypsin immobilised within agarose gels by multi-point covalent attachment is a useful catalyst for peptide or amino acid ester synthesis in mainly organic media. Moist gel beads (optionally containing one reactant) may be suspended in organic phases based on ethyl acetate, 1,1,1-trichloroethane or pentan-3-one.     

Metabolism of volatile chlorinated aliphatic hydrocarbons by Pseudomonas fluorescens.

A Pseudomonas fluorescens strain designated PFL12 was isolated from soil and water that were contaminated with various chloroaliphatic hydrocarbons. The isolate was able to metabolize 1,2-dichloroethane, 1,1,2-trichloroethane, 1,2-dichloropropane, 2,2-dichloropropane, and trichloroethylene.     

Metabolism of volatile chlorinated aliphatic hydrocarbons by Pseudomonas fluorescens

A Pseudomonas fluorescens strain designated PFL12 was isolated from soil and water that were contaminated with various chloroaliphatic hydrocarbons. The isolate was able to metabolize 1,2-dichloroethane, 1,1,2-trichloroethane, 1,2-dichloropropane, 2,2-dichloropropane, and trichloroethylene.     

Aerobic degradation of 1,1,1-trichloroethane by Mycobacterium spp. isolated from soil.

Two strains of 1,1,1-trichloroethane (TCA)-degrading bacteria, TA5 and TA27, were isolated from soil and identified as Mycobacterium spp. Strains TA5 and TA27 could degrade 25 and 75 mg. liter of TCA(-1) cometabolically in the presence of ethane as a carbon source, respectively. The compound 2,2,2-trichloroethanol was produced as a metabolite of the degradation process.     

An attempt to determine lipid peroxides with polyethylene glycol-modified hemin

Hemin, having two carboxyl groups, was coupled with alpha-(3-aminopropyl)-omega-methoxypoly(oxyethylene) through the acid-amide bond formed with carbodiimide. The modified hemin catalyzed the peroxidase reaction in 1,1,1-trichloroethane using benzoyl peroxide or peroxides in unsaturated fatty acids as the hydrogen acceptor and leuco crystal violet as the hydrogen donor. A basic study on quantitative microanalysis of the lipid peroxides was attempted.     

Ligand structure-dependent activation of estrogen receptor alpha/Sp by estrogens and xenoestrogens

This study investigated the effects of E2, diethylstilbestrol (DES), antiestrogens, the phytoestrogen resveratrol, and the xenoestrogens octylphenol (OP), nonylphenol (NP), endosulfan, kepone, 2,3,4,5-tetrachlorobiphenyl-4-ol (HO-PCB-Cl(4)), bisphenol-A (BPA), and 2,2-bis-(p-hydroxyphenyl)-1,1,1-trichloroethane (HPTE) on induction of luciferase activity in breast cancer cells transfected with a construct (pSp1(3)) containing three tandem GC-rich Sp binding sites linked to luciferase and wild-type or variant ERalpha. The results showed that induction of luciferase activity was highly structure-dependent in both MCF-7 and MDA-MB-231 cells. Moreover, RNA interference assays using small inhibitory RNAs for Sp1, Sp3 and Sp4 also demonstrated structure-dependent differences in activation of ERalpha/Sp1, ERalpha/Sp3 and ERalpha/Sp4. These results demonstrate for the first time that various structural classes of ER ligands differentially activate wild-type and variant ERalpha/Sp-dependent transactivation, selectively use different Sp proteins, and exhibit selective ER modulator (SERM)-like activity.     

Comparative study of the toxic actions of 2,2-bis(p-chlorophenyl)-1,1,1-trichloroethane and 2,2-bis(p-chlorophenyl)-1,1-dichloroethylene on the growth and respiratory activity of a microorganism used as a model.

A strain of Bacillus stearothermophilus was used as a model for a comparative study of the toxic effect of 2,2-bis(p-chlorophenyl)-1,1,1-trichloroethane and 2,2-bis(p-chlorophenyl)-1,1-dichloroethylene. Bacterial growth, the O2 consumption rate, and respiration-related enzymatic activities provided quantitative data in agreement with results reported for other systems. The use of this bacterium for screening for chemical toxicity is discussed.     

Exposure of Japanese quail embryos to o,p'-DDT has long-term effects on reproductive behaviors, hematology, and feather morphology

Japanese quail eggs were injected with 1-(2-chlorophenyl)-1-(4-chlorophenyl)-2,2,2-trichloroethane o,p'-DDT(1-10 mg),1,1-bis(4-chlorophenyl)-2,2,2-trichloroethane p,p'-DDT (1-10 mg), or, in one study, 0.5 mg chlordecone dissolved in 50 microliters of corn oil on day 1 of incubation. Hatchability was not decreased by o,p'-DDT or p,p'-DDT, as compared to corn-oil-injected controls, but was reduced in progeny of parents injected in ovo with either isomer. Tremor was observed for up to 4 days posthatching only in birds injected with 1.75-10 mg p,p'-DDT or chlordecone. Survivability to 5 weeks posthatch was reduced (less than or equal to 50%) in birds injected in ovo with 6.25-7.5 mg, o,p'-DDT or 1.75-5 mg p,p'-DDT as compared to corn oil (96%). Reproductive behaviors were attenuated in birds injected during development with o,p'-DDT, both DDT isomers decreased the total number of ovipositions, and o,p'-DDT increased the total number of eggshell malformations. Neither body weights nor reproductive organ weights at 12 weeks were affected by injection of either isomer. Exposure to DDT did not affect acquisition of a matched-to-sample food-reinforced response or subsequent responding on a random interval schedule of reinforcement. In another experiment, total circulating erythrocyte numbers were reduced in females after injection in ovo with o,p'-DDT but not after injection with p,p'-DDT. A primary humoral immune response was not affected by in ovo exposure to either isomer of DDT. In ovo exposure to o,p'-DDT but not to p,p'-DDT had long-term and estrogen-like effects on behavior and hematology in Japanese quail. Posthatch primary feather morphology was also altered by embryonic exposure to o,p'-DDT, p,p'-DDT, and chlordecone.