Overview of a system for the computer-assisted operation of a small animal inhalation facility.

Automatic monitoring of the concentration of test gases and other environmental variables in small animal inhalation exposure chambers, coupled with computing capability and feedback control of the concentration of test gas, allows almost fully automatic operation of the chambers with a minimal amount of human intervention. Time-varying exposure profiles may be generated repeatedly with great accuracy, thus allowing a more realistic simulation of real-life exposures than is approached by operating chambers manually at ostensibly constant concentrations of test gases. Carefully conducted, pre-experimental calibration procedures are performed, and daily calibration checks allow statistical control of daily chamber operation and longer term quality control. At the conclusion of each experiment the investigator is supplied with records that document chamber conditions that have been monitored throughout the entire experiment, with estimates of the accuracy that was achieved in creating the specified exposure profile. A purpose of this report is to help to bridge the gap between the practicing inhalation toxicologist and the engineer in order to encourage their cooperation and mutual understanding of the technical problems involved in developing computer-assistance packages for inhalation facilities.

Calibration of a system for the computer-assisted operation of a small animal inhalation facility.

The initialization of chambers in the computer-assisted inhalation facility at the National Institute of Environmental Health Sciences (1) includes a series of operations that we call "characterization." Characterization consists of two parts, the first of which is one of the topics of this report. In the first part of the characterization the mathematical relationship between the concentration of the chemical of interest and the output of the analyzer is approximated. This amounts to establishing a standard against which subsequent, daily calibrations can be compared. The second part of the characterization represents a wholly automatic operation in which certain dynamic characteristics of the system are quantified. A daily calibration is performed at the beginning of each day of chamber operation after the system has been characterized. The daily calibration data are checked against the characterization standard. The conversion equation for the daily operation of the chamber is derived from the daily calibration data combined with the characterization data. An equation that converts the output of the analyzer to units of concentration of the chemical of interest is at the heart of the computer-assisted monitoring and control system for our inhalation facility. The equation is derived from a calibration procedure that is conducted prior to starting each day's chamber operation. Quality control requires that, in addition to having a daily calibration of the system, a standard of reference be available against which each day's calibration data can be checked. This practice provides protection against the introduction of spurious calibration data on a daily basis, as well as providing a means for the detection of longer term drift.(ABSTRACT TRUNCATED AT 250 WORDS)

PBPK modeling/Monte Carlo simulation of methylene chloride kinetic changes in mice in relation to age and acute, subchronic, and chronic inhalation exposure.

During a 2-year chronic inhalation study on methylene chloride (2000 or 0 ppm; 6 hr/day, 5 days/week), gas-uptake pharmacokinetic studies and tissue partition coefficient determinations were conducted on female B6C3F1, mice after 1 day, 1 month, 1 year, and 2 years of exposure. Using physiologically based pharmacokinetic (PBPK) modeling coupled with Monte Carlo simulation and bootstrap resampling for data analyses, a significant induction in the mixed function oxidase (MFO) rate constant (Vmaxc) was observed at the 1-day and 1-month exposure points when compared to concurrent control mice while decreases in glutathione S-transferase (GST) rate constant (Kfc) were observed in the 1-day and 1-month exposed mice. Within exposure groups, the apparent Vmaxc maintained significant increases in the 1-month and 2-year control groups. Although the same initial increase exists in the exposed group, the 2-year Vmaxc is significantly smaller than the 1-month group (p < 0.001). Within group differences in median Kfc values show a significant decrease in both 1-month and 2-year groups among control and exposed mice (p < 0.001). Although no changes in methylene chloride solubility as a result of prior exposure were observed in blood, muscle, liver, or lung, a marginal decrease in the fat:air partition coefficient was found in the exposed mice at p = 0.053. Age related solubility differences were found in muscle:air, liver:air, lung:air, and fat:air partition coefficients at p < 0.001, while the solubility of methylene chloride in blood was not affected by age (p = 0.461). As a result of this study, we conclude that age and prior exposure to methylene chloride can produce notable changes in disposition and metabolism and may represent important factors in the interpretation for toxicologic data and its application to risk assessment.

Characterization of hepatocellular resistance and susceptibility to styrene toxicity in B6C3F1 mice.

Short-term inhalation exposure of B6C3F1 mice to styrene causes necrosis of centrilobular (CL) hepatocytes. However, in spite of continued exposure, the necrotic parenchyma is rapidly regenerated, indicating resistance by regenerated cells to styrene toxicity. These studies were conducted to test the hypothesis that resistance to repeated styrene exposure is due to sustained cell proliferation, with production of hepatocytes that have reduced metabolic capacity. Male mice were exposed to air or 500 ppm styrene (6 h/day); hepatotoxicity was evaluated by microscopic examination, serum liver enzyme levels, and bromodeoxyuridine (BrdU)-labeling index (LI). Metabolism was assessed by measurement of blood styrene and styrene oxide. Both single and repeated exposures to styrene resulted in mortality by Day 2; in mice that survived, there was CL necrosis with elevated BrdU LI at Day 6, and complete restoration of the necrotic parenchyma by Day 15. The BrdU LI in mice given a single exposure had returned to control levels by Day 15. Re-exposure of these mice on Day 15 resulted in additional mortality and hepatocellular necrosis, indicating that regenerated CL cells were again susceptible to the cytolethal effect of styrene following a 14-day recovery. However, in mice repeatedly exposed to styrene for 14 days, the BrdU LI remained significantly increased on Day 15, with preferential labeling of CL hepatocytes with enlarged nuclei (karyomegaly). If repeated exposures were followed by a 10-day recovery period, CL karyomegaly persisted, but the BrdU LI returned to control level and CL hepatocytes became susceptible again to styrene toxicity as demonstrated by additional mortality and acute necrosis after a challenge exposure. These findings indicated a requirement for continued styrene exposure and DNA synthesis in order to maintain this resistant phenotype. Analyses of proliferating-cell nuclear-antigen (PCNA) labeling were conducted to further characterize the cell cycle kinetics of these hepatocytes. The proportion of cells in S-phase was increased by repeated exposure. However, PCNA analysis also revealed an even larger increase in the G1 cell compartment with repeated exposures, without a concurrent increase in G2 phase or in mitotic cell numbers. These data indicate that resistance to styrene-induced necrosis under conditions of repeated exposure is not due to sustained cell turnover and production of new, metabolically inactive cells, but rather is due to some other, as yet unknown, protective phenotype of the regenerated cells.

Characterization of inhaled alpha-methylstyrene vapor toxicity for B6C3F1 mice and F344 rats.

alpha-Methylstyrene (AMS) is a chemical intermediate used in the synthesis of specialty polymers and copolymers. Inhalation studies of AMS were conducted because of the lack of toxicity data and the structural similarity of AMS to styrene, a toxic and potentially carcinogenic chemical. Male and female B6C3F1 mice were exposed to 0, 600, 800, or 1000 ppm AMS 6 h/day, 5 days/week, for 12 days. After 1 exposure, 21% (5/24) of female mice were found dead in the 1000-ppm group, 56% (10/18) in the 800-ppm group, and 6% (1/18) in the 600-ppm concentration group. After 12 exposures, relative liver weights were significantly increased and relative spleen weights were significantly decreased in both male and female mice at all concentrations. No microscopic treatment-related lesions were observed. A decrease in hepatic glutathione (GSH) was associated with AMS exposure for 1 and 5 days. Male and female F344 rats were exposed to 0, 600 or 1000 ppm AMS for 12 days. No mortality or sedation occurred in AMS-exposed rats. Relative liver weights were significantly increased in both males and females after 12 exposures to 600 or 1000 ppm. An increased hyaline droplet accumulation was detected in male rats in both concentration groups; no significant microscopic lesions were observed in other tissues examined. Exposure of male and female F344 rats and male NBR rats to 0, 125, 250 or 500 ppm AMS, 6 h/day for 9 days resulted in increased accumulation of hyaline droplets in the renal tubules of male F344 rats in the 250 and 500 ppm concentration groups. Although AMS and styrene are structurally very similar, AMS was considerably less toxic for mice and more toxic for male rats than styrene.

Distribution and disposition of morpholine in the rabbit.

The results of a variety of in vivo and in vitro experiments suggested that the kidneys were the primary route of elimination of morpholine in the rabbit. Morpholine was not bound to serum proteins and was excreted 90% unchanged. The concentration of [14C]morpholine in the renal cortex was 6.6 times the concentration in the blood, and in the renal medulla was 15.3 times the concentration in the blood 30 min after the intravenous injection of single boluses of labelled compound. The chemical appeared to be distributed mainly to the extracellular space, and its rate of elimination was enhanced by acidification of the urine.

Failure of carbon disulfide and levothyroxine to modify the cardiovascular response of rabbits to a high-cholesterol diet.

Exposure of rabbits for 12 weeks to 300 ppm carbon disulfide (CS2) for 6 h/day, 5 days/week, or to 25 mg/day of thiourea or 2% cholesterol in the diet, or to any combination thereof caused a significant reduction in the concentration of serum thyroxine (T4). The reduction of the concentration of serum T4 in rabbits by the treatments was completely offset by the inclusion of 0.1 mg/day of sodium levothyroxine in the diet. Ingestion of feed containing 2% cholesterol significantly increased the degree of atherosclerosis present in the aortic arch and significantly increased the oil red O positive lipid present in the heart and the aorta, with the aortic arch being the most severely affected. The response of the aorta and the heart to the 2% cholesterol diet was not significantly modified by concurrent exposure to CS2 by inhalation or by treatment with thiourea, a metabolite of CS2. We found no evidence that the development of cardiovascular lesions induced by a 2% cholesterol diet in rabbits was mediated by a mechanism involving a component of hypothyroidism.

Evidence for oxidative damage to red blood cells in mice induced by arsine gas.

In animals and human beings exposed to arsine gas (AsH3) a severe and fulminant lysis of erythrocytes occurs. Little is known about the effects of subchronic exposure on the hematopoietic system or about the mechanism of hemolysis produced by arsine gas. To examine these, we exposed male and female mice to 0.000, 0.025, 0.500 and 2.500 ppm arsine gas for 6 h a day, 5 days a week during a 90-day period. After 5, 15, and 90 days of exposure, blood was collected and routine hematologic profiles were performed to document the effects of arsine gas on peripheral blood. A moderate hemolytic anemia, indicated by decreases in erythrocyte counts, hematocrits, hemoglobin concentrations and increases in mean corpuscular hemoglobins and mean corpuscular hemoglobin concentrations, was seen in blood samples collected after 5 days of exposure. In blood collected after 15 and 90 days of exposure, the anemia was less severe but a greater increase in mean corpuscular volumes and absolute reticulocyte counts revealed an active regenerative response. Higher concentrations of methemoglobin in animals in the 2.500 ppm exposure group (measured after 90 days of exposure) indicated that the rate of oxidation of heme (ferrous to ferric) increased due to exposure to arsine gas. Additionally, the presence of Heinz bodies in blood smears stained with brilliant cresyl blue and decreases in reduced glutathione concentrations in red blood cells exposed to arsine gas in vitro provide evidence that the mechanism of hemolysis involves depletion of intracellular reduced glutathione resulting in an oxidation of sulfhydryl groups in hemoglobin and possibly red cell membranes.

Carbon disulfide neurotoxicity in rats: II. Toxicokinetics.

Carbon disulfide (CS2) is an important industrial chemical widely used in the production of rayon, cellophane, fungicides and biocides. The uptake and elimination kinetics of CS2 was characterized for a single i.v. dose and for a single inhalation exposure. The uptake of CS2 into the blood was rapid with half times of 6 to 9 minutes. Elimination was relatively quick with terminal elimination half times of 41 to 77 minutes. The plateau CS2 blood concentration was lower in females than in males and lower in the male 50 ppm treatment group than would be predicted by linear dose proportionality compared to the 500 ppm and 800 ppm treatments. The CS2 blood concentration for the female 50 ppm group was below the limit of detection. The total and central compartment apparent volumes of distribution, 4.2 l/kg and .9 l/kg, were estimated from a single 50 mg/kg i.v. dose. The concentration of CS2 in blood resulting from repeated exposure, was investigated in a 13 week inhalation study. Blood samples were taken in rats previously exposed to 0, 50, 500, and 800 ppm CS2 for 2, 4, 8, or 13 weeks. The concentration of CS2 in the blood of male rats remained relatively constant throughout study. However the female 500 and 800 ppm groups showed a marked decrease over the course of the 13 week study. The concentration of CS2 in the blood from the 500 and 800 ppm groups of both sexes at all time points was higher compared to the 50 ppm group, than would be predicted by linear dose proportionality. The concentration of 2-thiothiazolidine-4-carboxylic acid in urine collected from the same animals lacked dose proportionality between the treatment groups at all time points. CS2 exposure caused dose-related decreases in body weight gain in both male and female rats.

Assessment of adult toxicity in developmental versus prechronic toxicology studies.

There is no general agreement at the present time regarding the role of maternal toxicity in the manifestation of teratogenic effects or developmental toxicity animal studies designed to identify the teratogenic potential of chemicals. A survey of 90 teratology studies published in the recent literature revealed wide differences in the amount and nature of maternal toxicity data collected in teratology studies. In addition, the use of the maternal toxicity data in the process of interpreting developmental toxicity varied widely between authors. In comparison with teratology studies, there is more uniformity in the collection of toxicity data in prechronic toxicity studies. The guidance provided by various government agencies on the parameters to be observed in prechronic toxicity studies is much more explicit than that provided regarding the collection of maternal toxicity data in teratology studies. Because of the likely importance of maternal toxicity in the conduct and interpretation of teratology studies, it is recommended that more maternal toxicity data be collected in teratology studies and the parameters be standardized between laboratories so that data are comparable. Guidelines should be established for the use of maternal toxicity data in the interpretation of the results of teratology studies.

Time-varying concentration profile as a determinant of the inhalation toxicity of carbon tetrachloride.

Certain limitations on the flexibility of small-animal inhalation exposure systems are overcome by the machine control and monitoring of the concentration of the gas or vapor of interest. Computer assistance of chamber operation allows the user to simulate time-varying concentration profiles accurately and repeatedly. We exposed rats to seven different profiles in which the maximum concentration of carbon tetrachloride (CCl4) was 1500 ppm and the product of concentration times time (C X T) was 4500 ppm X h. The purpose was to determine the effects of systematically varying the shape of the concentration profile on the expression of hepatotoxicity of a chemical about which much was already known. All of the exposures were conducted within a span of 6 h. Examination of the severity of vacuolation and pattern of necrosis could be used to distinguish some of the exposure profiles from others. For example, vacuolation was less severe when two equal pulses were presented with an interval of 60 min, rather than 180-240 min. The indexes of necrosis varied in a more complex way, and the differences among the profiles that accounted for the differences in the patterns of the histopathological changes were not immediately apparent. We concluded that the characteristic of a time-related variation in concentration is one of the determinants of the inhalation hepatotoxicity of CCl4 and that the simple, time-weighted, average concentration may not always fairly represent the best model for the study of problems in inhalation toxicology.

Comparative toxicity of arsine gas in B6C3F1 mice, Fischer 344 rats, and Syrian golden hamsters: system organ studies and comparison of clinical indices of exposure.

In order to examine possible species differences in response to arsine exposure, multiple inhalation studies consisting of acute (1-day), subacute (14- and 28-day), and subchronic (90-day) exposures to this agent were conducted using three different species of rodents. Evaluations of hematopoietic organs and alterations in the heme biosynthetic pathway were the focus of these studies. Species used were B6C3F1 mice (exposed 1, 14, or 90 days), Fischer 344 rats (exposed 14, 28, or 90 days), and Syrian Golden hamsters (exposed 28 days). All arsine exposures were at concentrations of 0.5, 2.5, or 5.0 ppm except for 90-day studies, in which concentrations were lowered to 0.025, 0.5, or 2.5 ppm. No changes in body weight gain were observed in either sex of mice or hamsters. The only decrease in body weight gain occurred in male rats exposed to 5.0 ppm arsine for 28 days. Significant exposure-related increases in relative spleen weights occurred in both sexes of mice and rats in the 0.5 (except 14-day female rats), 2.5, and 5.0 ppm exposure groups from all studies and in hamsters in the 2.5 and 5.0 ppm exposure groups. Generally, increases in relative liver weight occurred in fewer exposure groups and were of a lesser magnitude than increases in spleen weight. Other parameters affected included decreased packed cell volumes (mice, rats, and hamsters), hematology profiles (rats), and an increase in delta-aminolevulinic acid dehydratase activity in all species. Arsenic content was measured in livers of rats after 90 days of exposure. Concentrations increased in relation to atmospheric concentrations of arsine. Histopathologic changes included increased hemosiderosis and extramedullary hematopoiesis in spleen and intracanalicular bile stasis (mice only) in liver. Additionally, bone marrow hyperplasia was observed in rats. Effects on other organs were not observed, suggesting that the hematopoietic system is the primary target for arsine. In conclusion, we have determined that the effects of arsine exposure upon mice, rats, and hamsters are similar. Most importantly, even though no effects on the hematopoietic system were observed following a single exposure to 0.5 ppm arsine which is 10 times the Threshold Limit Value (TLV) set by the American Conference of Governmental Industrial Hygienists, repeated exposure to 0.025 ppm (one-half the TLV) caused a significant anemia in rats.

Endogenous formation of N-nitrosomorpholine in mice from 15NO2 by inhalation and morpholine by gavage.

Male CD-1 mice were exposed to an nominal concentration of 20 p.p.m. of 15N-nitrogen dioxide (15NO2) for 6 h/day for 4 days and for 2 h on the day 5, and to 1 g morpholine/kg body wt by gavage daily for five consecutive days. N-Nitrosomorpholine (NMOR) was found in whole mice, stomachs, skins with hair, and remains. The sum of individual tissue concentrations measured separately was 3421 ng/tissue, where the average skin weighed 4.3 g, the average stomach weighed 1.0 g and the average remains weighed 22.2 g. The average whole mouse weighed 27.7 g and contained a total of 3903 ng of NMOR. The concentration of NMOR was highest in the skin, next highest in the stomach, and lowest in the remains. However, the total quantity of NMOR per tissue, while highest in the skin (83%), was next highest in the remains (14.8%) and lowest in the stomach (2.2%). GC-MS analysis served to distinguish between the NMOR of 15NO2 origin and that of other origin. All of the NMOR in the whole mouse homogenates was identified as 15NMOR. In the stomach 73% was identified as 14NMOR, representing 1.6% of the total NMOR in the mouse, and 27% as 15NMOR, representing 0.6% of the total NMOR in the mouse. N-Nitrosamine formation in vivo is discussed as a possibly ongoing mammalian process.

Arsine: absence of developmental toxicity in rats and mice.

Arsine gas is a potent hemolytic agent but the effects of exposure to tolerated concentrations on pregnancy and prenatal development have not been reported. In the present evaluation, groups of bred mice and rats were exposed to arsine at concentrations of 0.025, 0.5, or 2.5 ppm on Gestation Days (gd) 6 through 15. Animals were killed on gd 17 (mice) or on gd 20 (rats) and endpoints of maternal and developmental toxicity were evaluated. In rats, maternal spleens were enlarged in the 2.5 ppm group and there was a decrease in packed red cell volume in pregnant rats. Fetuses weighed more than in the control group but other endpoints of developmental toxicity were not affected by arsine exposure. In another experiment involving separate groups of rats, the arsenic content of maternal blood and fetal livers increased with increasing atmospheric arsine concentrations, as assessed on gd 20. In mice, maternal spleen size was significantly increased in the 2.5 ppm group. The number of live fetuses, mean fetal body weight, and percentages of resorptions or malformations per litter were not affected by arsine exposure. In conclusion, arsine at atmospheric concentrations that caused increases in maternal spleen size and measurable levels of arsenic in maternal blood and fetal livers did not adversely affect endpoints of developmental toxicity.

Absorption, distribution, metabolism, and excretion of 1,2-dihydro-2,2,4-trimethylquinoline in the male F344 rat.

1,2-Dihydro-2,2,4-trimethylquinoline (TMQ), an antioxidant used in the rubber industry, was readily absorbed from the gastrointestinal tract of the male Fischer 344/N rat and rapidly distributed throughout the body tissues. Absorption, distribution, metabolism, and excretion were not significantly affected by dose in the range 11.5-1150 mumol/kg. Following iv administration, the greatest amounts of TMQ-derived radioactivity were present in the high volume tissues including muscle, adipose, skin, liver, and blood. TMQ had no particular affinity for any tissue. TMQ-derived radioactivity was excreted primarily in urine (60-70%) and feces (20-30%) within 3 days after administration. Greater than 99% of the TMQ dose excreted in urine and feces was in the form of metabolites. Urine contained two major and ten minor metabolites while feces contained two major and four minor metabolites. The two major TMQ metabolites in urine were identified by NMR and mass spectroscopy as the O-sulfate conjugate of 1,2-dihydro-6-hydroxy-2,2,4-trimethylquinoline and the monosulfate conjugate of 1,2-dihydro-1,6-dihydroxy-2,2,4-trimethylquinoline. In vitro studies with liver subcellular fractions suggest that most of the metabolites present in urine, feces, and bile are the products of mixed function oxidase activity and conjugates of these metabolites. Multiple exposure of rats to high TMQ doses (1150 mumol/kg) resulted in some bioaccumulation of TMQ-derived radioactivity in all tissues examined, but these residues did not persist when dosing was discontinued.

Effects of various pretreatments on the hepatotoxicity of inhaled styrene in the B6C3F1 mouse.

1. The roles of cytochrome P450 monooxygenases (P450) and glutathione (GSH) in styrene hepatotoxicity were investigated in mice by pretreating with either phenobarbital (PB; P450 inducer), SKF 525A (P450 inhibitor), N-acetylcysteine (NAC; GSH precursor), or saline (vehicle control) prior to a 6-h exposure to either 500 ppm styrene on air. 2. Styrene caused hepatocellular degeneration or necrosis in all groups; these changes were more extensive and severe in mice pretreated with PB. Styrene significantly increased relative liver weights and serum ALT and SDH levels only in mice pretreated with PB. NAC did not prevent GSH depletion or hepatotoxicity. 3. In the fat of SKF 525A-pretreated mice a slight but statistically significant increase in styrene levels was observed, suggesting that metabolism was decreased; the SO/styrene ratio in the fat of PB-pretreated mice showed a slight, but statistically significant, increase indicating a slight increase in styrene metabolism. Neither SKF 525A nor PB caused changes in microsomal enzyme activity in vitro. 4. These results suggest that styrene may be activated by a pathway not totally dependent upon P450 enzyme activity, or more likely that PB and SKF 525A are not specific for the P450 enzymes involved in activation and detoxification of styrene.

Comparison of styrene hepatotoxicity in B6C3F1 and Swiss mice.

Inhalation exposure to styrene at concentrations that cause metabolic saturation results in significantly greater hepatotoxicity in B6C3F1 mice than in Swiss mice; females of both strains are more susceptible than males. These studies were conducted to investigate the mouse strain and gender differences in susceptibility to hepatotoxicity caused by repeated exposure to styrene at concentrations that do not cause metabolic saturation. Male and female B6C3F1 and Swiss mice (8 weeks old) were exposed to 0, 150, or 200 ppm styrene for 6 hr/day, 5 days/week, for up to 2 weeks. Changes in body and liver weights, serum alanine aminotransferase (ALT) and sorbitol dehydrogenase (SDH) levels, liver histopathology, and total liver glutathione (GSH) were evaluated after 2, 3, 5, and 10 exposures (six mice/sex/strain/time point/concentration). Blood levels of styrene and styrene-7,8-oxide (SO) were measured in mice exposed to 200 ppm styrene for 2,3, or 5 days (six mice/sex/strain/time point/concentration). Serum ALT and SDH levels were significantly elevated only in female B6C3F1 mice after 3 exposures to 200 ppm styrene; enzyme levels had returned to control levels when measured after 5 and 10 exposures. Degeneration and coagulative necrosis of centrilobular hepatocytes were observed in female B6C3F1 mice exposed 2, 3, and 5 days to 150 or 200 ppm styrene; incidences of these lesions were greater in the 200 ppm than in the 150 ppm dose group. After 10 days of exposure to 150 or 200 ppm styrene, hepatocellular lesions had resolved, although a residual chronic inflammation was present in livers of most female B6C3F1 mice.(ABSTRACT TRUNCATED AT 250 WORDS)

Inhalation toxicity studies of the alpha,beta-unsaturated ketones: 2-cyclohexene-1-one.

2-Cyclohexene-1-one (CHX) is a cyclic alpha,beta-unsaturated ketone with broad human exposure. CHX is an environmental pollutant and is present in tobacco smoke and in soft drinks sweetened with cyclamate. Interest in the toxicity of this class of compounds is due to their structural similarity to the cytotoxin acrolein. In a pilot study, rats and mice were exposed to 0, 20, 40, or 80 ppm CHX for 6 h/day. The study was terminated after 4 days due to acute toxicity in the high-dose groups. In a subsequent 14-day study, mice and rats were exposed to 0, 2.5, 5, or 10 ppm CHX for 6 h/day. All animals survived exposure until terminal sacrifice. Body weights were not significantly different from controls after 14 days of exposure. Liver/body weights were increased in male and female mice exposed to 5 and 10 ppm, and in male and female rats exposed to 10 ppm CHX. Ninety-day toxicity studies were conducted to provide data required to design chronic toxicity and carcinogenicity studies of CHX if it is determined such studies are necessary. Groups of 10 male and female F-344 rats and B6C3F1 mice were exposed to 0, 2.5, 5, or 10 ppm CHX for 6 h/day for 13 wk. All animals survived until sacrifice. Body weights were not significantly different from controls after 13 wk of exposure. Liver weights were increased in male and female mice exposed to 5 and 10 ppm and in male and female rats exposed to 10 ppm CHX. No adverse effects on bone-marrow micronuclei, sperm motility, or vaginal cytology were observed. Microscopic lesions included hyperplasia, and squamous metaplasia in the nasal cavity in rats and mice of both sexes at all doses. Nasal-cavity erosion and suppurative inflammation also occurred in high-dose mice. Larynx and lung were not affected in either sex or species. Dose-related hepatic centrilobular cytoplasmic vacuolation was seen in male rats only. These data suggest that CHX acts as an alkylating agent primarily producing toxicity at the exposure site.

Toxicity of divinylbenzene-55 for B6C3F1 mice in a two-week inhalation study.

Divinylbenzene (DVB) is a crosslinking monomer used primarily for copolymerization with styrene to produce ion-exchange resins. The toxicity of inhaled DVB was investigated because of the potential for worker exposure and the structural similarity of DVB to styrene, a potential carcinogen. Male and female B6C3F1 mice were exposed to 0, 25, 50, or 75 ppm DVB for 6 hr/day, 5 days/week for up to 2 weeks. Six mice/sex/dose group were killed after 3, 5, and 10 exposures and six mice/sex in the 75 ppm group were killed 7 days after 10 exposures. The most severe effects occurred in the nasal cavity and liver, with less severe effects occurring in the kidneys. In the nasal cavity olfactory epithelium acute necrosis and inflammation were present at early time points followed by regeneration, architectural reorganization, and focal respiratory metaplasia by 7 days after the last exposure. Olfactory epithelial changes were concentration-dependent with extensive involvement at 75 ppm and peripheral sparing at 25 ppm. There was also necrosis and regeneration of olfactory-associated Bowman's glands as well as the lateral nasal (Steno's) glands. Hepatocellular centrilobular (CL) necrosis was observed only in the 75 ppm dose group and was similar to that caused by styrene. A time-dependent progression was observed, characterized by CL degeneration after 1 exposure, necrosis after 3 and 5 exposures, and chronic inflammation with CL karyomegaly after 10 exposures and 7 days after the 10th exposure. Hepatic GSH levels were decreased in a dose-dependent manner. In the kidneys, transient tubular damage was observed in some male mice exposed to 75 ppm, and appeared to be a response to DVB-induced tubular epithelial injury.