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PubMed2004

Nonbiological removal of cis-dichloroethylene and 1,1-dichloroethylene in aquifer sediment containing magnetite.

The U.S. EPA Technical Protocol for Evaluating Natural Attenuation of Chlorinated Solvents in Groundwater emphasizes biological reductive dechlorination as the primary mechanism for destruction of chlorinated solvents. However, biological reductive dechlorination could not explain the removal of cis-dichloroethylene (cis-DCE) and 1,1-DCE from a plume of contaminated groundwater in Minnesota. Several recent laboratory studies have demonstrated that common iron minerals such as magnetite can also transform chlorinated alkenes. Laboratory microcosms were constructed with sediment from three depth intervals in the aquifer near the source of the plume. The microcosms were autoclaved to prevent biological transformations. In these autoclaved sediments, the rates of removal of cis-DCE in samples from the shallow, intermediate, and deeper depth intervals in the aquifer were 0.58 +/- 0.09, 2.29 +/- 0.26, and 0.31 +/- 0.08 per year at 95% confidence. The rate of removal of 1,1-DCE in sediment from the shallow interval was 1.37 +/- 0.50 per year. The rates of removal in the microcosms are similar to the rates of attenuation observed in the field. Magnetite was identified in the sediment by X-ray diffraction and optical microscopy. Published rates of transformation of cis-DCE by magnetite are consistent with the rates of removal in the microcosm study.

Dichloroethylenes↗
PubMed2005

Cometabolic transformation of cis-1,2-dichloroethylene and cis-1,2-dichloroethylene epoxide by a butane-grown mixed culture.

Aerobic cometabolism of cis-1,2-dichloroethylene (c-DCE) by a butane-grown mixed culture was evaluated in batch kinetic tests. The transformation of c-DCE resulted in the coincident generation of c-DCE epoxide. Chloride release studies showed approximately 75% oxidative dechlorination of c-DCE. Mass spectrometry confirmed the presence of a compound with mass-to-charge-fragment ratios of 112, 83, 48, and 35. These values are in agreement with the spectra of chemically synthesized c-DCE epoxide. The transformation of c-DCE required O2, was inhibited by butane and was inactivated by acetylene (a known monooxygenase inactivator), indicating that a butane monooxygenase enzyme was likely involved in the transformation of c-DCE. This study showed c-DCE epoxide was biologically transformed, likely by a butane monooxygenase enzyme. c-DCE epoxide transformation was inhibited by both acetylene and c-DCE indicating a monooxygenase enzyme was involved. The epoxide transformation was also stopped when mercuric chloride (HgCl2) was added as a biological inhibitor, further support a biological transformation. To our knowledge this is the first report of the biological transform c-DCE epoxide by a butane-grown culture.

Acetylene↗
PubMed2002

NTP Technical Report on the toxicity studies of trans-1,2-dichloroethylene (CAS no. 156-60-5) administered in microcapsules in feed to F344/N rats and B6C3F(1) mice.

1,2-Dichloroethylene exists in two isomeric states: trans-1,2-dichloroethylene and cis-1,2-dichloroethylene. The trans isomer is used more widely in industry than the cis isomer. trans-1,2-Dichloroethylene is used as a solvent for waxes, resins, and acetylcellulose. It is also used in the extraction of rubber, as a refrigerant, and in the manufacture of pharmaceuticals and artificial pearls. F344/N rats and B6C3F1 mice were administered trans-1,2-dichloroethylene in microcapsules in feed for 14 weeks. Animals were evaluated for clinical pathology, reproductive system effects, and histopathology. Genetic toxicity studies were conducted in vitro in Salmonella typhimurium and Chinese hamster ovary (CHO) cells, and in vivo in mouse bone marrow cells and peripheral blood erythrocytes. In the 14-week feed studies, groups of 10 male and 10 female rats and mice were fed diets containing microcapsules with a chemical load of 45% trans-1,2-dichloroethylene. Dietary concentrations of 3,125, 6,250, 12,500, 25,000, and 50,000 ppm microencapsulated trans-1,2-dichloroethylene resulted in average daily doses of 190, 380, 770, 1,540, and 3,210 mg/kg for male rats; 190, 395, 780, 1,580, and 3,245 mg/kg for female rats; 480, 920, 1,900, 3,850, and 8,065 mg/kg for male mice; and 450, 915, 1,830, 3,760, and 7,925 mg/kg for female mice. Additional groups of 10 male and 10 female rats and mice served as untreated and vehicle controls. There were no exposure-related deaths of rats or mice. Mean body weights of male rats and male and female mice in the 50,000 ppm groups were significantly less than those of the vehicle controls. The mean body weight gains of female mice in the 12,500 and 25,000 ppm groups were also significantly less than that of the vehicle controls. On day 21 and at week 14, there were mild decreases in hematocrit values, hemoglobin concentrations, and erythrocyte counts in groups of male and female rats in the 25,000 and 50,000 ppm groups. At week 14, these effects were seen in male rats exposed to 6,250 and 12,500 ppm. There were no exposure-related alterations in clinical chemistry parameters in rats or mice. The liver weights of female rats exposed to 6,250 ppm or greater were significantly greater than those of the vehicle controls. The absolute kidney weights of male rats exposed to 25,000 or 50,000 ppm were significantly decreased. No gross or microscopic lesions were observed in rats or mice that could be attributed to trans-1,2-dichloroethylene exposure. Neither cis-, trans-, nor cis,trans-1,2-dichloroethylene was mutagenic in S. typhimurium strain TA97 (cis isomer only), TA98, TA100, TA1535, or TA1537, with or without S9 metabolic activation enzymes. In CHO cells in vitro, cis- 1,2-dichloroethylene induced sister chromatid exchanges (SCEs) in the absence of S9; with S9, the single trial that was performed yielded equivocal results. The cis,trans isomer induced significant increases in SCEs in cultured CHO cells with and without S9. In contrast to these positive results, trans-1,2-dichloroethylene gave negative results in the SCE test, with and without S9. Neither cis-, trans-, nor cis,trans-1,2-dichloroethylene induced chromosomal aberrations (Abs) in cultured CHO cells, with or without S9. In vivo, no induction of SCEs or Abs was noted in bone marrow cells of male mice administered cis- or trans-1,2-dichloroethylene by intraperitoneal injection once, with sampling performed 23 hours (for SCE analyses) or 17 hours (for Abs analyses) after injection. In addition, negative results were obtained in a peripheral blood micronucleus test in male and female mice administered trans- 1,2-dichloroethylene in microcapsules in feed for 14 weeks. Very little toxicity was associated with ingestion of microencapsulated trans-1-2-dichloroethylene. Histopathology and clinical chemistry data, combined with body and organ weight data, revealed that the maximum tolerated dose was not reached in these studies.

Animals↗
PubMed1982

The 1,2-dichloroethylenes: their metabolism by hepatic cytochrome p-450 in vitro.

Cis- and trans-1,1-dichloroethylene bound to the active site of hepatic microsomal cytochrome P-450 with the production of a Type I difference spectrum and stimulated CO-inhibitable hepatic microsomal NADPH oxidation. Incubation of cis- and trans-1,2-dichloroethylene plus hepatic microsomes, NADPH-generating system-EDTA resulted in the production of measurable levels of 2,2-dichloroethanol and dichloroacetaldehyde but not of 2-chloroethanol, chloroacetaldehyde or chloroacetic acid and, also, resulted in decreased levels of hepatic microsomal cytochrome P-450 and heme. In addition, dichloroacetic acid was produced from trans-dichloroethylene under these experimental conditions. The omission of any component of the incubation mixture eliminated the above effects, while the inclusion of SKF-525A, metyrapone or CO:O2 (80, v/v) diminished these effects. The effects of beta-naphthoflavone and phenobarbital pretreatment on the values of Ks, delta Amax, Km and Vmax for the binding and metabolism of the 1,2-dichloroethylenes are reported. The binding and metabolism of the 1,2-dichloroethylenes and the 1,2-dichloroethylene-mediated inactivation of cytochrome P-450 were enhanced per mg of microsomal protein, but generally not per nmole of cytochrome P-450 by prior induction with beta-naphthoflavone or phenobarbital. It is concluded that multiple forms of hepatic microsomal cytochrome P-450 bind and metabolize the 1,2-dichloroethylenes. The role of cytochrome P-450 in the metabolic activation of the dichloroethylenes is considered.

Animals↗
PubMed1990

Cardiac teratogenesis of trichloroethylene and dichloroethylene in a mammalian model.

Recent epidemiologic studies have demonstrated a greater than expected number of pediatric patients with congenital heart disease in areas where drinking water was contaminated by halogenated aliphatic hydrocarbons. Trichloroethylene, trichloroethane and dichlorethylene were the principal contaminants in the groundwater. A previous study of chick embryos demonstrated that when injected into the air sacs of fertilized eggs trichloroethylene produced more than three times the number of cardiac defects that are found in control embryos. This mammalian study demonstrates similar effects of trichloroethylene and dichloroethylene when applied under provocative circumstances (that is, solutions delivered through a catheter into the gravid uterus from an intraperitoneal osmotic pump) to the developing rat fetus in utero during the period of organ differentiation and development. Furthermore, the effect is dose dependent for both agents. Although only a very small number of congenital heart anomalies (3%) were found in the control group, 9% and 12.5% were found in the lower dose trichloroethylene and dichloroethylene groups and 14% and 21% in the higher dose groups, respectively (p less than 0.05). A variety of cardiac defects were found. Dichloroethylene appears to be at least as great a cardiac teratogen as trichloroethylene even though it was administered at a 10-fold lower concentration. These agents appear to be specific cardiac teratogens because only a single noncardiac anomaly was found. This study in a rat model demonstrates a dose-dependent relation between fetal exposure to trichloroethylene and dichloroethylene in utero during the period of organogenesis and the appearance of a variety of congenital cardiac defects.

Abnormalities, Drug-Induced↗
PubMed1998

Serum-borne factor(s) of 1,1-dichloroethylene and 1,2-dichlorobenzene-treated mice inhibited in vitro antibody forming cell response and natural killer cell activity.

1,1-Dichloroethylene and 1,2-dichlorobenzene administered to mice produced liver and/or kidney damage which was quantified in this study by a histochemical method. The in vitro effect of sera obtained from these mice on antibody forming cell (AFC) response and natural killer (NK) cell activity was investigated in parallel with the assessment of sera tumor necrosis factor-alpha (TNF-alpha) and interleukin-6 (IL-6) levels. 1,1-Dichloroethylene (100, 150 and 200 mg/kg) provoked liver and kidney damage. Peak kidney damage occurred 16 h after the dose was administered and at 24 h in the case of the liver. During the peak level of liver damage, a serum-borne immunosuppressive effect was also at its highest level. With respect to sera cytokine levels, an increase of TNF-alpha and IL-6 was detected earlier, i.e. 6 h after toxic administration, followed by a decrease that tended toward a baseline level. There was a relationship between the tissue damage induced by 1,1-dichloroethylene and the immunosuppressive effect of mice sera on AFC response and NK cell activity. 1,2-Dichlorobenzene (300, 500 and 600 mg/kg) provoked only liver damage. Peak liver damage severity was observed 48 h after toxic administration, whereas the highest serum-borne immunosuppressive effect was observed almost immediately, i.e. 6 h after administration. As regards sera cytokine levels, only TNF-alpha could be detected 6 h after administering 500 and 600 mg/kg doses of 1,2 dichlorobenzene. There was a relationship between the liver damage induced by 1,2-dichlorobenzene and the immunosuppressive effect of mice sera on the AFC response. In view of the above results, this study suggests that the immunosuppressive effect in sera of mice treated with 1,1-dichloroethylene and 1,2-dichlorobenzene may result from tissue damage, and that the increased levels of TNF-alpha and IL-6 in sera may contribute to this effect. Further studies are needed to clarify the factor(s) responsible, including transforming growth factor-beta1 (TGF-beta1) causing immunosuppression.

Animals↗
PubMed2001

The convulsant and anesthetic properties of cis-trans isomers of 1,2-dichlorohexafluorocyclobutane and 1,2-dichloroethylene.

UNLABELLED: The differences in potencies of optical isomers of anesthetics support the hypothesis that anesthetics act by specific receptor interactions. Diastereoisomerism and geometrical isomerism offer further tests of this hypothesis but have not been explored. They are the subject of this report. We quantified the nonimmobilizing and convulsant properties of the cis and trans diastereomers of the nonimmobilizer 2N (1,2-dichlorohexafluorocyclobutane). Although the lipophilicity of the diastereomers predicts complete anesthesia at the partial pressures applied, neither diastereomer had anesthetic activity alone, and the cis form may have a small (10%) capacity to antagonize anesthesia, as defined by additive effects on the MAC (the minimum alveolar concentration required to suppress movement to a noxious stimulus in 50% of rats) of desflurane. Both diastereomers produced convulsions, the cis form being nearly twice as potent as the trans form: convulsant 50% effective dose (mean +/- SD) was 0.039 +/- 0.009 atmospheres (atm) for the purified cis and 0.064 +/- 0.009 atm for the purified trans isomer. The MAC value for cis-1,2-dichloroethylene equaled 0.0071 +/- 0.0006 atm, and MAC for trans-1,2-dichloroethylene equaled 0.0183 +/- 0.0031 atm. In qualitative accord with the Meyer-Overton hypothesis, the greater cis potency was associated with a greater lipophilicity. However, the product of MAC x solubility differed between the cis and trans isomers by 40%-50%. We conclude that neither the cis nor trans isomers of 2N have anesthetic properties, but isomerism does influence 2N's convulsant properties and the anesthetic properties of dichloroethylene. These isomeric effects may be as useful in defining receptor-anesthetic interactions as those found with optical isomers. IMPLICATIONS: Cis-trans isomerism can influence the convulsant properties of the nonimmobilizer 2N (1,2-dichlorohexafluorocyclobutane) and the anesthetic properties of dichloroethylene. Such isomeric effects may be as useful as those found with optical isomers in defining receptor-anesthetic interactions.

Anesthetics, Inhalation↗
PubMed2001

Aerobic degradation of mixtures of tetrachloroethylene, trichloroethylene, dichloroethylenes, and vinyl chloride by toluene-o-xylene monooxygenase of Pseudomonas stutzeri OX1.

A recombinant strain of Escherichia coli (JM109/pBZ1260) expressing constitutively toluene-o-xylene monooxygenase (ToMO) of Pseudomonas stutzeri OX1 degraded binary mixtures (100 microM each) of tetrachloroethylene (PCE) with either trichloroethylene (TCE), 1,1-dichloroethylene (1,1-DCE), cis-dichloroethylene (cis-DCE), trans-1,2-dichloroethylene (trans-DCE), or vinyl chloride (VC). PCE degradation was 8-20% for these binary mixtures, while TCE and trans-DCE with PCE were degraded at 19%, 1,1-DCE at 37%, cis-DCE at 97%, and VC at 27%. The host P. stutzeri OXI was also found to degrade binary mixtures of PCE/TCE, PCE/cis-DCE, and PCE/VC when induced with toluene. Degradation of quaternary mixtures of PCE/TCE/trans-DCE/VC and PCE/TCE/cis-DCE/VC by JM109/pBZ1260 were also investigated as well as mixtures of PCE/TCE/trans-DCE/1,1-DCE/cis-DCE/VC; when all the chlorinated compounds were present, the best degradation occurred with 24-51% removal of each. For these degradation reactions, 39-85% of the stoichiometric chloride expected from complete degradation of the chlorinated ethenes was detected. The time course of PCE/TCE/1,1-DCE degradation was also measured for a mixture of 8, 17, and 6 microM, respectively; initial degradation rates were 0.015, 0.023. and 0.029 nmol/min x mg protein, respectively. This indicates that for the first time an aerobic enzyme can degrade mixtures of all chlorinated ethenes, including the once--so it was believed-completely recalcitrant PCE.

Dichloroethylenes↗
PubMed1995

Reaction of glutathione with the electrophilic metabolites of 1,1-dichloroethylene.

1,1-Dichloroethylene (DCE) requires cytochrome P450-catalyzed bioactivation to electrophilic metabolites (1,1-dichloroethylene oxide, 2-chloroacetyl chloride and 2,2-dichloroacetaldehyde) to exert its cytotoxic effects. In this investigation, we examined the reactions of these metabolites with glutathione by spectroscopic and chromatographic techniques. In view of the extreme reactivity of 2-chloroacetyl chloride, primary reactions are likely to include alkylation of cytochrome P450, conjugation with GSH to give S-(2-chloroacetyl)-glutathione, or hydrolysis to give 2-chloroacetic acid. Our results showed conjugation of GSH with 1,1-dichloroethylene oxide, through formation of the mono- and di-glutathione adducts, 2-S-glutathionyl acetate and 2-(S-glutathionyl) acetyl glutathione, respectively. The observed equilibrium constant between the hydrate of 2,2-dichloroacetaldehyde and S-(2,2-dichloro-1-hydroxy)ethylglutathione was estimated from 1H-NMR experiments to be 14 +/- 2 M-1. Thus, 2,2-dichloroacetaldehyde is unlikely to make a significant contribution to GSH depletion as GSH concentrations above normal physiological levels would be necessary to form significant amounts of S-(2,2-dichloro-1-hydroxy)ethylglutathione. We also compared the formation of the glutathione conjugates in rat and mouse liver microsomes using 14C-DCE. The results demonstrated a species difference; the total metabolite production was 6-fold higher in microsomes from mice, compared with samples from rat. Production of DCE metabolites in hepatic microsomes from acetone-pretreated mice was 3-fold higher than those from untreated mice suggesting a role for P450 2E1 in DCE bioactivation. These results indicate that the epoxide is the major metabolite of DCE that is responsible for GSH depletion, suggesting that it may be involved in the hepatotoxicity evoked by DCE. Furthermore, this metabolite is formed to a greater extent in mouse than in rat liver microsomes and this difference may underlie the enhanced susceptibility found in the former species.

Acetaldehyde↗
PubMed1978

Inhibition of mixed function oxidases in rat liver by trans- and cis-1,2-dichloroethylene.

A single 8-h exposure to trans-1,2-dichloroethylene (t-DCE) or cis-1,2-dichloroethylene (c-DCE) at 200 ppm (hygienic standard in workplaces) resulted in a significant increase in the hexobarbital sleeping time, the zoxazolamine paralysis time, and the metabolic formation of 4-aminoantipyrine from aminopyrine in adult female Wistar rats. Higher DCE concentrations caused a dose-dependent and substantial enhancement of these effects, the effects of c-DCE being stronger than that of t-DCE. In the course of enzyme-kinetic measurements in isolated rat liver microsomes, t-DCE proved to be a competitive inhibitor of the oxidative N-demethylation of aminopyrine and of the O-demethylation of p-nitroanisole. It is concluded from the results that the inhibition of hepatic drug metabolism is caused by a competitive and reversible interaction of the 2 DCE isomers with the mixed-function oxidase system, the interaction possibly operating at the type I binding site.

Animals↗
PubMed1991

1,1-Dichloroethylene hepatotoxicity: hypothyroidism decreases metabolism and covalent binding but not injury in the rat.

Our objective was to determine if the previously reported protective effect of hypothyroidism against 1,1-dichloroethylene hepatotoxicity was associated with a change in distribution and covalent binding. Sprague-Dawley male rats were made hypothyroid (HypoT) by surgical thyroidectomy 2 weeks prior to studies and compared to euthyroid (EuT) rats. Hypothyroidism decreased body weights and liver to body weight ratios while mitochondrial non-protein sulfhydryl groups and cytosolic alcohol dehydrogenase activities were increased by 50%. Rats received a single oral dose of 100 mg [14C]1,1-dichloroethylene (DCE)/kg in mineral oil and were killed at 2, 4, 12 or 24 h; controls received mineral oil only. More rapid liver injury, as measured by serum alanine aminotransferase activity and histology, was present at 2 and 4 h after DCE in HypoT than EuT rats, but a similar magnitude of injury was evident at 12 and 24 h. DCE decreased liver non-protein sulfhydryl groups to a comparable extent in HypoT and EuT rats. Cytosolic glutathione S-transferase and alcohol dehydrogenase activities were decreased only in HypoT rats after DCE. HypoT rats excreted approximately 30% less total [14C]DCE-derived label in urine and their livers, kidneys and lungs consistently contained slightly less covalently bound [14C]DCE-derived label. In contrast, between 1 and 4 h after DCE, greater amounts of acid-soluble and acid-precipitable [14C]DCE-derived label were recovered in red blood cells of HypoT rats. Our results indicate that hypothyroidism did not protect against oral DCE hepatotoxicity but was associated with a more rapid injury at early times. Concurrently, hypothyroidism was found to change the fate of [14C]DCE with higher amounts of 14C-label recovered at early times in red blood cells while less 14C-label was excreted in urine and bound to liver.

Administration, Oral↗
PubMed2000

Tandem MS analysis of model peptide adducts from reactive metabolites of the hepatotoxin 1,1-dichloroethylene.

Dichloroethylene (DCE) is a hepatotoxin that undergoes cytochrome P450-catalyzed bioactivation in hepatocytes to form 2-chloroacetyl chloride and 1,1-dichloroethylene oxide. 2-Chloroacetyl chloride reacts with nucleophilic residues and with N-terminal amines to produce 2-chloroacetylated residues and with glutathione to form the reactive electrophile S-(2-chloroacetyl)glutathione (ClCH(2)COSG), which, in turn, is capable of sulfhydryl alkylation. 1,1-DCE oxide can bind to cysteine sulfhydryl groups and subsequently hydrolyze to form an S-carboxymethylated cysteine residue. S-Carboxymethylated, 2-chloroacetylated, and GSCOCH(2)-S-Cys-peptide adducts of model cysteine-containing peptides were synthesized, and their fragmentation patterns were characterized by electrospray tandem mass spectrometry. Synthesis of GSCOCH(2)-S-Cys-peptide adducts was achieved via a novel tert-butoxycarbonyl (tBOC) derivative of ClCH(2)COSG. CID of GSCOCH(2)-S-Cys-peptide adducts resulted in product ions and neutral losses indicative of the GSCOCH(2)-S-Cys moiety as well fragment ion pairs in the b- and y-ion series corresponding to the modified cysteine residue. S-Carboxymethylated peptides exhibited only a characteristic b- or y-series ion pair separated by 161 Da, corresponding to cysteine + CH(2)COOH. CID of 2-chloroacetylated peptides showed neutral losses of 36 (HCl), 78 (HCOCH(2)Cl), 96 (HCOCH(2)Cl + H(2)O), and 114 Da (HCOCH(2)Cl + 2H(2)O). Combinations of characteristic fragment ions, neutral losses, and ion pairs thus are characteristic for DCE-derived adducts. These features can be used in an MS/MS data reduction algorithm for the selective identification of protein targets of DCE metabolites.

Dichloroethylenes↗
PubMed2006

Reactions of OH and NO radicals with 1,1-dichloroethylene in argon matrices. FTIR and theoretical studies.

HONO/1,1-dichloroethylene/Ar matrices were subjected to UV radiation (lambda > 340 nm) from a medium pressure mercury lamp. The products of the photolysis were studied experimentally by means of FTIR spectroscopy and theoretically using the ab initio MP2 method. Two conformers of 2-nitroso-2,2-dichloroethanol molecule have been identified as the final products of the double addition reaction of the OH, NO radicals to 1,1-dichloroethylene. The additional reactive species observed in the matrix is tentatively identified as an 1,1-dichloro-2-hydroxyethyl radical, an intermediate formed by single addition of OH to 1,1-dichloroethylene. The three photoproducts have been identified and observed for the first time. The identities of the products have been justified by comparison with the experiments with deuterated DONO and by performing concentration and annealing studies as well as by reference to the spectral data of related molecules. The results of the quantum mechanical calculations confirmed both the assignment of the new molecules and mechanism of the reaction observed in our experiment.

Argon↗
PubMed2002

4-week inhalation toxicity study with a mixture of dichloroethylene and perfluorobutylethylene in rats.

Inhalation studies were conducted to determine the potential subchronic toxicity of a mixture of trans-1,2-dichloroethylene (70%), cis-1,2-dichloroethylene (5%), and perfluorobutylethylene (25%). Groups of rats were exposed to 0, 400, 2000, or 8000 ppm concentrations of the mixture vapor 6 h/day, 5 days/wk, for a total of 20 exposures. Subgroups of rats were further observed during a 1-mo recovery period. Functional observational battery (FOB) and motor activity (MA) behavioral tests were conducted prior to initiation of the exposures, during exposure wk 4, and after a 1-mo postexposure recovery period. Clinical pathology evaluations were conducted at the end of the exposure period and after a 1-mo recovery period. At the end of the 4-wk exposure period, tissues from rats were collected, histologically processed, and evaluated by light microscopy. Test substance-related, biologically significant decreased body weights and body weight gains occurred in male and female rats exposed to 8000 ppm. In addition, test substance-related, statistically significant decreases in food consumption and/or food efficiency were observed in male rats exposed to 8000 ppm. During exposures to 8000 ppm, some rats exhibited tremors and ataxia. Usually tremors and ataxia were observed within 1 h after initiation of the daily exposure period and were observed during each exposure day. Tremors were also observed during 1 exposure day in the 2000 ppm animals. In addition to the tremors and ataxia, rats exposed to 2000 ppm or 8000 ppm had a diminished and/or no alerting response to a sharp, sound stimulus during each of the daily exposure periods. These effects were transient since no clinical observations of compromised neurological function were detected when the rats were evaluated upon return to the animal room following exposure. Daily reoccurrence of this apparently acute effect in the 8000 ppm group did not produce enduring neurological changes since there were no test substance-related effects on FOB parameters or on MA conducted the day following the last exposure or during the recovery period. In addition, there were no toxicologically significant changes in hematology, clinical chemistry, or urinalysis parameters in either males or females for any exposure concentration; and there were no test substance-related gross or microscopic morphological changes in males or females administered any exposure concentration. Under the conditions of the study, the no-observed-effect level (NOEL) was 400 ppm in males and females based on clinical signs of toxicity during exposure to 2000 or 8000 ppm.

Animals↗
PubMed1985

Biotransformation of tetrachloroethylene to trichloroethylene, dichloroethylene, vinyl chloride, and carbon dioxide under methanogenic conditions.

Tetrachloroethylene (PCE) and trichloroethylene (TCE), common industrial solvents, are among the most frequent contaminants found in groundwater supplies. Due to the potential toxicity and carcinogenicity of chlorinated ethylenes, knowledge about their transformation potential is important in evaluating their environmental fate. The results of this study confirm that PCE can be transformed by reductive dehalogenation to TCE, dichloroethylene, and vinyl chloride (VC) under anaerobic conditions. In addition, [14C]PCE was at least partially mineralized to CO2. Mineralization of 24% of the PCE occurred in a continuous-flow fixed-film methanogenic column with a liquid detention time of 4 days. TCE was the major intermediate formed, but traces of dichloroethylene isomers and VC were also found. In other column studies under a different set of methanogenic conditions, nearly quantitative conversion of PCE to VC was found. These studies clearly demonstrate that TCE and VC are major intermediates in PCE biotransformation under anaerobic conditions and suggest that potential exists for the complete mineralization of PCE to CO2 in soil and aquifer systems and in biological treatment processes.

Biotransformation↗
PubMed1984

1,1-Dichloroethylene: an apoptotic hepatotoxin?

Within 2 hr after 1,1-dichloroethylene administration, the following phenomena occur in livers of fasted rats: dilation and disruption of bile canaliculi, plasma membrane invagination and loss of microvilli, cytoplasmic vacuolation, and loss of density in mitochondrial matrices. Early, selective loss of enzyme activities was localized by histochemical staining to bile canalicular, and inner and outer mitochondrial membranes. Biliary permeability to inulin increased, a change suggestive of the breakdown of junctions between hepatocytes. Endoplasmic reticulum and lysosomes appeared spared. In addition, scattered, individual hepatocytes exhibited changes characteristic of apoptosis by 2 hr: chromatin aggregation and margination, nucleolar coarse granulation and enlargement, rounded blebs and proturberances on cell surfaces, and the separation of these cells from surrounding parenchyma. In contrast, evidence of plasma membrane leakiness to K+, Ca2+ and soluble cytoplasmic enzymes was not detected until after 2 hr. Based on these observations, we propose that 1,1-dichloroethylene may initiate apoptosis-like cell degradation in selected parenchymal cells prior to or coincident with centrolobular necrosis.

Animals↗