The effect of dose and vehicle on early tissue damage and regenerative activity after chloroform administration to mice

Correlation of a specific mitochondrial phospholipid-phosgene adduct with chloroform acute toxicity

The dose and time dependence of formation of a specific adduct between mitochondrial phospholipid and phosgene have been determined in the liver of Sprague-Dawley (SD) rats as well as in the liver and kidney of B6C3F1 mice after dosing with chloroform. Rats were induced with phenobarbital or non-induced. Determination of tissue glutathione (GSH) and of serum markers of hepatotoxicity and nephrotoxicity was also carried out. With dose-dependence experiments, a strong correlation between the formation of the specific phospholipid adduct, GSH depletion and organ toxicity could be evidenced in all the organs studied. With non-induced SD rats, no such effects could be induced up to a dose of 740 mg/kg. Time-course studies with B6C3F1 mice indicated that the specific adduct formation took place at very early times after chloroform dosing and was concurrent with GSH depletion. The adduct formed during even transient GSH depletion (residual level: 30% of control) and persisted after restoration of GSH levels. Following a chloroform dose at the hepatotoxicity threshold (150 mg/kg), the elimination of the adduct in the liver occurred within 24 h and correlated with the recovery of ALT, which was slightly increased (12 times) after treatment. Following a moderately nephrotoxic dose (60 mg/kg), the renal adduct persisted longer than 48 h, when a 100% increase in blood urea nitrogen and a 40% increase in serum creatinine indicated the onset of organ damage. The formation of the adduct in the liver mitochondria of B6C3F1 mice was associated with the decrease of phosphatidyl-ethanolamine (PE), in line with previous results in rat liver indicating that the adduct results from the reaction of phosgene with PE. The adduct levels implicated the reaction of phosgene with about 50% PE molecules in the liver mitochondrial membrane of phenobarbital-induced SD rats and of about 10% PE molecules of the inner mitochondrial membrane of the liver of B6C3F1 mice. The association of this adduct with the toxic effects of chloroform makes it a very good candidate as the primary critical alteration in the sequence of events leading to cell death caused by chloroform.

Effect of dosing vehicle on the hepatotoxicity of CCl4 and nephrotoxicity of CHCl3 in rats

There are conflicting results in the literature concerning the effect of gavage vehicle, corn oil (CO) versus aqueous suspension, on the toxicity of haloalkanes. The purpose of our study was to assess the influence of oral dosing vehicle on the acute hepatotoxicity of CCl4 and nephrotoxicity of CHCl3. Male Sprague-Dawley rats, fed ad libitum, were treated (po) with single doses of CCl4 or CHCl3 using corn oil (CO), or an aqueous preparation (5%) of Emulphor (EL620) or Tween-85 (Tw-85) as vehicle (10 ml/kg). Rats were killed 48 h after treatment. Blood was collected for plasma alanine aminotransferase (ALT) determination and renal cortical slices were prepared for p-aminohippuric acid (PAH) incorporation. The comparison, between gavage vehicles, of the slopes and ED50 of the dose-response curves, although not significantly different, indicated clear trends for enhanced potency with CO for CHCl3 nephrotoxicity but not for CCl4 hepatotoxicity. However, ALT values, a measure of the severity of effect for CCl4, also indicated that CO, when compared to EL620 and Tw-85, tended to enhance CCl4 hepatotoxicity at low toxicity incidence. Furthermore, CO clearly enhanced the severity of effect for CHCl3 nephrotoxicity, as measured by the slice-to-medium PAH ratios, at high dosage. The greater severity of the lesion produced by exposure to these chemicals, when administered in CO, is consistent with the trends observed for their potency (dose-response curves). Our results agree with an increased toxicity of haloalkanes by the gavage vehicle CO reported in the literature. Thus, CO should be considered a potential confounder in hepato- and nephrotoxicity assays.

Effect of oral dosing vehicles on the subchronic hepatotoxicity of carbon tetrachloride in the rat

Previous studies in this laboratory have shown that corn oil delayed and prolonged the gastrointestinal absorption of carbon tetrachloride (CCl4) and reduced its acute hepatotoxicity in rats. The objective of the present study was to extend the duration of ingestion of CCl4 to assess vehicle effects on the subchronic oral toxicity of CCl4. Male Harlan Sprague-Dawley rats were given doses of 0, 25, or 100 mg CCl4/kg body weight by gavage in either corn oil or a 1% Emulphor aqueous emulsion 5 times a week for 13 wk. Blood was collected at 4, 8, and 13 wk for measurement of serum enzymes. Liver samples were also taken at 13 wk for measurement of triglyceride and microsomal enzyme levels, as well as for histopathological examination. Serum enzyme levels peaked at 8 wk in the high-dose groups, but not until 13 wk in the low-dose animals. Effects of CCl4 on serum and microsomal enzymes were of similar magnitude in the two vehicle groups. A comprehensive histopathological examination revealed no qualitative or quantitative differences between the corn oil and aqueous vehicle groups in hepatic lesions. Although CCl4 and chloroform have been reported by other investigators to be more hepatotoxic to mice when given for 90 d in corn oil, current findings indicate that corn oil does not significantly alter the subchronic hepatotoxicity of CCl4 in rats from that when the halocarbon is given in an aqueous medium.

A review of the carcinogenicity of chemicals most frequently found at National Priorities List sites

Several studies have shown that numerous National Priorities List (NPL) sites have been contaminated with arsenic (747), cadmium (791), chloroform (596), or nickel (664). The National Toxicology Program (NTP, 1991) has classified these substances as known human carcinogens (arsenic and certain arsenic compounds) or as substances that may reasonably be anticipated to be carcinogens (cadmium and certain cadmium compounds, chloroform, and nickel and certain nickel compounds). The general population is probably exposed to low levels of these hazardous substances through drinking water, eating food, or inhaling contaminated air. People working or living near industries and facilities that manufacture and use chloroform, nickel, arsenic, or cadmium may be exposed to higher than background levels of these hazardous substances. Multiple pathways of exposure may exist for populations near hazardous waste sites. For example, high levels of chloroform (1,890 ppb) were found in well water near a waste site; high levels of cadmium exposure may exist for individuals living near cadmium-contaminated waste sites.

The time course of liver injury and [3H]thymidine incorporation in chlordecone-potentiated CHCl3 hepatotoxicity

The mechanism by which chlordecone (CD) potentiates CHCl3 hepatotoxicity and lethality remains unknown. We examined the time course of the hepatotoxicity by following serum enzymes, liver histopathology, hepatocellular regeneration, and tissue repair by morphometric analysis and [3H]thymidine (3H-T) incorporation into nuclear DNA. Male mice fed control, or CD (10 ppm), mirex (Mx. 10 ppm), or phenobarbital (PB. 225 ppm) diets for 15 days and receiving a single ip dose of 0.1 ml CHCl3/kg in corn oil vehicle were used. Liver damage was assessed by plasma alanine and aspartate transaminases and by histopathology at 4, 12, 24, 36, 48, 72, and 96 hr after CHCl3 administration. None of the dietary pretreatments caused plasma transaminase elevations, any liver necrosis, or any increase in 3H-T incorporation in nuclear DNA at any time. CHCl3 alone caused only limited hepatocellular necrosis without any increase in plasma transaminases. The same dose of CHCl3 given to CD-pretreated mice resulted in greatly increased liver injury. Plasma transaminases were elevated starting at 4 hr, reaching a maximum value at 12 hr and a decline starting at 48 hr. Centrilobular and midzonal necroses were evident at 12 hr onward. PB pretreatment caused some increase in CHCl3-induced necrosis and a moderate rise in transaminases at 24 hr, but Mx pretreatment caused neither effect. 3H-T incorporation was increased at 72 and 96 hr after CHCl3 alone. The same dose of CHCl3 caused only a modest increase in PB and Mx and a significant and maximal biphasic increase at 36 and 72 hr CD-pretreated mice. Morphometry of liver sections indicated that hepatocellular regeneration is stimulated at 72 hr after CHCl3 alone. The same dose of CHCl3 results in a greater stimulation of hepatocellular regeneration in CD-pretreated mice, and this event is pushed forward at 48 hr, continuing through 96 hr to compensate for greater hepatocellular necrosis associated with this treatment. Lesser stimulation of hepatocellular regeneration was observed in PB + CHCl3 and Mx + CHCl3 groups of mice consonance with much lesser hepatotoxicity. These results suggest that the critical decisive event in the recovery from limited hepatocellular injury is the hepatocellular regeneration and tissue repair, which appear to be stimulated in proportion to the injury.

Ranking possible carcinogenic hazards

This review discusses reasons why animal cancer tests cannot be used to predict absolute human risks. Such tests, however, may be used to indicate that some chemicals might be of greater concern than others. Possible hazards to humans from a variety of rodent carcinogens are ranked by an index that relates the potency of each carcinogen in rodents to the exposure in humans. This ranking suggests that carcinogenic hazards from current levels of pesticide residues or water pollution are likely to be of minimal concern relative to the background levels of natural substances, though one cannot say whether these natural exposures are likely to be of major or minor importance.