Influence of exposure route and oral dosage regimen on 1, 1-dichloroethylene toxicokinetics and target organ toxicity.

The objective of this investigation was to elucidate the effects of route of exposure and oral dosage regimen on the toxicokinetics (TK) of 1,1-dichloroethylene (DCE). Fasted male Sprague-Dawley rats that inhaled 100 or 300 ppm for 2 h absorbed total systemic doses of (10 or 30 mg/kg DCE, respectively. Other groups of rats received 10 or 30 mg/kg DCE by intravenous injection, bolus gavage (by mouth), or gastric infusion (g.i.) over a 2-h period. Serial microblood samples were taken from the cannulated, unanesthetized animals and analyzed for DCE content by gas chromatography to obtain concentration versus time profiles. Inhalation resulted in substantially higher peak blood concentrations and area under blood-concentration time curves (AUC(0)(2)) than did gastric infusion of the same dose over the same time frame at each dosage level, although inhalation (AUC(0)(infinity)) values were only modestly higher. Urinary N-acetyl-beta-D-glucosaminidase (NAG) and gamma-glutamyltranspeptidase (GGT) activities were monitored as indices of kidney injury in the high-dose groups. NAG and GGT excretion were much more pronounced after inhalation than gastric infusion. Administration of DCE by gavage also produced much higher Cmax and AUC(0)(2) values than did 2-h g.i., although AUC(0)(infinity) values were not very different. The 30 mg/kg bolus dose produced marked elevation in serum sorbitol dehydrogenase, an index of hepatocellular injury. Administration of this dose by inhalation and gastric infusion was only marginally hepatotoxic. These findings demonstrate the TK and target organ toxicity of DCE vary substantially between different exposure routes, as well as dosage regimens, making direct extrapolations untenable in health risk assessments.

Inhaled chemicals may enhance allergic airway inflammation in ovalbumin-sensitised mice.

Occupational allergy and asthma is a challenging issue in the developing countries. Chemicals inhaled in the workplaces may act not only as allergens but also as immune response modifiers, contributing to asthma exacerbation. In this study, we tested the adjuvant effect of 20 ppm chloroform, 10 ppm 1,1-dichloroethylene, and 100 ppm styrene in mice. Female BALB/c mice were sensitised to ovalbumin (OVA) without using alum. During the OVA-sensitisation period, these mice were exposed by inhalation to the chemicals studied for 6h/day for four consecutive days. After two OVA-intratracheal challenges, a mild Th2 immune response was observed in the OVA-exposed groups. This response was characterised by a mild increase in serum specific IgE level, in local Th2 cytokine production, and in lung inflammatory reaction. Exposure to styrene or chloroform alone slightly increased Th2 cytokine production by lung-draining lymph node cells cultured with concanavaline A, except for the IL-4 level in the chloroform exposure group, which decreased. On the other hand, exposure to 1,1-dichloroethylene alone markedly increased the Th2 cytokine levels compared to those observed in the groups exposed to OVA alone. In the combined OVA+chemical-treated groups, styrene potentiated IL-4, -5 and -13 production efficiently (approximately two, four and three times higher, respectively), resulting in an increase in the total IgE levels and inflammatory reaction. On the other hand, the enhanced IgE levels and the exacerbation of the inflammatory response by 1,1-dichloroethylene or chloroform were associated with only minor changes in local cytokine levels. These findings suggest that exposure to chemicals through inhalation may aggravate the allergic lung inflammation. And this, depending on the chemical exposure conditions, may result from the synergistic effect of chemicals and allergen on local Th2 cytokine production.

Dose-dependent transitions in mechanisms of toxicity: case studies.

Experience with dose response and mechanisms of toxicity has shown that multiple mechanisms may exist for a single agent along the continuum of the full dose-response curve. It is highly likely that critical, limiting steps in any given mechanistic pathway may become overwhelmed with increasing exposures, signaling the emergence of new modalities of toxic tissue injury at these higher doses. Therefore, dose-dependent transitions in principal mechanisms of toxicity may occur, and could have significant impact on the interpretation of reference data sets for risk assessment. To illustrate the existence of dose-dependent transitions in mechanisms of toxicity, a group of academic, government, and industry scientists, formed under the leadership of the ILSI Health and Environmental Sciences Institute (HESI), developed a series of case studies. These case studies included acetaminophen, butadiene, ethylene glycol, formaldehyde, manganese, methylene chloride, peroxisome proliferator-activated receptor (PPAR), progesterone/hydroxyflutamide, propylene oxide, vinyl acetate, vinyl chloride, vinylidene chloride, and zinc. The case studies formed the basis for technical discourse at two scientific workshops in 2003.

Effect of inhaled industrial chemicals on systemic and local immune response.

Using immunotoxic functional tests, namely IgM response to sheep red blood cells (SRBCs) and interferon-gamma (IFN-gamma) production, this study simultaneously evaluated the effects of inhaled chloroform (10, 20, and 50 ppm), carbon tetrachloride (100, 200, and 300 ppm), 1,1-dichloroethylene (5, 10, and 15 ppm), and styrene (100, 200, and 300 ppm) on the systemic (spleen) and local (lung-associated lymph nodes) immune response. At least one concentration of all the chemicals studied provoked a statistically significant increase in IgM response in the lymph nodes compared with the controls, as expressed by the number of plaque-forming cells (PFCs), whereas only the highest concentration of 1,1-dichloroethylene provoked an increase in the number of PFCs statistically different from the controls in the case of the spleens. The release of IFN-gamma in the lymph node cell cultures of the exposed mice exceeded that of the controls by more than 600%, whereas the release of IFN-gamma in the spleen cell cultures of the exposed mice was moderately different from the controls. It would appear from these results that the lung-associated lymph nodes are sensitive targets for chemical inhalation and that the results of systemic tests in the spleen may not mirror local immune response dysfunction. For risk assessment of inhaled chemicals, it is therefore important to take the local immunotoxic effects into consideration, in particular immunostimulation which may be involved in the rise in allergic diseases in industrialised countries.

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.

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.

Pulmonary bioactivation of 1,1-dichloroethylene is associated with CYP2E1 levels in A/J, CD-1, and C57BL/6 mice.

1,1-Dichloroethylene (DCE) elicits lung cytotoxicity and selectively targets Clara cells of bronchioles. The toxic effects are ascribed to CYP2E1-mediated formation of reactive intermediates including the DCE epoxide. Here we tested the hypothesis that differential CYP2E1 levels in the lungs of A/J, CD-1, and C57BL/6 mice lead to differences in the extents of DCE bioactivation and lung damage. Our results showed that lung CYP2E1 levels differed significantly in the three murine strains, and followed the rank order A/J > CD-1 > C57BL/6. Covalent binding of [(14)C]DCE to lung proteins in A/J mice was significantly higher than in either CD-1 or C57BL/6 mice. HPLC analysis of lung cytosol from DCE-treated mice showed that 2-S-glutathionyl acetate, a glutathione (GSH) conjugate derived from the epoxide (conjugate [C]), was the major metabolite formed. Levels of [C] detected in cytosol from A/J and CD-1 mice were significantly higher than in C57BL/6 mice. Immunohistochemical staining for [C] was pronounced in the lungs of A/J mice, was lower in CD-1 mice, and was lowest in C57BL/6 mice. Levels of GSH were similar in the lungs of all untreated mice. However, significant reduction in GSH was found in DCE-treated mice, with decreases comparable in all three strains. Bronchiolar Clara cell damage was more severe in A/J and CD-1 mice than in C57BL/6 mice. These results showed differences in CYP2E1 levels in the lungs of A/J, CD-1, and C57BL/6 mice that correlated with the extent to which the DCE epoxide is formed as well as with the severity of lung cytotoxicity.

Do endogenous volatile organic chemicals measured in breath reflect and maintain CYP2E1 levels in vivo?

The effect of trans-1,2-dichloroethylene (DCE), an inhibitor of cytochrome P450 (P450) 2E1 (CYP2E1), on the composition and quantity of volatile organic chemicals (VOCs) expired in the breath of male F-344 rats was determined in parallel with hepatic P450 activity and content. Hepatic microsomes were prepared from groups of rats prior to dosing and at 2, 5, 12, and 24 hr postdosing with DCE (100 mg/kg ip), and total P450 content and the activity of CYP2E1 was determined. Breath was collected from parallel groups of rats predose and at several intervals that encompassed the time points for rats euthanized for microsome preparation. Over 100 breath components were identified by GC/MS and quantitated by GC/FID. The overall change in the profile of breath VOCs resulting from administration of DCE was striking. An increase of approximately 1000% was measured in the mass of non-DCE-derived VOCs exhaled 4-6 hr after dosing, but there was no increase in hepatic lipid peroxidation. In addition to hexane, short-chain methyl ketones were particularly affected, and percentage increases in response to inhibition were inversely related to chain length, with acetone and 2-butanone > 2-pentanone >> 2-hexanone > 2-heptanone. There were no statistically significant decreases in total content of P450, but the activity of CYP2E1 was diminished about 65% at 2 and 5 hr after DCE treatment. However, 24 hr after inhibitor administration the total mass of VOCs expired was only marginally elevated above baseline and CYP2E1 activity was not significantly different from that of untreated rats. The compounds most markedly increased upon inhibition of CYP2E1 are also excellent inducers of that isozyme, and this finding is consistent with the hypothesis that these chemicals are important to the normal homeostasis of CYP2E1. The increase in breath components observed following inhibition of CYP2E1 suggests that VOCs in breath can reflect the activity of that isozyme in vivo.

Biotransformation and renal processing of nephrotoxic agents.

Nephrotoxicity is often observed as an endpoint in animal toxicity studies. In recent years, the mechanisms of biotransformation, which often provide the basis for renal toxicity, have been elucidated for a variety of compounds. These studies showed that nephrotoxicity of chemicals is either due to accumulation of certain metabolites in the kidney and further bioactivation or due to intrarenal bioactivation of the parent xenobiotic. Both types of mechanisms will be discussed using two relevant samples. The polychlorinated olefin hexachlorobutadiene and other haloolefins cause necrosis of the S-3 segment of the proximal tubules; their nephrotoxicity is dependent on bioactivation reactions. In the liver, hexachlorobutadiene is transformed by conjugation with glutathione to (S-pentachlorobutadienyl)glutathione. This S-conjugate is processed by the enzymes of mercapturic acid formation to give N-acetyl-(S-pentachlorobutadienyl)-L-cysteine, which is accumulated in the proximal tubule cells and deacetylated there to give (S-pentachlorobutadienyl)-L-cysteine. Further bioactivation is catalyzed by renal cysteine conjugate beta-lyase. Both the renal accumulation by the organic anion transporter and the topographical distribution of cysteine conjugate beta-lyase along the nephron are major determinants of organ and cell selectivity. Vinylidene chloride (VDC) is nephrotoxic in mice after inhalation, but not after oral or intraperitoneal administration. The nephrotoxicity of VDC is due to the selective expression of an androgen-dependent cytochrome P450 in the proximal tubules of male mice. This enzyme oxidizes VDC to an electrophile and is not present in female mice, but can be induced be androgen treatment. The observation of nephrotoxicity of VDC after inhalation only is due to the high blood flow to the kidney and thus high concentrations of VDC delivered to the kidney after inhalation. After oral or intraperitoneal application, hepatic first-pass metabolism efficiently reduces the amount of VDC delivered to the kidney. The results demonstrated here demonstrate that prior to in vitro nephrotoxicity screening, toxicokinetics and biotransformation pathways for a chemical have to be elucidated and metabolites have to be included into the testing regimen.

Renal tumorigenicity of 1,1-dichloroethene in mice: the role of male-specific expression of cytochrome P450 2E1 in the renal bioactivation of 1,1-dichloroethene.

1,1-Dichloroethene is used as intermediate in the manufacture of polymers. In male mice, 1,1-dichloroethene caused renal tumors after inhalation. Renal tumors were not observed in female mice or in both sexes of rats. We investigated the metabolic basis for the species- and sex-specific nephrotoxicity and tumorigenicity of 1,1-dichloroethene. Kidney microsomes from male mice biotransformed 1,1-dichloroethene to chloroacetic acid; the amounts of chloroacetic acid formed were dependent on the hormonal status of the animals and correlated well with the ability of kidney microsomes to oxidize p-nitrophenol and chlorozoxazone, specific substrates for cytochrome P450 2E1. In kidney microsomes from naive females, significantly lower rates of oxidation of 1,1-dichloroethene, p-nitrophenol, and chlorozoxazone were observed; oxidation could be induced by testosterone. With a rabbit anti-rat liver cytochrome P450 2E1 antibody, a cross-reactive protein was detected in male mouse kidney microsomes with a molecular weight very similar to that of rat liver cytochrome P450 2E1; the expression of this protein was regulated by testosterone and correlated well with the ability of the microsomes to oxidize p-nitrophenol, chlorozoxazone, and 1,1-dichloroethene. When the relative cytochrome P450 2E1 contents of renal microsomes of male mice from different strains were compared, differences in the expression of cytochrome P450 2E1 were observed. Moreover, nephrotoxicity in Swiss-Webster mice after inhalation of 1,1-dichloroethene was observed only in males and testosterone-treated females, but not in naive females. In kidney microsomes obtained from both sexes of rats and in six samples of human kidney (male donors), no p-nitrophenol oxidase activity was detected. These data suggest that cytochrome P450 2E1 or a P450 enzyme with very similar molecular weight, substrate specificities, and immunological properties is expressed only in male mouse kidney and bioactivates 1,1-dichloroethene.

Hyperthyroidism increases covalent binding and biliary excretion of 1,1-dichloroethylene in rats.

Distribution, covalent binding, and biliary excretion of 1,1-dichloroethylene (DCE) were examined in euthyroid (EuT) and hyperthyroid (HyperT) rats, which are more vulnerable to DCE hepatotoxicity. Male Sprague-Dawley rats were made hyperthyroid by 3 sc injections of thyroxine at 48-h intervals prior to experiments; euthyroid controls received vehicle injections. A time course study monitored the circulation and excretion of 14C-DCE label for 24 h after administration of 14C-labeled DCE (50 mg/kg in mineral oil) in serial blood and urine samples. At 24 h, total and covalently bound 14C-label were measured in liver, kidney, and lung. Hepatotoxicity of DCE was enhanced in the HyperT rats, as evidenced by elevated serum activities of aminotransferase and histopathology, and was associated with increases in circulating metabolite, and in metabolite bound to red blood cells and liver but not to kidney or lung. Hyperthyroidism had little effect on in vitro capacity of hepatic microsomes to convert DCE to reactive intermediates as reflected by covalent binding. A biliary excretion study in pentobarbital-anesthetized rats showed a striking, but transient, increase in toxicant metabolite excretion in bile of HyperT rats during the first 2 h after toxicant administration (14C-DCE, 100 mg/kg). During the next 2 h, biliary metabolite excretion by HyperT rats decreased while there was a rise in circulating amounts of total and bound 14C-label. Thus, although hyperthyroidism had little effect on the total extent of DCE metabolized, this hormonal disturbance may have transiently enhanced metabolite formation and definitely was associated with a lesser ability to detoxify reactive DCE metabolites capable of injuring hepatic cell constituents by covalent binding reactions.

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.

Influence of enzyme induction and exposure profile on liver injury due to chlorinated hydrocarbon inhalation.

Rats were exposed for four weeks either to air or to vapours of chloroform, carbon tetrachloride or 1,1-dichloroethylene given either as a constant concentration (continuous profile) or as repeated exposures for 6 hr per day, 5 days per week (fluctuating profile). Vapour concentrations were used such that the total exposure (concentration x time) was the same for the two profiles. Within each group, some animals received the enzyme-inducing agents, phenobarbitone or 1,3-butanediol, in their drinking water. Separate experiments were conducted to determine the influence of enzyme inducers and vapour concentration on chlorocarbon uptake and metabolism. In the case of chloroform, hepatic injury was more severe in animals exposed to constant vapour concentration, while dichloroethylene was more toxic when given as a fluctuating profile, especially in butanediol-treated rats. Carbon tetrachloride hepatotoxicity was similar in the two exposure profiles but was exacerbated by butanediol treatment. Butanediol-treated animals in the fluctuating profile group showed evidence of developing cirrhosis. These results could not be fully explained on the basis of the effect of enzyme inducers and exposure profile on amount of agent metabolized. Both the amount of toxic metabolites and the temporal pattern of their formation appear to be important determinants of liver injury.

Long-term carcinogenicity bioassay on vinylidene chloride administered by inhalation to Sprague-Dawley rats. New results.

Vinylidene chloride was administered by inhalation, 7 hours daily, 5 days weekly, at the concentration of 100 and 0 ppm, to Sprague-Dawley rats. The treatment was started on 13-week-old breeders, and male and female offspring (12-day embryos). The breeders and some of the offspring were exposed for 104 weeks; the other offspring were exposed for 15 weeks only. An increased incidence was found of malignant tumors and of leukemias, particularly in offspring treated for 104 weeks.

Lactate dehydrogenase activity in mouse lung following 1,1-dichloroethylene: index of airway injury.

Lactate dehydrogenase (LD) activity and its isozyme profile in mouse lung homogenate was affected by oral administration of 1,1-dichloroethylene (1,1-DCE). Following 100 mg 1,1-DCE/kg, LD-3 increased significantly. After 200 mg 1,1-DCE/kg, LD-5 increased whereas LD-1 and LD-2 decreased, with a resultant higher M:H ratio than controls. In contrast, elevated LD activity in serum following 1,1-DCE was predominantly associated with striking increases in total activity and changes in isozyme patterns resulting in a decrease in the M:H ratio. LD activity in liver and erythrocytes were unaffected by 1,1,-DCE administration. Although total activity in kidney was decreased, no changes were detected in the isozyme profile. Pulmonary damage induced by 1,1-DCE was reflected in significant increases in total activity and all isozymes in bronchopulmonary lavage fluids. Thus, detection of lung-derived LD activity in lung lavage fluids can be a useful index of pulmonary airway injury.

Molecular mechanism of 1,1-dichloroethylene toxicity: excreted metabolites reveal different pathways of reactive intermediates.

The excretion and biotransformation of [14C] 1,1-dichloroethylene (vinylidene chloride, VDC) after administration of a single oral dose has been investigated in female rats. Seventy-two hours after a dose of 0.5, 5.0, and 50.0 mg/kg, 1.26, 9.70, 16.47%, respectively, are exhaled as unchanged VDC, and 13.64, 11.35, 6.13% as 14CO2. The main pathway of elimination is through renal excretion with 43.55, 53.88, 42.11% of the administered radioactivity. Through the biliary system, 15.74, 14.54, 7.65% of the activity are eliminated. The isolation of the main metabolites of VDC from 24 h urine is accomplished through the combined application of solvent extraction, ion exchange chromatography and thin layer chromatography. Then gas chromatography and mass spectrometry are used for their identification. Three metabolites have been identified: thiodiglycolic acid, N-acetyl-S-(2-carboxymethyl)cysteine and methyl-thio-acetylaminoethanol. In addition, three smaller unidentified radioactive peaks have been found. Thiodiglycolic acid is the main metabolite in VDC metabolism. The simultaneous formation of an ethanolamine- and a cysteine-conjugation product points to different reaction pathways of the postulated intermediate reactive epoxide; ethanolamine probably originates from membrane lipids, which react with VDC-epoxide and/or its derivatives. This pathway could explain, in part, the parenchyma damaging effect of VDC.