Inhalation carcinogenicity of 1,1,1-trichloroethane in rats and mice.

Carcinogenicity of 1,1,1-trichloroethane (TCE) was examined by an inhalation exposure of F344 rats and BDF1 mice of both sexes to TCE at 0, 200, 800 or 3200 ppm for 6 h/d, 5 d/week for 104 weeks. In male rats, the incidences of bronchiolo-alveolar adenomas and peritoneal mesotheliomas were significantly increased in the 800 and 3200 ppm-exposed groups, respectively. The incidence of bronchiolo-alveolar adenomas in the 3200 ppm-exposed groups exceeded the range of historical control data in the Japan Bioassay Research Center. In female rats, the tumor incidences were not increased in any organs of the TCE-exposed groups. In male mice, a significant positive trend with dose was shown for incidences of bronchiolo-alveolar carcinomas, combined incidences of bronchiolo-alveolar adenomas/carcinomas and hepatocellular adenomas. The incidence of Harderian gland adenomas was significantly increased in the 3200 ppm-exposed group, and malignant lymphomas of spleen at this highest dose exceeded the range of historical control data. In female mice, the combined incidence of bronchiolo-alveolar adenomas/carcinomas was significantly increased in the 3200 ppm-exposed group, and the incidences of hepatocellular adenomas and combined incidences of hepatocellular adenomas/carcinomas were significantly increased in the 200, 800 and 3200 ppm-exposed groups with dose dependence except the combined incidence of hepatocellular adenomas/carcinomas in the 200 ppm-exposed group. The incidences of bronchiolo-alveolar adenomas in the 3200 ppm-exposed group and combined incidences of hepatocellular adenomas/carcinomas in the 200 ppm-exposed groups exceeded the ranges of historical control data. Thus, this study provided clear evidence of inhalation carcinogenicity for TCE in both rats and mice.

Toxicity of industrially relevant chlorinated organic solvents in vitro.

The cytotoxic effects of 4 industrially important chlorinated organic solvents, dichloromethane (DCM), 1,2-dichloroethane (DCE), trichloroethylene (TCE), and tetrachloroethylene (PERC) in vitro, were investigated. Jurkat T cells were exposed to the solvents individually for 72 hours and changes in reactive oxygen species (ROS) formation, cell proliferation, intracellular free calcium concentration ([Ca(2+)]), and caspase-3 activity were measured. There was a concentration-dependent increase in the ROS formation and intracellular free [Ca(2+)] following exposure to each of the solvents. This was accompanied by a decrease in the cell proliferation. Solvent potency decreased in the following order: PERC > TCE > DCM > DCE. Caspase-3 activity was increased in a concentration-dependent manner by TCE and PERC but was not significantly altered by DCM or DCE. n-Acetyl-l-cysteine pretreatment showed that changes in the intracellular free [Ca(2+)] and caspase-3 activity were independent of ROS formation. However, increased ROS formation did play a causal role in the decreased cell proliferation observed.

Comparative analysis of S-fatty acylation of gel-separated proteins by stable isotope-coded fatty acid transmethylation and mass spectrometry.

Covalent attachment of palmitic acid or other fatty acids to the thiol groups of cysteine residues of proteins through reversible thioester bonds has an important role in the regulation of diverse biological processes. We describe here the development of a mass spectrometry protocol based on stable isotope-coded fatty acid transmethylation (iFAT) for qualitative and comparative analysis of protein S-fatty acylation under different experimental conditions. In this approach, cellular proteins extracted from different cell states are separated by SDS-PAGE and then the gel is stained with either Coomassie blue or Nile red for improved sensitivity. Protein bands are excised and then an in-gel stable iFAT procedure is performed. The fatty acid methyl esters resulting from derivatization with d0- and d3-methanol are identified by mass spectrometry. By measuring the intensities of labeled and unlabeled fragment ion pairs of fatty acid methyl esters, the levels of S-fatty acylation in different cells or tissues can be compared. This approach has been applied to monitor the changes of S-fatty acylation of zebrafish liver proteome in response to environmental dichlorodiphenyltrichloroethane exposure. Compared with the approach using metabolic incorporation of radioactive fatty acid analogs, it is not only simple and effective but also eliminates the hazards of handling radioactive isotopes.

Health risk assessment of exposure to selected volatile organic compounds emitted from an integrated iron and steel plant.

Workplace air samples from sintering, cokemaking, and hot and cold forming processes in the integrated iron and steel industry were analyzed to determine their volatile organic compound (VOC) concentration. Sixteen VOC species including three paraffins (cyclohexane, n-hexane, methylcyclohexane), five chlorinated VOC species (trichloroethylene, 1,1,1-trichloroethane, tetrachloroethylene, chlorobenzene, 1,4-dichlorobenzene), and eight aromatics (benzene, ethylbenzene, styrene, toluene, m,p-xylene, o-xylene, 1,2,4-trimethylbenzene, 1,3,5-trimethylbenzene) were selected to measure their noncancer risk for workers. Concentrations of toluene, xylene, 1,2,4-trimethylbenzene, 1,3,5-trimethylbenzene, dichlorobenzene, and trichloroethylene were high in all four processes. Carbon tetrachloride and tetrachloroethylene concentrations were high in the hot and cold forming processes. The noncancer risk followed the increasing order: cokemaking > sintering > hot forming > cold forming. 1,2,4-trimethylbenzene and 1,3,5-trimethylbenzene contributed 44% to 65% and 13% to 20% of noncancer risk, respectively, for the four processes. Benzene accounted for a high portion of the noncancer risk in cokemaking. The hazard index (HI: 17-108) of the average VOC concentrations suggests that health risks can be reduced by improving workplace air quality and protecting workers.

The National Exposure Registry: history and lessons learned.

The National Exposure Registry (NER) was created as a comprehensive group of data repositories that sought, over time, to relate specific environmental exposures to dioxin, trichloroethylene (TCE), benzene, and trichloroethane (TCA) to registrants' health conditions. Some parts of the NER were well conceived, whereas others were not. The most important design deficiency of the NER was its inability to adequately assess exposure. This was the key missing element and the Achilles heel of the NER program. At least three other important issues were never satisfactorily resolved in the design of the NER. They were unverified self-reporting, appropriate control groups, and the use of biomarkers. The many health effects that were observed to be in excess when compared with national norms might be explained by methodological differences in data analysis and reliance on self-reported nonverified data. Creating and maintaining a population-based chemical exposure registry is a more difficult challenge than creating and maintaining an outcome registry, such as a cancer registry.

Final report on the safety assessment of Trichloroethane.

Trichloroethane functions in cosmetics as a solvent. Although Trichloroethane has been reported to the Food and Drug Administration (FDA) to be used in cosmetic products, an industry survey found that it is not in current use in the cosmetic industry. Trichloroethane is considered a Class I ozone-depleting substance by the Environmental Protection Agency (EPA) and its use is prohibited in the United States, unless considered essential. The FDA has stated that Trichloroethane's use in cosmetics is considered nonessential. Trichloroethane is detected by gas chromatography, gas chromatography-mass spectrometry, and gas-liquid chromatography. In rats, Trichloroethane, whether inhaled or injected, is mostly expelled intact from the body through exhalation. A very small percentage is excreted in the urine. In humans, Trichloroethane is rapidly absorbed through the skin and eliminated in exhaled air and a very small percentage is excreted in urine. Inhaled Trichloroethane is eliminated in exhaled air. Acute oral LD(50) values have been reported as follows: 12.3 g/kg in male rats; 10.3 g/kg in female rats; 11.24 g/kg in female mice; 5.66 g/kg in female rabbits; and 9.47 g/kg in male guinea pigs. Acute toxicity studies using other routes of exposure, including subcutaneous injection and inhalation, produced no evidence of significant toxicity, except at very high exposure levels. Continuous inhalation exposure of rabbits to 750 mg/m(3) for 90 days did not produce any signs of toxicity. Continuous exposure of rats, guinea pigs, rabbits, and monkeys to 500 ppm Trichloroethane for 6 months did not produce any signs of toxicity. Other short-term and subchronic inhalation exposures confirmed acute and short-term exposure findings that the toxic effects of inhalation were a function of both concentration and time. Rats receiving 750 or 1500 mg/kg day(- 1) Trichloroethane in corn oil by oral gavage 5 days per week for 78 weeks had reduced body weights and early mortality. Reduced body weights, decreased survival rates, and early mortality (in females) were found in mice dosed with 3000 or 6000 mg/kg day(- 1) (over the last 58 weeks; lower doses were administered for the first 20 weeks). Mice exposed to prolonged periods of Trichloroethane in an inhalation chamber had increased motor activity at levels up to 5000 ppm. Further increase of concentration of exposure resulted in less of an increase of motor activity until motor activity began to fall below normal at 10,000 ppm. Adverse effects on motor activity in rats were seen at exposures as low as 3000 ppm for 4 h. Rabbits had slight reddening and scaling after 10 24-h applications to abdominal skin of Trichloroethane mixed with 2.4% to 3.0% dioxane, and slight to moderate erythema, slight edema, and slight exfoliation was observed when 75% Trichloroethane and 25% tetrachloroethylene were applied to rabbit ears for 11 days. Undiluted Trichloroethane applied to the clipped backs of guinea pigs produced histopathologic damage in the epidermis. A primary irritation index of 5.22 (out of 8) was reported in rabbits. Trichloroethane applied to the eyes of rabbits resulted in transient irritation and apparent pain, but no corneal damage. There was no effect on gestation, pup survival, or growth in mice given Trichloroethane in drinking water at up to 5.83 mg/ml during mating and/or gestation. Rats exhibited no or minimal effects of ingestion of Trichloroethane up to 30 ppm in drinking water during mating and/or gestation. There was no effect on gestation, pup survival, or growth in mice or rats inhaling 875 ppm Trichloroethane. However, prenatal exposure of rodents to Trichloroethane can produce developmental toxicity in the form of delayed development in the offspring. Trichloroethane has been found to be mutagenic in the Ames assay in some studies and not mutagenic in others. Trichloroethane induced transformations in Fischer rat embryo cell system at 99 mu M, was not mutagenic using the mouse lymphoma assay at up to 0.51 mu g/ml, was equivocal in that assay when tested with S9, and was also equivocal in a sister-chromatid exchange assay using Chinese hamster ovarian (CHO) cells with and without S9. Mice ingesting 80,000 ppm Trichloroethane in their drinking water had an increase in the frequency of micronucleated normochromatic erythrocytes. A peripheral blood micronucleus test in female mice was negative. Trichloroethane was not carcinogenic to rats when administered 1500 mg/kg by oral gavage 5 days/week for 78 weeks or in mice administered 6000 mg/kg. Exposure to 1500 ppm Trichloroethane vapor for 6 h/day, 5 days/week for 2 years likewise gave no indications of oncogenic effects in rats or mice. People who have been exposed to Trichloroethane have reported dizziness, lassitude, unconsciousness, respiratory depression, peripheral vascular collapse, impaired postural control, mild encephalopathy, perioral tingling, burning on the tongue and discomfort in the hands and feet. The Cosmetic Ingredient Review (CIR) Expert Panel recognizes that Trichloroethane (1,1,1-Trichloroethane) has been declared a Class I ozone-depleting substance by the EPA and its use is limited to essential products. The FDA has determined that use of Trichloroethane in aerosol cosmetic products is considered nonessential. At issue for this assessment is the safety of direct exposure to individuals as a result of exposure to cosmetic products that may contain Trichloroethane. The Expert Panel found the available data to be sufficient to support the safety of Trichloroethane as a solvent in cosmetic products.

Application of PBPK modeling in support of the derivation of toxicity reference values for 1,1,1-trichloroethane.

PBPK modeling has been increasingly applied in chemical risk assessment for dose, route, and species extrapolation. The use of PBPK modeling was explored in deriving toxicity reference values for 1,1,1-trichloroethane (1,1,1-TCE). This effort involved a 5-step process: (i) reconstruction of several published PBPK models for 1,1,1-TCE in the rat and human; (ii) selection of appropriate pharmacokinetic datasets for model comparison; (iii) determination of the most suitable PBPK model for supporting reference value derivation; (iv) PBPK model simulation of two critical studies to estimate internal dose metrics; and (v) calculation of internal dose metrics for human exposure scenarios for reference value derivation. The published model by Reitz et al. [Reitz, R.H., McDougal, J.N., Himmelstein, M.W., Nolan, R.J., Schumann, A.M., 1988. Physiologically based pharmacokinetic modeling with methylchloroform: implications for interspecies, high dose/low dose, and dose route extrapolations. Toxicol. Appl. Pharmacol. 95, 185-199] was judged the most suitable. This model has liver, fat, and rapidly and slowly perfused compartments, contains a saturable process for 1,1,1-TCE hepatic metabolism, and accommodates multiple exposure pathways in three species. Data from a human volunteer study involving acute inhalation exposure [Mackay, C.J., Campbell, L., Samuel, A.M., Alderman, K.J., Idzikowski, C., Wilson, H.K., Gompertz, D., 1987. Behavioral changes during exposure to 1,1,1-trichloroethane: time-course and relationship to blood solvent levels. Am. J. Ind. Med. 11, 223-239] and a chronic rat inhalation study [Quast, J.F., Calhoun, L.L., Frauson, L.E., 1988. 1,1,1-Trichloroethane formulation: a chronic inhalation toxicity and oncogenicity study in Fischer 344 rats and B6C3F1 mice. Fundam. Appl. Toxicol. 11, 611-625] were selected to simulate appropriate internal dosimetry data from which to derive reference value points of departure. Duration, route, and species extrapolations were performed based on internal dose metrics.

Comparative study of the effects of toluene, benzene, 1,1,1-trichloroethane, diethyl ether, and flurothyl on anxiety and nociception in mice.

The main purpose of this study was to compare the effects of solvents from different chemical classes on anxiety and nociception. Independent groups of mice were exposed to air (control group), toluene (1000-4000 ppm), benzene (1000-4000 ppm), 1,1,1-trichloroethane (TCE, 2000-12000 ppm), diethyl ether (10,000-30,000) or flurothyl (200-600 ppm). After a 30-min exposure, animals were tested either in the anxiety paradigm conditioned defensive burying (CDB) test or in the hot plate test. All solvents but flurothyl produced anxiolytic-like actions being the order of potency toluene > benzene > TCE > diethyl ether. When tested in the hot plate paradigm, toluene and TCE increased nociception, benzene and diethyl ether had no effects, and flurothyl decreased nociception Additional groups of mice were conditioned to recognize the aversive stimulus (electrified prod) prior to toluene exposure and then tested in the CDB test. In unconditioned animals, toluene increased the number of shocks that mice received; however, when mice had previous experience in the CDB test, toluene lacked this effect. Taken together, these results show that inhalants have different effects with different potencies both in the CDB and in the hot plate tests. Additionally, data suggest that acute administration of toluene could impair learning.

Developmental effects of intermittent prenatal exposure to 1,1,1-trichloroethane in the rat.

The effects of daily three 1-h exposures to 7000 ppm 1,1,1-trichloroethane (TCE) on physical and behavioral development were examined in Sprague-Dawley rats exposed during the last week of gestation. A sham group was exposed to filtered air. Offspring of both groups were fostered to untreated dams. No significant group differences were detected in total maternal weight gain or food and water consumption, but differences were observed in initial litter characteristics, including a longer gestation period in the TCE group, a smaller number of litters delivered in the TCE group, and fewer live pups per litter in the TCE group. At birth, the total litter weight was less in the TCE group, but there was no significant difference in average pup weight. Pups prenatally exposed to TCE did not differ from shams in day of eye opening, pinnae detachment, or incisor eruption. The TCE group weighed less the first 2 weeks of life, was impaired in its ability to perform the inverted screen, negative geotaxis, and vertical screen tests, and had less forelimb grip strength. Locomotor activity was reduced in the TCE group, and the ratio of brain to body weight was reduced in TCE-exposed offspring. These data provide evidence for neurobehavioral teratogenicity of intermittent prenatal exposure to high concentrations of TCE in rats.

Functional observational battery comparing effects of ethanol, 1,1,1-trichloroethane, ether, and flurothyl.

Several recent reports have demonstrated that acute solvent exposure in animals produces a profile of neurobehavioral effects similar to that of classical CNS depressant drugs such as the barbiturates and ethanol. The present investigation further delineated the behavioral pharmacology of three solvents [1,1,1-trichloroethane (TCE), ether, and flurothyl] using a functional observational battery (FOB) composed of 21 qualitative and quantitative measures of behavior. The profiles of acute effects produced by TCE and ether were similar to one another and similar to the profile of effects produced by the IP administration of ethanol. This profile of depressant effects included changes in posture, decreased arousal, disturbances in gait, decreased forelimb grip strength, increased landing foot splay, and impaired psychomotor coordination. Flurothyl exposure also produced dose-related effects on many of the measures in the FOB; however, unlike the depressant vapors, flurothyl did not affect measures of muscle tone and equilibrium such as forelimb grip strength and landing foot splay, or measures of sensorimotor reactivity, including the touch response and tail pinch response. In addition, flurothyl produced handling-induced convulsions in some mice. Recovery from the acute effects of these vapors was rapid and began within minutes of removal from the exposure chamber. These results provide further evidence that exposure to certain solvents produces a profile of reversible effects qualitatively similar to that produced by depressant drugs and alcohol, and that the FOB can be used to compare and contrast profiles of depressant and excitatory effects of inhalants.

Evaluation of the Allium anaphase-telophase test in relation to genotoxicity screening of industrial wastewater.

The Allium anaphase-telophase test was evaluated to find out if it could be recommended in the screening of wastewater for genotoxicity. Five mutagenic or carcinogenic chemicals usually found in wastewater were tested in the Allium anaphase-telophase test. Sodium dichromate (25 microM), benzene (100 microM), dichloromethane (175 microM) and 1,1,1-trichloromethane (175 microM) increased the frequency of chromosome aberrations in the root cells, whereas formaldehyde (1 mM) was found to be non-mutagenic in this test system. Other studies where chemicals were tested in the Allium test were reviewed. For 15 chemicals the results were compared with results from the Ames test, the Microscreen assay, and carcinogenicity tests in rodents. The sensitivity of the Allium test was calculated to be 82%. In conclusion the Allium test is recommended for the screening of wastewater because it has a high sensitivity, is cheap, rapid, easy to handle, and because it can be used on wastewater without pretreatment of the sample.

1,1,1 - Tricloroetano, tricloroetileno, percloroetileno: aspectos toxicológicos / 1,1,1 - Trichloroethane, thichloroethylene, perchloroethylene: toxicologycal aspects

Säo solventes de ampla utilizaçäo industrial empregados, principalmente, nas operaçöes de desengraxamento de peças metálicas. O desenvolvimento significativo das indústrias mecânicas brasileiras sugere a larga utilizaçäo desses agentes e, consequentemente, um grande número de indivíduos expostos, sendo a exposiçäo ocupacional a principal causa de intoxicaçäo. Nesta revisäo objetivou-se apresentar as propriedades físico-químicas destas substâncias, as condiçöes que afetam suas biodisponibilidades químicas e seus efeitos tóxicos, conhecimentos necessários para a implantaçäo de um programa adequado de monitorizaçäo biológica.

Potentiating effects of chlorinated hydrocarbons on carbon tetrachloride toxicity in isolated rat hepatocytes and plasma membranes.

A number of chemicals are known to potentiate the hepatotoxicity of carbon tetrachloride. The halocarbon trichloroethylene was shown in a previous study to enhance both carbon tetrachloride-induced toxicity and lipid peroxidation in isolated hepatocytes. In this study three other chlorocarbons have been investigated in order to determine whether this interaction was peculiar to trichloroethylene or common to chlorinated solvents. Hepatocyte suspensions were exposed to carbon tetrachloride at subthreshold levels of toxicity and various concentrations of 1,1,1-trichloroethane, tetrachloroethylene, and chloroform over an eightfold concentration range. Plasma membrane preparations were exposed to tetrachloroethylene and carbon tetrachloride and effects on Mg(2+)- and Na(+)-K(+)-ATPase activities determined. None of the treatments alone caused statistically significant toxicity. Combined treatments resulted in toxicity as demonstrated by potassium ion, alanine aminotransferase, and lactate dehydrogenase leakage from the cells on coincubation of carbon tetrachloride with each of the other halocarbons studied. Only tetrachloroethylene and chloroform were found to potentiate lipid peroxidation, however. In liver plasma membranes no changes in Na(+)-K(+)-ATPase were observed with any of the treatments and only the highest dose of tetrachloroethylene was able to inhibit Mg(2+)-ATPase activity. There was no increase in this inhibition on coincubation with carbon tetrachloride, which does not support involvement of ATPases in combined halocarbon toxicity. In conclusion, the data suggest a mechanism of action common to this class of chemical although its specific nature remains to be established.

Health risk assessment of environmental exposure to 1,1,1-trichloroethane.

In 1986 a survey was published by CEFIC on the occurrence of chlorinated solvents in ambient air, in surface water, and in ground water. The present article concentrates on 1,1,1-trichloroethane (1,1,1-T), and puts into perspective the environmental occurrence and the toxicity. Critical toxicological data are briefly discussed. As no evidence of a carcinogenic effect of 1,1,1-T is apparent, the no-adverse-effect levels in chronic inhalation exposure in rats (875 ppm) and mice (1500 ppm) form the basis for the estimation of potential risk to human health. Environmental exposure to 1,1,1-T is mainly via the atmosphere (120 micrograms/day); the contributions of drinking water (2 micrograms/day) and food (3 micrograms/kg) are negligible. Safety margins are calculated by comparing the no-adverse-effect levels in rat and mouse studies with the total body burden. Safety margins are also calculated after converting no-adverse-effect levels into estimated internal dose levels by physiologically based pharmacokinetic modeling. Safety margins vary with the starting point, but are of the order of 10(5) for the general population and more than 10(4) for the population close to industrial activities. It may be concluded that the risk of a potential health effect resulting from environmental exposure to 1,1,1-trichloroethane is negligible.

1,1,1-trichloroethane formulation: a chronic inhalation toxicity and oncogenicity study in Fischer 344 rats and B6c3F1 mice.

Groups of male and female Fischer 344 rats and B6C3F1 mice (80/sex/group) were exposed to vapor concentrations of 0, 150, 500, or 1500 ppm 1,1,1-trichloroethane formulation 6 hr/day, 5 days/week, for 2 years. Ten rats and mice/sex from each group were predesignated for interim sacrifices after 6, 12, and 18 months of exposure. Fifty rats and mice/sex/group were assigned to the study to be terminated after 24 months. Parameters measured during the study included mortality, in-life clinical signs of toxicity, hematology, urinalysis (rats only), clinical chemistry, body weight, organ weights (liver, kidneys, brain, heart, testes), gross pathology, and histopathology. Inhalation exposure of male and female Fischer 344 rats to 1500 ppm vapor of the 1,1,1-trichloroethane formulation for 2 years resulted in a significant decrease in body weights of females. In addition, very slight microscopic hepatic effects were seen in the liver of 1500 ppm-exposed male and female rats necropsied at 6, 12, and 18 months. The hepatic effects could not be discerned at 24 months due to confounding geriatric changes. In the rats exposed to 150 and 500 ppm there were no changes that were considered due to exposure to the 1,1,1-trichloroethane formulation. There were no toxic effects noted in male or female mice at any exposure concentration tested. There were no indications of an oncogenic effect in rats or mice following 2 years of exposure to this 1,1,1-trichloroethane formulation.

Rat liver foci and in vitro assays to detect initiating and promoting effects of chlorinated ethanes and ethylenes.

Nine chlorinated aliphatics (CAs) were examined in a rat liver foci assay for tumor initiating and promoting activities. In this model, young adult male Osborne Mendel rats were first subjected to a partial hepatectomy, the test chemical was then administered at the maximum tolerated dose in the initiation or promotion phase in conjunction with diethylnitrosamine (DEN; 30 mg/kg b.w.) or phenobarbital (PB; 0.05 percent, w/w, in the diet), and gamma glutamyltranspeptidase (GGT) was used as a putative preneoplastic indicator. When administered in the promotion protocol after initiation with DEN, 1,1-dichloroethane, 1,1,2-trichloroethane (1,1,2-TCE), 1,1,2,2-tetrachloroethane (1,1,2,2-TTCE), tetrachloroethylene (TTCY), and hexachloroethane induced significant increases in GGT+-foci above control levels. 1,1,2,2-TTCE, TTCY, and 1,1,2-TCE also induced significant increases in GGT+-foci when administered in the promotion protocol without DEN initiation. Two variants of GGT+-foci were observed: the classical type associated with PB promotion, and the other, which was more diffuse, less intensely stained, resembling foci undergoing redifferentiation and associated with CAs. A number of CAs were also genotoxic in short-term in vitro tests. Taken together, the studies suggest that CAs may be complete carcinogens in vivo with weak initiating activity and stronger promoting activity.

Investigations on metabolism and carcinogenicity of 1,1,2-trichloroethane.

Two groups of male and female Sprague-Dawley rats (50 animals/group per sex) were treated with either 15.37 or 46.77 mumole of 1,1,2-TCE in DMSO/rat for 2 years. The animals were treated once a week by s.c. injection of test compound in the skin of neck. Two groups of controls received either DMSO or no treatment at all. The incidence of benign mesenchymal and epithelial tumors was not significant when compared with either DMSO-treated or untreated controls. The animals treated with 46.77 mumole 1,1,2-TCE significantly developed sarcomas when compared with the untreated controls. In a further experiment, either 40 mumole or 160 mumole 1,1,2-TCE was injected into male Wistar rats and the metabolites, TdGA and HEMA, were determined in 24-h urine samples. Comparative studies were carried out giving equimolar amounts of chloroethanol and 2-chloroacetaldehyde diethyl acetal. Analysis of the metabolites showed that no detectable HEMA was excreted in urine after treatment of rats with 1,1,2-TCE or chloroethanol. TdGA was excreted in urine much more among chloroacetaldehyde-treated animals than among 1,1,2-TCE- or chloroethanol-treated rats.