Developmental toxicity of dimethylacetamide in rabbits following inhalation exposure

(1) Dimethylacetamide was tested for developmental toxicity after inhalation exposure of pregnant Himalayan rabbits. Fifteen female rabbits per main group were exposed to dimethylacetamide vapours at concentrations of 0, 0.2, 0.7 or 2.0 mg/l (equivalent to 0, 57, 199.5 or 570 ppm) and five female rabbits per satellite group to 0 or 2.0 mg/l 6 h/day from day 7 post-insemination (p.i.) to day 19 p.i. All animals were observed until day 29 p.i. (2) No signs of maternal toxicity were seen in the does of the main groups (body weight and gross pathology) or in the does of the satellite groups (body weight, blood chemistry, histopathological findings of the liver). (3) Fetotoxic effects were caused at a concentration of 0.7 mg/l (e.g., increased skeletal variations) and 2.0 mg/l (e.g., significantly decreased fetal and placental weights, increase in soft tissue and skeletal variations). At 2.0 mg/l, there were also signs of a weak teratogenic effect expressed as a marginal, statistically not significant increase in soft tissue malformations (regarding the heart and great vessels). No compound-related effects were observed in the fetuses after exposure to 0.2 mg/l. (4) The highest concentration tested under these conditions (2.0 mg/l) was found to be a no-observable-adverse-effect-level (NOAEL) for the maternal Himalayan rabbit, whereas 0.2 mg/l was defined as the NOAEL for the developing organism.     

Developmental toxicity of N-methyl-2-pyrrolidone in rats following inhalation exposure.

The developmental toxicity of inhaled N-methyl-2-pyrrolidone (NMP) was studied in Sprague-Dawley rats. Pregnant rats were exposed whole body to NMP vapours at concentrations of 0, 30, 60 and 120 ppm, 6 h/day, on gestational days (GD) 6 through 20. Maternal body weight gain was significantly decreased at 60 and 120 ppm on GD 6-13 and maternal food consumption was reduced at 120 ppm on GD 13-21. No significant difference in the gestational weight change corrected for the weight of the gravid uterus was observed, whatever NMP concentration. There were no adverse effects on embryo/fetal viability or evidence of teratogenicity at any concentration tested. Fetal toxicity indicated by reduced fetal weight was observed at 120 ppm. Thus, the no-observed-adverse-effect level (NOAEL) for maternal and developmental toxicity was 30 and 60 ppm, respectively.     

Acute toxicity in the rat following either oral or inhalation exposure

A survey of 108 chemicals was conducted to determine the relationship between acute oral and acute inhalation toxicity data in the rat. LD50 or LC50 values were compared after classification of each chemical in terms of relative toxicity. A positive correlation (0.53, P less than 0.001) between the classification of toxicity for the oral and inhalation routes was determined. However, the magnitude of this correlation was such that the predictive value of one for the other was limited. For a complete acute toxicity profile, it does not appear as if the determination of acute toxicity by one of those routes would yield a reliable estimate of toxicity by the other route.     

Developmental toxicity of two trimethylbenzene isomers, mesitylene and pseudocumene, in rats following inhalation exposure.

The developmental toxicity of two trimethylbenzene isomers, mesitylene (1,3,5-trimethylbenzene) and pseudocumene (1,2,4-trimethylbenzene) was studied in Sprague-Dawley rats following inhalation exposure. Pregnant rats were exposed whole body to vapours of mesitylene (0, 100, 300, 600, and 1200 ppm) or pseudocumene (0, 100, 300, 600, and 900 ppm), 6h/day, on gestational days (GD) 6 through 20. Significant decrease in maternal body weight gain and food consumption was observed at concentrations of 300 ppm mesitylene, 600 ppm pseudocumene, or greater. Fetal toxicity, expressed as significant reduction in fetal body weight, occurred at 600 and 1200 ppm mesitylene, and at 600 and 900 ppm pseudocumene. There was no evidence of embryolethal or teratogenic effects following inhalation exposure to either of these chemicals. In summary, the no-observed-adverse-effect-level (NOAEL) for maternal toxicity was 100 ppm for mesitylene and 300 ppm for pseudocumene, and the NOAEL for developmental toxicity was 300 ppm for mesitylene and pseudocumene.     

Subchronic inhalation toxicity of dimethylformamide in rats and mice

Fisher F344 rats and B6C3F1 mice were exposed to concentrations of 0, 150, 300, 600 and 1200 ppm of dimethylformamide (DMF) for 6 hours a day, 5 days a week for 12 weeks. Detailed clinical observations were obtained weekly and body weights biweekly on all animals. Clinical chemistry and hematology evaluations were made on all rats and approximately half the mice at terminal sacrifice. Gross necropsy examinations were made on all animals. Histopathologic evaluations were conducted on selected tissues of animals of both species at all dose levels. Few overt signs of toxicity were seen in either rats or mice. There was a dose related depression in body weight gain in rats that was significant at the 1200 ppm level from the second week of study onwards. A total of 11 mice died or were sacrificed moribund during the study, 8 from the high dose and 2 from the 600 ppm dose level. Both clinical chemistry (in rats only) and gross necropsy observations, and histopathology of tissues indicate the possibility that liver may be the target in specific organ toxicity. The no-effect DMF dose was below the 150 ppm level for both rats and mice and the maximum tolerated dose was below the 600 ppm level.     

Teratogenic evaluation of mancozeb in the rat following inhalation exposure

Crl:CD rats were exposed (whole body) to mancozeb by inhalation at 0, 1, 17, 55, 110, 890, or 1890/500 mg/m3 for 6 hr/day from Day 6 through 15 of gestation (sperm-positive vaginal smear considered Day 1). Dams were killed 1 day prior to natural delivery and fetuses were examined externally, viscerally, and skeletally for any alterations. Maternal toxicity, as evidenced by significantly decreased body weight gain, hindlimb paralysis, general debilitation, and death or termination in extremis, was noted among rats exposed to mancozeb at concentrations of 500 to 1890 mg/m3. Dams from the 55 and 110 mg/m3 groups exhibited decreased body weight gain and hindlimb weakness. There was no maternal toxicity for dams exposed at a concentration of 17 mg/m3. Embryofetal toxicity, as evidenced by a significantly increased incidence of totally resorbed litters, external hemorrhage, and wavy ribs, was noted at concentrations of 55 mg/m3 and above. The embryofetal toxicity occurred only at concentrations toxic to the dam. Among the groups exposed to mancozeb, the incidence of major malformations was not dose related. Hence, under the test conditions of this study, mancozeb was not found to be teratogenic and produced no toxicity unique to the conceptus.     

The toxicity of microcystin LR in mice following 7 days of inhalation exposure.

Microcystins, a family of cyclic heptapeptides produced by the cyanobacteria, Microcystis aeruginosa, have documented hepatotoxic and tumor promoting activities. The purpose of this study was to evaluate the toxicity of inhaled microcystin LR (microcystin). Male BALB/c mice were exposed by nose-only inhalation to 260-265 microg microcystin/m(3) for 7 days. The low-, mid- and high-dose groups were exposed for 0.5, 1, and 2h, respectively. Control animals were sham exposed to aerosolized vehicle. Treatment-related microscopic lesions were observed only in the nasal cavity of the mid- and high-dose groups. These lesions consisted of minimal to moderate multifocal degeneration and necrosis of the respiratory epithelium, with variable neutrophilic inflammation and minimal to marked degeneration, necrosis, and atrophy of the olfactory epithelium. The no-adverse-effect dose for the nasal lesions was approximately 3 microg/kg body weight, or 20 ng/cm(2) of nasal epithelium. In serum, only two protein peaks, occurring at m/zs of 11,688 and 11,829 Da, exhibited decreases in intensity that were microcystin dose-dependent. While these proteins have not been positively identified, they may be useful in the future as biomarkers of microcystin exposure in humans.     

Acute respiratory toxicity following inhalation exposure to soman in guinea pigs

Respiratory toxicity and lung injury following inhalation exposure to chemical warfare nerve agent soman was examined in guinea pigs without therapeutics to improve survival. A microinstillation inhalation exposure technique that aerosolizes the agent in the trachea was used to administer soman to anesthetized age and weight matched male guinea pigs. Animals were exposed to 280, 561, 841, and 1121 mg/m³ concentrations of soman for 4 min. Survival data showed that all saline controls and animals exposed to 280 and 561 mg/m³ soman survived, while animals exposed to 841, and 1121 mg/m³ resulted in 38% and 13% survival, respectively. The microinstillation inhalation exposure LCt₅₀ for soman determined by probit analysis was 827.2 mg/m³. A majority of the animals that died at 1121 mg/m³ developed seizures and died within 15-30 min post-exposure. There was a dose-dependent decrease in pulse rate and blood oxygen saturation of animals exposed to soman at 5-6.5 min post-exposure. Body weight loss increased with the dose of soman exposure. Bronchoalveolar lavage (BAL) fluid and blood acetylcholinesterase and butyrylcholinesterase activity was inhibited dose-dependently in soman treated groups at 24 h. BAL cells showed a dose-dependent increase in cell death and total cell counts following soman exposure. Edema by wet/dry weight ratio of the accessory lung lobe and trachea was increased slightly in soman exposed animals. An increase in total bronchoalveolar lavage fluid protein was observed in soman exposed animals at all doses. Differential cell counts of BAL and blood showed an increase in total lymphocyte counts and percentage of neutrophils. These results indicate that microinstillation inhalation exposure to soman causes respiratory toxicity and acute lung injury in guinea pigs.     

Developmental neurotoxicity after toluene inhalation exposure in rats.

Rats were exposed to 1200 ppm or 0 ppm toluene (CAS 108-88-3) for 6 h per day from day 7 of pregnancy until day 18 postnatally. Developmental and neurobehavioral effects in the offspring were investigated using a test battery including assessment of functions similar to those in the proposed OECD TG for Developmental Neurotoxicity Study, i.e., physical development, reflex ontogeny, motor function, motor activity, sensory function, and learning and memory. The exposure did not cause maternal toxicity or decreased viability of the offspring. Lower birth weight, delayed ontogeny of reflexes, and increased motor activity in the open field was registered in the exposed offspring. Impaired cognitive function was revealed in the exposed female offspring at the age of 3.5 months, i.e., they used more time to locate the hidden platform in the Morris water maze after platform relocation. The difference was not related to poorer swimming capabilities, because swim speeds were similar to control values. The results show that exposure to 1200 ppm toluene during brain development caused long-lasting developmental neurotoxicity in rats.     

Assessments of lung toxicity to Acrawax C following acute inhalation exposure

Acrawax is a trademark for a series of synthetic waxes which are used as flatteners in paint, and lubricants in plastics, and these materials have been routinely regarded as nuisance dusts. Due to a paucity of information regarding the pulmonary toxicity of this material, we investigated the effects of acute inhalation of Acrawax C in rats. CD rats were exposed to aerosols of Acrawax C for 6 hours at 112 mg/m3. Fluids and cells from sham and exposed animals were recovered by bronchoalveolar lavage (BAL) and measured for cellular and biochemical parameters at 0, 24, 48, 172 hrs (8 days), and 1 month postexposure. Pulmonary macrophages (PM) were cultured and studied for in vitro and in vivo phagocytosis, as well as surface morphology. The lungs of additional animals exposed to Acrawax were fixed for assessment by histopathology, and transmission electron microscopy. Our results showed that Acrawax C exposure produced a mild inflammatory response at 24 hours postexposure, but cell differentials were not significantly different from controls at 48 hrs after exposure. BAL levels of lactate dehydrogenase, alkaline phosphatase and protein were slightly different from controls only at 8 days postexposure, and had returned to control values by 1 month of recovery. Acrawax exposure had no adverse effects on either morphology or the phagocytic capacity of pulmonary macrophages recovered from exposed animals. Histopathologic analysis of lung tissue from Acrawax C-exposed rats revealed normal lung architecture. Based on acute studies, our results suggest that the response to inhaled Acrawax C is not substantially different from the response to other nuisance dusts such as carbonyl iron and titanium dioxide.     

Developmental toxicity in rats after inhalation exposure of di-2-ethylhexylphthalate (DEHP)

Di-2-ethylhexylphthalate (DEHP) was investigated in Wistar rats for developmental toxicity after head-nose exposure to aerosol concentrations of 0, 0.01, 0.05 and 0.3 mg/l for 6 h per day from gestation day 6 through 15. A range finding study revealed peroxisome proliferation in the liver of the dams throughout exposure levels of 0.2, 0.5 and 1.0 mg/l with an increasing trend. 0.3 mg/l was therefore regarded as an exposure level leading to peroxisome proliferation as a marker for maternal effects. All concentrations were tolerated without clinical signs of maternal toxicity. The fetuses of 20 animals per exposure group were investigated for structural defects. Five additional animals per group were allowed to litter and the offsprings were raised and observed for postnatal signs of toxicity. No significant developmental toxicity or changes in the postnatal physical development were observed. DEHP is assumed not to exhibit developmental toxicity under the experimental conditions employed.     

Acute pulmonary toxicity following inhalation exposure to aerosolized VX in anesthetized rats

ABSTRACT

This study evaluated acute toxicity and pulmonary injury in rats at 3, 6 and 24?h after an inhalation exposure to aerosolized O-ethyl S-[2-(diisopropylamino)ethyl] methylphosphonothioate (VX). Anesthetized male Sprague-Dawley rats (250–300?g) were incubated with a glass endotracheal tube and exposed to saline or VX (171, 343 and 514?mg×min/m³ or 0.2, 0.5 and 0.8?LCt₅₀, respectively) for 10?min. VX was delivered by a small animal ventilator at a volume of 2.5?ml?×?70 breaths/minute. All VX-exposed animals experienced a significant loss in percentage body weight at 3, 6, and 24?h post-exposure. In comparison to controls, animals exposed to 514?mg×min/m³ of VX had significant increases in bronchoalveolar lavage (BAL) protein concentrations at 6 and 24?h post-exposure. Blood acetylcholinesterase (AChE) activity was inhibited dose dependently at each of the times points for all VX-exposed groups. AChE activity in lung homogenates was significantly inhibited in all VX-exposed groups at each time point. All VX-exposed animals assessed at 20 min and 3, 6 and 24?h post-exposure showed increases in lung resistance, which was prominent at 20 min and 3?h post-exposure. Histopathologic evaluation of lung tissue of the 514?mg×min/m³ VX-exposed animals at 3, 6 and 24?h indicated morphological changes, including perivascular inflammation, alveolar exudate and histiocytosis, alveolar septal inflammation and edema, alveolar epithelial necrosis, and bronchiolar inflammatory infiltrates, in comparison to controls. These results suggest that aerosolization of the highly toxic, persistent chemical warfare nerve agent VX results in acute pulmonary toxicity and lung injury in rats.     

Teratogenic evaluation of 1,4-dichlorobutene-2 in the rat following inhalation exposure

The teratogenic potential of 1,4-dichlorobutene-2 (1,4-DCB) was evaluated in the rat. From inhalation toxicity studies, particularly ongoing lifetime studies, exposure levels of 0, 0.5, and 5.0 ppm were selected. Rats were exposed for 6 hr per day on Days 6 through 15 of gestation (sperm-positive vaginal smear considered Day 1). Female rats were killed 1 day prior to natural delivery and fetuses were examined for external development, structure and integrity of internal tissues and organs, and skeletal development. The only clinical sign of toxicity observed among rats exposed to 1,4-DCB, was a significantly-reduced rate of weight gain seen at the 5.0-ppm level. 1,4-DCB exposure did not change either the number of pregnant rats or the number of implantation sites, resorption sites, and fetuses per female. Treatment did not affect embryonal development as measured by fetal weight and crown-rump length, or by gross external, visceral, and skeletal examination of the fetuses. Under the test conditions of this study, 1,4-DCB was neither embryotoxic nor teratogenic.     

An inhalation toxicity study of chlorine in Fischer 344 rats following 30 days of exposure.

A subacute study was completed in groups of 10 male and 10 female Fischer 344 rats exposed to air (controls), 1, 3, or 9 ppm chlorine for 6 hr/day, 5 days/week, for 6 weeks. Concentration related decreases in body weight gain were seen at all exposure concentrations in females and at 3 and 9 ppm in males. Additionally, three females at 9 ppm died before the end of Day 30 of exposure. Urinalysis, hematology, and clinical chemistry evaluations were completed on the surviving animals. The urine specific gravity was elevated at all exposure concentrations in the females and at 3 and 9 ppm in the males. The hematocrit and white blood cell count were increased in the females exposed to 9 ppm. Elevations in alkaline phosphatase activity, blood urea nitrogen, γ-glutamyl transpeptidase, and serum glutamic-pyruvic transaminase occurred at 9 ppm; alkaline phosphatase was elevated at 3 ppm in rats of both sexes. Widespread evidence of inflammation was seen throughout the respiratory tract with hyperplasia and hypertrophy of epithelial cells of the respiratory bronchioles, alveolar ducts, and alveoli of male and female rats exposed to 9 ppm. Changes in male rats at 3 or 1 ppm consisted of focal inflammation of the nasal turbinates and a slight to moderate inflammatory reaction around the respiratory bronchioles and alveolar ducts. Increased eosinophilic cytoplasmic homogeneity and decreased granularity of the epithelial cells of the proximal convoluted tubules were seen in the kidneys of male rats exposed to 9 ppm. The livers of rats of both sexes at 9 or 3 ppm had an increased hepato-cellular cytoplasmic vacuolation. These data indicated that repeated exposure of Fischer 344 rats to chlorine resulted in pulmonary effects at all levels of chlorine used, and hepatic and renal effects at 9 and 3 ppm.     

Developmental and reproductive toxicity evaluation of toluene vapor in the rat II. Developmental toxicity

The developmental toxicity of toluene was evaluated via whole body inhalation exposure, in pregnant Sprague Dawley rats exposed to toluene (99.9% pure) from gestation day (GD) 6–15 inclusive, 6 h/day, at concentrations of 0, 250, 750, 1500 and 3000 ppm (0, 938, 2812, 5625 and 11250 mg/m³). Doses were selected from a preliminary study performed over a range of concentrations from 0 to 5000 ppm, in which maternal and fetal toxicity were observed at 2000 ppm and above. This study has been cited in various regulatory documents and is presented here to allow greater accessibility to results and conclusions.

Toluene induced clinical signs in pregnant dams (ataxia, hyper-responsivity, increased water intake, decreased food consumption) at 3000 ppm, ataxia and hyper-responsivity at 1500 ppm, and reduced maternal body weight gain at 1500 during the exposure period only and at 3000 ppm from initiation of exposure to GD20. At Caesarean section on GD20, no adverse effects on implantation, number and viability of fetuses, or fetal sex distribution were observed. Litter weight and mean fetal weight was reduced at 3000 ppm and mean fetal weight was reduced at 1500 ppm. Instances of reduced or unossified skeletal elements occurred at the same dose levels. Mean fetal weight was also reduced at 250 ppm but not at 750 ppm. Extensive statistical analysis of fetal body weight data support the conclusion that there is no toxicologically significant dose-related effect on fetal body weight at or below 750 ppm. Low incidences (≤2.5%) of various malformations occurred in the 250, 1500, and 3000 ppm groups; there was no increase in the incidence of specific or total malformations with increased exposure and thus these were not attributed to toluene.

In this Toluene study, the maternal toxicity NOAEL was 750 ppm with a defined maternal and developmental toxicity LOAEL of 1500 ppm.     

Developmental toxicity but no immunotoxicity in the rat after prenatal exposure to diethylstilbestrol

Studies with dioxins and PCB's have shown that the developing immune system may be especially vulnerable to xenobiotics during the perinatal period. However, current guidelines for reproductive toxicity testing do not include immune parameters. In the present study, we have explored the usefulness of including immune parameters within the prenatal developmental toxicity study in rats, using the treatment protocol as described in the OECD 414 developmental toxicity test guideline. In addition, the experimental protocol was enhanced by including ten dose groups to facilitate dose-response analysis. Diethylstilbestrol (DES) was used as the model compound, as it is known to be toxic both for embryofetal development and for the immune system. The results show developmental toxicity in terms of decreased fetal survival and decreased pup body weight in the presence of reduced maternal food consumption and reduced body weight gain. However, immune parameters, including histopathology, hematology, and antibody responses to sheep red blood cells (SRBC) in pups at 4 weeks of age were uncompromised. It is speculated that rather than the prenatal exposure protocol used here, the generation study design with both pre- and postnatal exposure may be preferable as a general screen to detect developmental immunotoxic injury after xenobiotic exposure.     

Distribution to the fetus and major organs of the rat following inhalation exposure to pyrene.

Concentrations of pyrene and total metabolites were determined for individual fetuses and selected maternal organs and tissues immediately and 6 h following a 95-min head-only exposure of pregnant Wistar rats, on gestation day 17, to five levels of pyrene over the range 200-800 mg m-3 as a microcondensation aerosol. The influence of uterine horn, side and position, on distribution to the fetus was assessed. The concentration of both pyrene and its metabolites increased more over the exposure range (eightfold) than did those in the fetus. Concentrations of pyrene or its metabolites in fetal tissues were not found to be related to its position on the uterine horn. There was an unexplained and significant (P less than 0.01) higher concentration of pyrene in fetuses on the right side relative to the left side of the uterine horn for the animals killed immediately following exposure. A comparison of the levels in maternal tissues measured immediately following the exposure and 6 h later showed that there was some redistribution of pyrene and its metabolites to the fat tissues, i.e. levels in the fat increased over the 6 h period following the exposure. Levels in the other tissues diminished during this period. In general, concentrations of pyrene and its metabolites were lowest in the fetal tissues relative to those in the sampled maternal organs and tissues.     

Developmental toxicity of cobalt in the rat

To determine the potential developmental toxicity of cobalt, pregnant Sprague-Dawley rats were given by gavage a daily dose of 0, 25, 50; and 100 mg/kg cobalt(II) chloride on d 6-15 of gestation. Females were sacrificed on d 20. Maternal effects included significant reductions in weight gain and food consumption, particularly at 100 mk/kg.d. Hematocrit, hemoglobin concentration, mean corpuscular volume, mean corpuscular hemoglobin, and reticulocytes were increased significantly in the 100-mg/kg.d group. No treatment-related changes were recorded in the number of corpora lutea, total implants, resorptions, the number of live and dead fetuses, fetal size parameters, or fetal sex distribution data. Increased incidence of stunted fetuses per litter was the only adverse finding at 50 and 100 mg/kg.d group. However, this increase was not statistically significant. Examination of fetuses for gross external abnormalities, skeletal malformations, or ossification variations revealed that cobalt did not produce teratogenicity or significant fetotoxicity in the rat at doses as high as 100 mg/kg.d.     

Benzene disposition in the rat after exposure by inhalation.

Little information is available on benzene disposition after exposure by inhalation despite the importance of this route in man. Benzene metabolites as a group have been measured in bone marrow, but quantitation of individual metabolites in this target tissue has not been reported. Male Fischer-344 rats were exposed to 500 ppm benzene in air and the uptake and elimination was followed in several tissues. Concentrations of free phenol, catechol, and hydroquinone in blood and bone marrow were also measured. Steady-state concentrations of benzene (11.5, 37.0, and 164.0 μg/g in blood, bone marrow, and fat, respectively) were achieved within 6 hr in all tissues studied. Benzene half-lives during the first 9 hr were similar in all tissues (0.8 hr). A plot of amount of benzene remaining to be excreted in the expired air was biphasic with $\text{t}\text{1}\text{2}$ values for the α and β phases of 0.7 and 13.1 hr, respectively. Phenol was the main metabolite in bone marrow at early times (peak concentration, 19.4 μg/g). Catechol and hydroquinone predominated later (peak concentrations, 13.0 and 70.4 μg/g, respectively). Concentrations of these two metabolites declined very slowly during the first 9 hr. These data indicate that free catechol and hydroquinone persist in bone marrow longer than benzene or free phenol.     

Developmental toxicities of ethylbenzene, ortho-, meta-, para-xylene and technical xylene in rats following inhalation exposure.

The developmental toxicities of ethylbenzene, o-, m-, p-xylene and technical xylene were studied in Sprague-Dawley rats after inhalation exposure. Animals were exposed to either of these agents at 100, 500, 1000 or 2000 ppm, for 6 h/day, during days 6-20 of gestation. All the agents tested caused maternal toxicity expressed as a reduction in maternal body weight gain at 1000 and 2000 ppm. Decreased corrected weight gain and food consumption were observed at 1000 and 2000 ppm ethylbenzene, o-, m- or p-xylene, and at 2000 ppm technical xylene. No evidence of teratogenic effects was found after exposure to any of these agents up to 2000 ppm. Fetal toxicity evidenced by significant decreases in fetal body weights occurred at concentrations of 500 ppm or greater of o-xylene or technical xylene, and 1000 ppm or greater of ethylbenzene, m- or p-xylene. A significant increase in the mean percentage of fetuses per litter with skeletal variations was also noted at 2000 ppm ethylbenzene, o- and p-xylene. In summary, all tested agents produced developmental toxicity at 1000 and 2000 ppm, concentrations that also produced significant maternal toxicity. With o-xylene and technical xylene, developmental toxicity also occurred at 500 ppm, in the absence of maternal toxic effects. However, the only indication of a treatment-related effect was a slight decrease in fetal weight.