Studies on the distribution and covalent binding of 1,1-dichloroethylene in the mouse. Effect of various pretreatments on covalent binding in vivo

1,1-Dichloroethylene-Induced Mitochondrial Damage Precedes Apoptotic Cell Death of Bronchiolar Epithelial Cells in Murine Lung

1,1-Dichloroethylene (DCE) causes pulmonary injury that is characterized by necrosis of bronchiolar Clara cells. Mitochondria have been identified as an early target in the toxic response. Because mitochondria have been implicated in both necrotic and apoptotic cell death, we have undertaken studies to test the hypothesis that DCE induces apoptosis, in addition to necrosis, in murine lung. A primary objective is to identify the biochemical events associated with pulmonary apoptosis. Groups of female CD-1 mice were treated with DCE (75 mg/kg i.p.) or corn oil. Using an antibody directed against DCE-cysteine conjugates, adducts were detected primarily in association with mitochondria in the apices of bronchiolar Clara cells. Furthermore, morphological studies demonstrated early mitochondrial alterations in Clara cells that included severe swelling and disruption of cristae. Western blotting of lung cytosolic proteins showed greater immunoreactivity for cytochrome c in fractions from mice treated with DCE for 4 h than in controls. Immunohistochemical studies with an antibody to activated caspase-3 and terminal deoxynucleotidyl transferase dUTP nick-end labeling were used to detect apoptotic cells. In both experiments, positive reactivities were observed in the bronchiolar epithelium at 12 and 24 h after DCE treatment, whereas reactivities were absent in tissues from control animals. Finally, bronchiolar epithelial cells showing morphological criteria of apoptosis (chromatin condensation and margination) were observed at 24 h after 75 and 125 mg/kg DCE. Apoptotic-like cells were more abundant in larger bronchioles. These data suggested that DCE produces pulmonary bronchiolar apoptosis by inducing mitochondrial perturbations, causing release of cytochrome c into the cytosol and caspase activation.

Evidence That 1,1-Dichloroethylene Induces Apoptotic Cell Death in Murine Liver

1,1-Dichloroethylene (DCE) causes dysfunction of hepatic mitochondria. As mitochondria have been implicated in apoptosis through opening of the permeability transition pore (PTP), we have undertaken studies to test the hypothesis that DCE induces apoptosis, in addition to necrosis, in murine liver. Our primary objective was to identify the biochemical events associated with DCE-induced apoptosis. Female CD-1 mice were treated with a mildly hepatotoxic dose of DCE (125 mg/kg, i.p.). Using the fluorescent dye JC-1 (5,5',6,6'-tetrachloro-1,1',3,3'-tetraethylbenzimidazolocarbocyanine iodide), decreased hepatic mitochondrial membrane potential was detected at 2 h. Western blotting of liver cytosolic proteins showed greater immunoreactivity for cytochrome c in fractions from mice treated with DCE for 4 h than in controls. Furthermore, caspase-9 activity was significantly increased 6 h after DCE exposure. Immunohistochemical studies with an antibody to activated caspase-3 and terminal deoxynucleotidyl transferase dUTP nick-end labeling staining were used to detect apoptotic cells. In both experiments, positive reactivities were observed in centrilobular hepatocytes 12 and 24 h after DCE. Additionally, centrilobular hepatocytes showing morphological criteria of apoptosis were observed at 24 h. Apoptosis and all apoptotic events were inhibited by pretreatment for 20 min with cyclosporine A (CyA) (50 mg/kg), a specific inhibitor of the mitochondrial PTP. To determine a major role for mitochondrial permeability transition (MPT) in DCE hepatotoxicity, serum alanine aminotransferase (ALT) activity was evaluated. ALT activity was significantly elevated 2 to 24 h after DCE, and CyA failed to inhibit this activity. These data suggested that DCE produces apoptosis by inducing MPT, causing release of cytochrome c into the cytosol and caspase activation.

Mitochondrial dysfunction is an early manifestation of 1,1-dichloroethylene-induced hepatotoxicity in mice

Hepatotoxicity induced by 1,1-dichloroethylene (DCE) is mediated by cytochrome P450-dependent metabolism to reactive intermediates, including the epoxide. We have tested the hypothesis that mitochondria are a primary target of toxicity by investigating dose- and time-dependent effects of DCE on mitochondrial respiration. Hepatotoxicity, as assessed by serum alanine aminotransferase (ALT) activity, was evaluated. We have also determined the effectiveness of N-acetyl-L-cysteine (NAC) in protecting against respiratory perturbations and hepatotoxicity. Liver mitochondria were isolated 2 h after DCE (50, 75, 100, 125, and 150 mg/kg) treatment. Glutamate (complex I)- and succinate (complex II)-supported mitochondrial respiration was assessed by measurement of state 3 (ADP-stimulated) and state 4 (resting) rates of oxygen consumption. The corresponding respiratory control ratios (RCRs, state 3/state 4) and ADP:O ratios were then calculated. A DCE dose of 125 mg/kg significantly inhibited glutamate- and succinate-supported state 3 respiration, leading to a significant reduction in corresponding RCRs and ADP:O ratios. In time-dependent studies, state 3 respiration rates and RCRs for glutamate-supported respiration were significantly decreased as early as 20 min after DCE (125 mg/kg) treatment, whereas those for succinate-supported respiration were significantly decreased at 90 min. Additionally, ADP:O ratios for glutamate-supported respiration were significantly decreased starting at 60 min, and those for succinate-supported respiration at 90 min. Alterations in mitochondrial function preceded significant increases in ALT activity, which was first manifested at 2 h. Pretreatment with NAC (1200 mg/kg) abrogated DCE-induced GSH depletion and inhibited disturbances in mitochondrial respiration. Moreover, NAC protected against increased ALT activity, suggesting that the protective effect of NAC is due to increased GSH for conjugation reactions and/or its antioxidant property. These results showed that DCE-mediated mitochondrial dysfunction is an early event that preceded the onset of hepatotoxicity.

Mechanisms of 1,1-dichloroethylene-induced cytotoxicity in lung and liver

Exposure to 1,1-dichloroethylene (DCE) causes lung and liver toxicities in mice. The lesions are characterized by damage preferentially to bronchiolar Clara cells in the lung and necrosis of centrilobular hepatocytes in the liver. The primary metabolites formed from DCE in lung and liver microsomal incubations are the epoxide, 2,2-dichloroacetaldehyde and 2-chloroacetyl chloride, which undergo hydrolysis and/or conjugation with glutathione (GSH). The major products formed are the epoxide-derived GSH conjugates 2-(S-glutathionyl) acetyl glutathione [B] and 2-S-glutathionyl acetate [C]. The hydrate of 2,2-dichloroacetaldehyde (acetal) is also detected. These metabolites are detected in vivo in murine lung and liver cytosol and in bile, and importantly, also in human lung and liver microsomal incubations. Formation of the epoxide is mediated mainly by CYP2E1. Immunohistochemical studies localized the epoxide-derived GSH conjugate [C] and cysteine-containing proteins in Clara cells and centrilobular hepatocytes. These findings are consistent with the premise that the lung and liver cytotoxicities induced by DCE are associated with in situ formation of the epoxide within the target cells.

1,1-Dichloroethylene-induced Clara cell damage is associated with in situ formation of the reactive epoxide. Immunohistochemical detection of its glutathione conjugate

Pulmonary Clara cells are selectively damaged in mice given 1, 1-dichloroethylene (DCE), a chemical used in the plastics industry. The cytotoxicity is attributed to formation of a reactive metabolite believed to be the DCE-epoxide, which was detected in vitro. We have undertaken in vivo studies to test the hypothesis that in situ formation of the DCE-epoxide within Clara cells mediates the cell-specific injury manifested after DCE exposure. Formation of the epoxide was estimated by trapping of the metabolite with glutathione (GSH) and identifying the conjugated products as 2-(S-glutathionyl) acetyl glutathione ([B]) and 2-S-glutathionyl acetate ([C]). High-pressure liquid chromatographic analyses showed that conjugates [B] and [C] were both detected in lung cytosol isolated from mice treated in vivo with [14C]DCE. Epoxide levels in the cytosol, as estimated by the total amount of conjugates formed, were dose-dependent at DCE doses ranging from 25 to 225 mg/kg. Pretreatment of mice with buthionine sulfoximine (BSO) decreased sulfhydryl levels and significantly inhibited the formation of the GSH conjugates. Epoxide levels were also reduced by pretreatment with diallyl sulfone (DASO2), an inhibitor of the P450 isozyme CYP2E1. A polyclonal antibody was developed that is specific for conjugate [C] and that recognizes an antigen consisting of the conjugate epoxide-GSH-glutaraldehyde-bovine serum albumin. Immunohistochemical studies with this antibody revealed staining in Clara cells of mice treated with DCE. Staining was also present in Clara cells of mice treated with both BSO and DCE, but at slightly reduced levels. Reduction of this staining was more pronounced in Clara cells of mice treated with both DASO2 and DCE. These results show that the DCE-epoxide is formed in vivo, is localized in Clara cells, and correlates with the cytotoxicity manifested in this cell type.

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.

Methylene chloride: an inhalation study to investigate toxicity in the mouse lung using morphological, biochemical and Clara cell culture techniques

Single exposures of mice to methylene chloride (MC) cause vacuolation and necrosis of the bronchiolar Clara cells which subsequently recover normal morphology on continued exposure. Both cytochrome P-450 (CYP)- and glutathione S-transferase (GST)-dependent metabolism of MC are known to occur. The current studies have investigated the metabolism of MC in mouse lung using inhibitors of both GST and CYP-dependent routes of metabolism, the consequences of metabolic inhibition on the Clara cell vacuolation, and any changes in cell proliferation, assessed in vitro, in Clara cells cultured from exposed individuals. Vacuolated bronchiolar cells were seen in mice exposed to 2000 and 4000 ppm MC but were not seen at lower concentrations, while addition of the CYP inhibitor, piperonyl butoxide, significantly reduced the bronchiolar cell vacuolation seen following exposure to 2000 ppm MC. Treatment of mice with the glutathione depletor, buthionine sulphoximine, had no effect on the number of vacuolated bronchiolar cells following MC. Exposure of mice to 1000 ppm MC and above for 6 h caused a burst of DNA synthesis in bronchiolar Clara cells cultured in vitro from the lungs of exposed animals. The results suggest that the Clara cell vacuolation following MC exposure is mediated via CYP metabolism, that depression of the CYP metabolic pathway occurs following exposure, and that Clara cell vacuolation may have a priming role in stimulating cell proliferation in the unaffected cell population.

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.

Nephrotoxicity and covalent binding of 1,1-dichloroethylene in buthionine sulphoximine-treated mice

Autoradiography of mice injected i.p. with 14C-labelled 1,1-dichloroethylene (vinylidene chloride, VDC) in C57B1/6 mice revealed a selective covalent binding of radioactivity in the proximal tubules, in the midzonal parts of the liver lobules and in the mucosa of the upper and lower respiratory tract. Since VDC is a renal carcinogen in male mice the effects of compounds modulating biotransformation and glutathione (GSH) levels on the renal covalent binding were examined following a single i.p. dose of 14C-VDC. Most pretreatments did not influence the level of binding but treatment with buthionine sulphoximine (BSO), an irreversible inhibitor of gamma-glutamylcysteine synthetase and glutathione (GSH)-depleting agent, increased the renal covalent binding of VDC three-fold. Histopathological examination of kidneys in BSO-pretreated male mice given single i.p. injections of subtoxic doses of VDC (25 and 50 mg/kg) showed necrosis in the proximal tubules (S1 and S2 segments) 24 h following administration. In mice given VDC only, no significant lesions in the kidneys were observed. The severe renal toxicity of VDC in BSO-pretreated mice is suggested to be related to metabolic activation of VDC in the proximal tubules, resulting in further GSH depletion and covalent binding.

1,1-Dichloroethylene-induced alterations in glutathione and covalent binding in murine lung: morphological, histochemical, and biochemical studies

Non-ciliated Clara cells of the pulmonary bronchiolar epithelium are preferentially damaged by administration of 1,1-dichloroethylene (1,1-DCE) to mice. In this study, an in vivo system was utilized to investigate the dose-dependent effects of 1,1-DCE (75, 125, 175, and 225 mg/kg) on covalent binding and on reduced glutathione (GSH) in murine lung. Treatment of mice with each dose level of 1,1-DCE elicited significant decreases in GSH content and resulted in covalent binding of [14C]1,1-DCE in a dose-dependent manner. Histochemical staining for GSH in lungs of control mice revealed positive cellular sites in alveolar septa and bronchiolar epithelium, with the highest staining intensities in Clara cells. Staining was reduced after exposure to 75 and 125 mg/kg 1,1-DCE, and at higher doses it was abolished in alveolar septa and retained in bronchiolar epithelium, albeit at considerably reduced intensities. Heterogeneity with respect to staining intensities was consistently observed in the Clara cell population in both control and 1,1-DCE-treated mice. Progressive increases in covalent binding and decreases in GSH content correlated with increasing severities of Clara cell injury. These results show a dose dependence in regard to the magnitudes of [14C]1,1-DCE binding, the alterations in cellular GSH, and the severities of Clara cell necrosis.

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.

Potentiation of 1,1-dichloroethylene hepatotoxicity: comparative effects of hyperthyroidism and fasting

The responses of fed, fasted, and hyperthyroid (T4) Sprague-Dawley male rats to 50 mg 1,1-dichloroethylene (1,1-DCE)/kg were compared. Hyperthyroid rats received three sc injections of thyroxine (100 micrograms/100 g) at 48-hr intervals; all other rats were sham-injected. 1,1-DCE was given po in mineral oil 24 hr after the last T4 dose; controls received only mineral oil. Animals were killed at 2, 4, and 8 hr. Liver GSH contents were lowered about 55% by both fasting and T4 while GSH transferase activities were lowered about 20% by fasting and 35% by T4. Only T4 pretreatment lowered alcohol dehydrogenase activities. Liver injury (i.e., serum glutamate pyruvate transaminase, histology) after 1,1-DCE was minimal in fed rats, moderate in fasted rats, and intermediate in T4 rats. Fasted rats showed a more pronounced depletion of liver GSH after 1,1-DCE than T4 rats and only in fasted rats did the toxicant decrease activities of the detoxification enzymes. Hypoglycemia after 1,1-DCE occurred in fed rats, but more rapidly in T4 rats. In contrast, fasted rats unexpectedly became hyperglycemic after the toxicant. Patterns of body temperature change after the toxicant, which might be due to its metabolites, were dissimilar. Hypothermia was not observed in fed rats, was only transiently evident in T4 rats, but occurred rapidly within 1 hr in fasted rats and steadily became more severe. The dissimilar patterns of liver enzyme and body temperature and serum glucose change after the toxicant in the three groups are indicative of different pathways of injury potentiation by fasting and hyperthyroidism.

In vitro studies on the metabolism and covalent binding of [14C]1,1-dichloroethylene by mouse liver, kidney and lung

The metabolism and covalent binding of 1,1-dichloro[1,2-14C]ethylene (DCE) to subcellular fractions of liver, kidney and lung of C57BL/6N mice have been investigated in vitro. Covalent binding was NADPH- and cytochrome P-450-dependent. The microsomal fraction bound more radiolabel than any other subcellular fraction, and the levels of covalent binding in cell fractions correlated well with their cytochrome P-450 content. Covalent binding by mouse liver and lung microsomes also reflected their cytochrome P-450 content. However, although mouse kidney microsomes contained twice as much total cytochrome P-450 as the lung, no detectable covalent binding of DCE-derived radioactivity occurred in kidney. Omission of NADPH, heat inactivation of microsomes, carbon monoxide, addition of SKF-525A, piperonyl butoxide or reduced glutathione (GSH), all inhibited (40-90%) covalent binding of radiolabel to liver and lung microsomes. The absence of O2 (incubation under N2) did not greatly affect the metabolism and covalent binding. Pretreatment of mice with various inducers, phenobarbital (PB), beta-naphthoflavone (beta-NF), pregnenolone 16 alpha-carbonitrile (PCN) and 3-methylcholanthrene (3-MC), evoked increases in total liver microsomal cytochrome P-450 content (2-fold) and corresponding increases in covalent binding (3-fold). However, microsomes from PCN-treated mice showed only a 50% increase in DCE binding. Kidney microsomes from control, PB-, and beta-NF-pretreated mice were incapable of covalent binding of radiolabel but those from PCN- and 3-MC-pretreated mice showed levels of binding similar to untreated mouse lung microsomes. It is proposed that the nephrotoxicity of DCE may be due to translocation of reactive metabolites from the liver to the kidney.