Information on nasal particle deposition is used in risk assessments for exposure to airborne particulate pollutants and for optimizing the delivery of therapeutic aerosols. Monkeys are commonly used to assess the therapeutic potential of inhaled substances and to a lesser extent the toxicity of inhaled xenobiotics. Yet no reliable measurements of the deposition efficiency of monkey nasal airways for particles >1 μm have been reported to date. The goals of this study were to measure the deposition efficiency (>1 μm) of a replica of monkey nasal airways and to investigate potential differences in nasal deposition between humans and monkeys by comparing results with similar measurements recently reported for human nasal replicas. The monkey nasal replica was an acrylic mold made from a postmortem cast of the nasal airways of a 12-kg, male rhesus monkey. Particle deposition in the monkey nasal mold was measured for monodisperse aerosols between 1 and 10 μm and constant inspiratory flow rates between 2 and 7 lpm. Total deposition efficiency increased from nearly 0 to 100% with increasing particle inertia and was uniquely determined by values of an inertial impaction parameter. The deposition efficiencies of the monkey replica agreed well with those of human nasal replicas when compared according to equivalent Stokes numbers based on minimum cross-sectional area. Results from this study could improve monkey-to-human extrapolation models and interpretations of data from particle toxicity and therapeutic aerosol studies using monkeys.

There is little information regarding the tissue distribution of manganese in neonates following inhalation. This study determined tissue manganese concentrations in lactating CD rats and their offspring following manganese sulfate (MnSO4) aerosol inhalation. Except for the period of parturition, dams and their offspring were exposed to air or MnSO4 (0.05, 0.5, or 1 mg Mn/m3) for 6 h/day, 7 days/week starting 28 days prior to breeding through postnatal day (PND) 18. Despite increased manganese concentrations in several maternal tissues, MnSO4 inhalation exposure did not affect body weight gain, terminal (PND 18) body weight, or organ weights in the dams. Exposure to MnSO4 at 1 mg Mn/m3 resulted in decreased pup body weights on PND 19 and decreased brain weights in some PND 14 to PND 45 pups. Exposure to MnSO4 at > or =0.05 mg Mn/m3 was associated with increased stomach content, blood, liver, and skull cap manganese concentrations in PND 1 pups, increased brain, lung, and femur manganese concentrations in PND 14 pups, and elevated olfactory bulb, cerebellum, and striatum manganese concentrations in PND 19 pups. When compared to controls, MnSO4 exposure to > or =0.5 mg Mn/m3 increased liver and blood manganese concentrations in PND 14 pups and increased liver, pancreas, and femur manganese concentrations in PND 19 pups. Manganese concentrations returned to control values in all offspring tissues by PND 45 +/- 1. Our data demonstrate that neonatal tissue manganese concentrations observed following MnSO4 inhalation are dependent on the MnSO4 exposure concentration and the age of the animal.

Information on the deposition of ultrafine particles in nasal airways is important for assessing the risks of exposure to airborne particulate matter and for understanding drug delivery implications for particles of this diameter. Nasal particle deposition is often studied using plastic replicas of nasal airways. Ultrafine particle deposition has been measured previously in replicas of nasal and upper airways that were manufactured from magnetic resonance images or cadaver specimens. Here we determined the deposition efficiency of two replicas of the same nasal airways manufactured by different stereolithography processes and investigated the sensitivity of ultrafine particle deposition to differences in nasal airways by comparing results from our nasal replicas with those of other models. Two replicas of the same nasal airways were manufactured from a finite-element mesh using stereolithography machines with different resolutions. Deposition efficiency of the replicas was measured for particle diameters between 0.005 and 0.15 μm and constant inspiratory flow rates of 10 and 20 I/min. Deposition efficiency was less than 10% for particles > 0.03 μm and increased for particles < 0.03 μm. The increase correlated with increased particle diffusivity. Deposition in the replicas was similar within the scatter of the measurements. Reasonable agreement was found between our deposition measurements and those reported previously for other models. Small differences in deposition measurements for the various nasal replicas could not be attributed to differences in methods used to manufacture the replicas. Ultrafine particle deposition results for nasal replicas suggest that small differences in nasal airways have minimal effect on nasal deposition efficiency for particles <0.15 μm.

The lacI mutant frequency and mutation spectrum were determined in the bone marrow and testes of B6C3F1 lacI transgenic mice exposed by inhalation to ethylene oxide (EO). Groups of male transgenic lacI B6C3F1 mice were exposed to 0, 25, 50, 100 or 200 p.p.m. EO for up to 48 weeks (6 h/day, 5 days/week) and were killed at 12, 24 or 48 weeks of EO exposure for determination of lacI mutant frequency. In the bone marrow, the lacI mutant frequency was significantly increased at the two highest exposure levels (100 and 200 p.p.m.) and at the 48 week exposure time point. The shape of the exposure-response curve for lacI mutant frequency in the bone marrow was non-linear. DNA sequence analysis of the bone marrow mutation spectrum revealed that only AT-->TA transversions occurred at an increased frequency in EO-exposed mice: 25.4% in EO-exposed mice for 48 weeks (200 p.p.m.) compared with 1.4% in air controls. In testes, the lacI mutant frequency was increased at a single exposure level of 200 p.p.m. for 24 weeks. At 48 weeks, the lacI mutant frequency in testes was significantly increased to an equal degree at 25, 50 and 100 p.p.m. EO but not at 200 p.p.m. Analysis of the testes mutation spectrum in air control mice and in mice exposed to 200 p.p.m. EO for 48 weeks revealed that no single mutational type occurred at an increased frequency. In the testes, there was a small increase across all mutational types that was sufficient to increase the overall lacI mutation frequency although not significant individually. The mutation spectrum in testes of EO-exposed mice also revealed that the increased lacI mutant frequency observed at 25 or 50 p.p.m. EO was not due to an increase in mutant siblings (clonality). These data demonstrate that inhalation exposure to EO for up to 48 weeks produces distinct mutagenic responses in bone marrow and testes.

Interspecies differences in pulmonary and pleural responses to the inhalation of natural mineral and synthetic vitreous fibers have been observed in chronic and subchronic studies. However, the reasons for these differences are not clearly understood. There are also fiber-specific differences in the outcome of chronic inhalation exposure to natural mineral and synthetic vitreous fibers. Whether these differences are dependent upon the ability of these fibers to translocate to the pleural space is unknown. The present study was conducted to compare retained fiber burdens and selected pathological responses in the pleural compartments of rats and hamsters following subchronic inhalation of MMVF 10a fiberglass, a fiber negative for tumorigenesis or fibrosis in chronic studies. Fischer 344 rats and Syrian golden hamsters were exposed for 4 or 12 weeks by nose-only inhalation at nominal aerosol mass concentrations of 45 mg/m3 (610 WHO fibers/cc). Pulmonary fiber burdens and pulmonary inflammatory responses were greater in rats than in hamsters. The total number of fibers in the lung was approximately three orders of magnitude greater than in the pleural compartment. Pleural burdens in the hamster (160 fibers/cm2 surface area) were significantly greater than burdens in similarly exposed rats (60 fibers/cm2 surface area) following 12 weeks of exposure. With time postexposure, pleural burdens decreased in hamsters but were essentially unchanged in rats. Pleural inflammatory responses in both species were minimal. In rats, pleural inflammation was characterized by increased numbers of macrophages and increases in mesothelial cell replication during the period of fiber exposure. In contrast, hamsters had increased numbers of macrophages and lymphocytes, and mesothelial-cell replication indices were elevated on the parietal pleura of the costal wall and diaphragm, with some of these responses persisting through 12 weeks of postexposure recovery. Taken together, the results suggest that differences among rodent species in pleural responses to inhaled fibers are due to a delivered dose of fibers and to the biological responses to the presence of the fibers.

Experiments examining the dosimetry of inhaled manganese generally focus on pulmonary deposition and subsequent delivery of manganese in arterial blood to the brain. Growing evidence suggests that nasal deposition and transport along olfactory neurons represents another route by which inhaled manganese is delivered to certain regions of the rat brain. The purpose of this study was to evaluate the olfactory uptake and direct brain delivery of inhaled manganese phosphate ( 54 MnHPO 4 ). Male, 8-wk-old, CD rats with either both nostrils patent or the right nostril occluded underwent a single, 90-min, nose-only exposure to a 54 MnHPO 4 aerosol (0.39 mg 54 Mn/m 3 ; MMAD 1.68 w m, σ g 1.42). The left and right sides of the nose, olfactory pathway, striatum, cerebellum, and rest of the brain were evaluated immediately after the end of the 54 MnHPO 4 exposure and at 1, 2, 4, 8, and 21 d postexposure with gamma spectrometry and autoradiography. Rats with two patent nostrils had equivalent 54 Mn concentrations on both sides of the nose, olfactory bulb, and striatum, while asymmetrical 54 Mn delivery occurred in rats with one occluded nostril. High levels of 54 Mn activity were observed in the olfactory bulb and tubercle on the same side (i.e., ipsilateral) to the open nostril within 1-2 d following 54 MnHPO 4 exposure, while brain and nose samples on the side ipsilateral to the nostril occlusion had negligible levels of 54 Mn activity. Our results demonstrate that the olfactory route contributes to 54 Mn delivery to the rat olfactory bulb and tubercle. However, this pathway does not significantly contribute to striatal 54 Mn concentrations following a single, short-term inhalation exposure to 54 MnHPO 4 .

Manganese-deficient individuals have decreased manganese elimination. This observation has prompted suggestions that relative manganese deficiency may increase the risk for manganese neurotoxicity following inhalation exposure. The objective of this study was to determine whether dietary manganese intake influences the pharmacokinetics of inhaled manganese tetroxide (Mn3O4). Postnatal day (PND) 10 rats were placed on either a low (2ppm), sufficient (10ppm), or high-normal (100ppm) manganese diet for 2 months. Beginning on PND 77 ± 2, male littermates were exposed 6h per day for 14 consecutive days to 0, 0.042, or 0.42mg Mn3O4/m3. End-of-exposure tissue manganese concentrations and whole-body 54Mn elimination rates were determined. Tissue manganese concentrations were dependent on the dietary intake of manganese, thus confirming that altered hepatic manganese disposition or metabolism occurred. Male rats given 100ppm manganese diet developed increased manganese concentrations in the femur, liver, and bile and had elevated whole-body 54Mn clearance rates when compared to animals given 2ppm manganese diet. Male rats exposed to 0.42mg Mn3O4/m3 had increased manganese concentrations in the olfactory bulb, lung, liver, and bile when compared to air-exposed male rats. A significant interaction between the concentration of inhaled Mn3O4 and dietary manganese level was observed only with the end-of-exposure liver manganese concentration. Our results indicate that animals maintained on either a manganese-deficient or high manganese diet do not appear to be at increased risk for elevated brain manganese concentrations following inhalation exposure to high levels of Mn3O4.

Chloroform is a nongenotoxic-cytotoxic carcinogen in rodent liver and kidney, including the female B6C3F1 mouse liver. Because tumors are secondary to events associated with cytolethality and regenerative cell proliferation, these end points are valid surrogates for tumor formation in cancer risk assessments. The purpose of the experiments presented here was to more clearly define the combinations of atmospheric concentration and duration of exposure necessary to induce cytolethality and regenerative cell proliferation in the sensitive female B6C3F1 mouse liver. Female B6C3F1 mice were exposed to chloroform by inhalation for 7 consecutive days using atmospheres of 10, 30, or 90 ppm and selected exposure times of 2, 6, 12, or 18 h/day. Bromodeoxyuridine (BrdU) was given the last 3.5 days via an implanted osmotic pump to label cells in S-phase. Labeled hepatocytes were visualized immunohistochemically, and the labeling index (LI) was determined as the percentage of cells in S-phase. LI was a more sensitive indicator of cellular damage than histopathological examination and is the more conservative end point for use in risk assessments. Significant concentration and exposure time related increases in LI were observed at 30 and 90 ppm but not at any 10-ppm exposure. These data defined an empirical relationship for the combinations of airborne exposure concentration and duration needed to induce cytolethality. These results suggest that concentrations of about 10 ppm or below will not induce hepatotoxicity in these mice regardless of exposure duration. Thus, the rate of production of toxic metabolites and the subsequent rate of cellular damage produced by a continual exposure of approximately 10 ppm chloroform are less than the maximum rates at which hepatocytes can detoxify those metabolites and repair any induced cellular damage. A physiologically based pharmacokinetic (PBPK) dosimetry model was used to compare anticipated responses in mice and humans and predicted that chloroform concentrations of approximately an order of magnitude greater than 10 ppm would be required to induce human liver toxicity. Thus, no safety factor to account for species to species extrapolation should be required in formulating a chloroform inhalation cancer risk assessment based on the dose x time inhalation data presented here.

tert-Butyl alcohol (TBA) has been shown to cause kidney tumors in male rats following chronic administration in drinking water. The objective of the present study was to determine whether TEA induces alpha 2u-globulin (alpha 2u) nephropathy (alpha 2u-N) and enhanced renal cell proliferation in male, but not female, F-344 rats, and whether the dosimetry of TBA to the kidney is gender specific. Male and female F-344 rats were exposed to 0, 250, 450, or 1750 ppm TEA vapors 6 h/day for 10 consecutive days to assess alpha 2u-nephropathy and renal cell proliferation and for 1 and 8 days to evaluate the dosimetry of TEA following a single and repeated exposure scenario. Protein droplet accumulation was observed in kidneys of male rats exposed to 1750 ppm TEA, with alpha 2u-globulin immunoreactivity present in these protein droplets. A statistically significant increase in alpha 2u concentration in the kidney, as measured by an enzyme-linked immunosorbent assay, was observed in male rats exposed to 1750 ppm TEA with a exposure-related increase in renal cell proliferation. Renal alpha 2u concentration was positively correlated with cell proliferation in male rat kidney, No histological lesions or increased renal cell proliferation was observed in female rats exposed to TEA compared to controls. The TEA kidney:blood ratio was higher at all concentrations and time points in male rats compared with female rats, which suggests that TBA is retained longer in male rat kidney compared with female rat kidney. Together these data suggest that TEA causes alpha 2u-N in male rats, which is responsible for the male rat-specific increase in renal cell proliferation.

Concerns exist as to whether individuals with relative manganese deficiency or excess may be at increased risk for manganese toxicity following inhalation exposure. The objective of this study was to determine whether manganese body burden influences the pharmacokinetics of inhaled manganese sulfate (MnSO(4)). Postnatal day (PND) 10 rats were placed on either a low (2 ppm), sufficient (10 ppm), or high (100 ppm) manganese diet. The feeding of the 2 ppm manganese diet was associated with a number of effects, including reduced body weight gain, decreased liver manganese concentrations, and reduced whole-body manganese clearance rates. Beginning on PND 77 +/- 2, male littermates were exposed 6 h/day for 14 consecutive days to 0, 0.092, or 0.92 mg MnSO(4)/m(3). End-of-exposure tissue manganese concentrations and whole-body (54)Mn elimination rates were determined. Male rats exposed to 0.092 mg MnSO(4)/m(3) had elevated lung manganese concentrations when compared to air-exposed male rats. Male rats exposed to 0.92 mg MnSO(4)/m(3) developed increased striatal, lung, and bile manganese concentrations when compared to air-exposed male rats. There were no significant interactions between the concentration of inhaled MnSO(4) and dietary manganese level on tissue manganese concentrations. Rats exposed to 0.92 mg MnSO(4)/m(3) also had increased (54)Mn clearance rates and shorter initial phase elimination half-lives when compared with air-exposed control rats. These results suggest that, marginally manganese-deficient animals exposed to high levels of inhaled manganese compensate by increasing biliary manganese excretion. Therefore, they do not appear to be at increased risk for elevated brain manganese concentrations.

Dissolution rate can influence the pulmonary clearance of a metal and thus affect its delivery to the brain and other organs. The goal of this study was to determine the exposure–response relationship for the relatively soluble sulfate (MnSO4) and insoluble tetroxide (Mn3O4) forms of inhaled manganese in adult male CD rats. Rats were exposed 6 h/day for 7 days/week (14 exposures) to either MnSO4 or Mn3O4 at 0, 0.03, 0.3, or 3 mg Mn/m3. End-of-exposure olfactory bulb, striatum, cerebellum, bile, lung, liver, femur, serum, and testes (n = 6 rats/concentration/chemical) manganese concentrations and whole-body 54Mn elimination were then determined. Increased whole-body 54Mn clearance rates were observed in animals from the high-dose (3 mg Mn/m3) MnSO4 and Mn3O4 exposure groups. Elevated manganese concentrations in the lung were observed following MnSO4 and Mn3O4 exposure to ≥0.3 mg Mn/m3. Increased olfactory bulb and femur manganese concentrations were also observed following MnSO4 exposure at ≥0.3 mg Mn/m3. Elevated striatal, testes, liver, and bile manganese concentrations were observed following exposure to MnSO4 at 3 mg Mn/m3. Elevated olfactory bulb, striatal, femur, and bile manganese concentrations were observed following exposure to Mn3O4 at 3 mg Mn/m3. Animals exposed to MnSO4 (3 mg Mn/m3) had lower lung and higher olfactory bulb and striatal manganese concentrations compared with levels achieved following similar Mn3O4 exposures. Our results suggest that inhalation exposure to soluble forms of manganese results in higher brain manganese concentrations than those achieved following exposure to an insoluble form of manganese.

The disposition of styrene was studied in a group of 12 Sprague Dawley rats and two groups of 30 CD1 mice exposed separately to 160 ppm [ring-U-(14)C]styrene of high specific radioactivity of 1.92 TBq x mol(-1) (52 Ci x mol(-1)) for 6 h. A nose-only exposure system was successfully adapted to (1) recirculate a portion of the flow to limit the amount of (14)C-styrene required, and (2) avoid any polymerization of the compound. The mean uptake of styrene in rats was 113 +/- 7 micromol x kg(-1) x h(-1) and stable over time. The mean uptake in mice was higher, 189 +/- 53 and 183 +/- 76 micromol x kg(-1) x h(-1), for the first and second mouse inhalation experiment, but decreased steadily over time. Some of the mice, but none of the rats, showed signs of overt toxicity. The overall excretion of styrene and its metabolites was quantitatively similar in rats and mice. Urinary excretion was the primary route of excretion while fecal excretion accounted for only a very small part of the radioactivity. There was, however, a significant difference between mice and rats in the exhalation of (14)CO(2), which must have resulted from opening and subsequent breakdown of the aromatic ring. In mice the exhalation of (14)CO(2) accounted for 6.4 +/- 1.0 and 8. 0 +/- 0.5% of the styrene retained during the first and second mouse inhalation experiment. In rats, exhalation of (14)CO(2) accounted for only 2.0 +/- 0.7% of the retained styrene. Together with the results from the quantitative whole-body autoradiography (showing significantly higher binding in mouse lung and nasal passages compared to rat) the larger production of (14)CO(2) might be indicative of the formation of reactive ring-opened metabolites in the mouse lung, which, in turn, might be related to the observed development of bronchioalveolar tumors and nasal effects in mice exposed to styrene.

We present a preliminary report of a bioassay designed to compare and contrast selected pulmonary responses of female B6C3F1 mice, Fischer 344 rats, and Syrian golden hamsters to inhaled pigmentary titanium dioxide (TiO2). Animals were administered 10, 50, or 250 mg/m(3) TiO2 for 6 h/day and 5 days/wk, for 13 wk. Recovery groups were held for an additional 4-, 13-, or 26-wk period. Following exposure and at each recovery time, TiO2 burdens in the lung and lung-associated lymph nodes were determined. A separate group of animals was used at each time point to assess the inflammatory response of the lung by assaying total protein in bronchoalveolar lavage fluid (BALF) and cytologic examination of cells recovered in BALF. Burdens (mg/mg dry weight) of TiO2 in the lung following exposure to 10, 50, or 250 mg/m(3) TiO2 were 5.2, 53.5, and 170.2 for the mouse; 7.1, 45.1, and 120.4 for the rat; and 2.6, 14.9, and 120.3 for the hamster. With time after exposure, lung burdens of TiO2 particles were decreased and lymph-node burdens increased. Changes in the hamsters' burdens were more rapid than those in mice and rats. Increases in BALF cell numbers (macrophages and neutrophils) and in total protein were observed in all 3 species following exposure to 50 and 250 mg/m(3) TiO2, with the magnitude of response being the grea test in the rat. These responses remained elevated relative to control levels at 26 wk postexposure. Histopathologic examination of lungs showed a concentration-dependent retention pattern of particles that varied by species. Hypertrophy and hyperplasia of alveolar epithelium along with alveolar metaplastic and fibrotic changes were observed in rats exposed to 250 mg/m(3) TiO2. Alveolar epithelial proliferative changes were associated with inflammation in mice and hamsters, but the metaplastic and fibrotic changes noted in rats were not present in similarly exposed mice or hamsters. These data suggest that rats exposed subchronically to extremely high concentrations of pigmentary TiO2 differ from mice and hamsters in their cellular responses in the lung as well as in the way they clear and sequester particles. These differences may partly explain the differential outcome of pulmonary responses in various rodent species following chronic inhalation exposure to poorly soluble particles.

Methylcyclopentadienyl manganese tricarbonyl (MMT) is used as a gasoline octane enhancer. Manganese phosphate is the primary respirable (PM2.5) MMT-combustion product emitted from the automobile tailpipe. The goal of this study was to determine the exposure–response relationship for inhaled manganese phosphate in adult male CD rats. Rats were exposed 6-h/day for either 5 days/week (10 exposures) or 7 days/week (14 exposures) to manganese phosphate at 0, 0.03, 0.3, or 3 mg Mn/m3 (MMAD ≅ 1.5 μm). The following tissues collected at the end of the 2-week exposure: plasma, erythrocytes, olfactory bulb, striatum, cerebellum, lung, liver, femur, and skeletal muscle (n = 6 rats/exposure group) were analyzed for manganese content by neutron activation analysis. Intravenous 54MnCl2 tracer studies were also conducted following the 14th exposure (n = 6 rats/concentration), and whole-body gamma spectrometry was performed immediately after injection and at 1, 2, 4, 8, 12, and 16 weeks after 54MnCl2 administration. Increased manganese concentrations were observed in olfactory bulb, lung, femur, and skeletal muscle following exposure to 3 mg Mn/m3 (10 or 14 exposures). Increased manganese concentrations were also observed in olfactory bulb, striatum, and lung following exposure to 0.3 mg Mn/m3 (14 exposures only). Red blood cell and plasma manganese concentrations were increased only in rats exposed to 3 mg Mn/m3 (10 exposures). Rats exposed to 3 mg Mn/m3 also had an increased whole-body manganese clearance rate when compared to air-exposed control animals. Our results suggest that the rat olfactory bulb may accumulate more manganese than other brain regions following inhalation exposure.

Bronchiolo-alveolar tumors were observed in mice exposed chronically to 160 ppm styrene, whereas no tumors were seen in rats up to concentrations of 1000 ppm. Clara cells, which are predominant in the bronchiolo-alveolar region in mouse lungs but less numerous in rat and human lung, contain various cytochrome P450s, which may oxidize styrene to the rodent carcinogen styrene-7,8-oxide (SO) and other reactive metabolites. Reactive metabolites may form specific DNA adducts and induce the tumors observed in mice. To determine DNA adducts in specific tissues and cell types, rats and mice were exposed to 160 ppm [ring-U-(14)C]styrene by nose-only inhalation for 6 h in a recirculating exposure system. Liver and lungs were isolated 0 and 42 h after exposure. Fractions enriched in Type II cells and Clara cells were isolated from rat and mouse lung, respectively. DNA adduct profiles differed quantitatively and qualitatively in liver, total lung, and enriched lung cell fractions. At 0 and 42 h after exposure, the two isomeric N:7-guanine adducts of SO (measured together, HPEG) were present in liver at 3.0 +/- 0.2 and 1.9 +/- 0.3 (rat) and 1.2 +/- 0.2 and 3.2 +/- 0.5 (mouse) per 10(8) bases. Several other, unidentified adducts were present at two to three times higher concentrations in mouse, but not in rat liver. In both rat and mouse lung, HPEG was the major adduct at approximately 1 per 10(8) bases at 0 h, and these levels halved at 42 h. In both rat Type II and non-Type II cells, HPEG was the major adduct and was about three times higher in Type II cells than in total lung. For mice, DNA adduct levels in Clara cells and non-Clara cells were similar to total lung. The hepatic covalent binding index (CBI) at 0 and 42 h was 0.19 +/- 0.06 and 0.14 +/- 0.03 (rat) and 0. 25 +/- 0.11 and 0.44 +/- 0.23 (mouse), respectively. The pulmonary CBIs, based on tissues combined for 0 and 42 h, were 0.17 +/- 0.04 (rat) and 0.24 +/- 0.04 (mouse). Compared with CBIs for other genotoxicants, these values indicate that styrene has only very weak adduct-forming potency. The overall results of this study indicate that DNA adduct formation does not play an important role in styrene tumorigenicity in chronically exposed mice.

Inhalation exposure of humans to high concentrations of manganese (Mn) is associated with elevated Mn levels in the basal ganglia and an extrapyramidal movement disorder. In the rat, direct olfactory transport of Mn from the nose to the brain has been demonstrated following intranasal instillation of (54)MnCl(2). However, the contribution this route makes to brain Mn delivery following inhalation is unknown and was the subject of our study. Male 8-week old CD rats underwent a single 90-min nose-only exposure to a (54)MnCl(2) aerosol (0.54 mg Mn/m(3); MMAD 2.51 microm). The left and right sides of the nose and brain, including the olfactory pathway and striatum, were sampled at 0, 1, 2, 4, and 8 days postexposure. Control rats were exposed to (54)MnCl(2) with both nostrils patent to evaluate the symmetry of Mn delivery. Another group of rats had the right nostril plugged to prevent nasal deposition of (54)MnCl(2) on the occluded side. Gamma spectrometry (n = 6 rats/group/time point) and autoradiography (n = 1 rat/group/time point) were used to compare the levels of (54)Mn found on the left and right sides of the nose and brain to determine the contribution of olfactory uptake to brain (54)Mn levels. Brain and nose samples from the side with the occluded nostril had negligible levels of (54)Mn activity, validating the nasal occlusion procedure. High levels of (54)Mn were observed in the olfactory bulb and tract/tubercle on the side or sides with an open nostril within 1-2 days following inhalation exposure. These results demonstrated, for the first time, that the olfactory route contributes the majority (up to >90%) of the (54)Mn found in the olfactory pathway, but not in the striatum, of the rat brain up to 8 days following a single inhalation exposure. These findings suggest that the olfactory route may make a significant contribution to brain Mn levels following inhalation exposure in the rat.

1,3-Butadiene (butadiene) is a potent carcinogen in mice, but not in rats. Metabolic studies may provide an explanation of these species differences and their relevance to humans. Male Sprague-Dawley rats and B6C3F1 mice were exposed for 6 h to 200 ppm [2,3-14C]-butadiene (specific radioactivity [sa] 20 mCi/mmol) in a Cannon nose-only system. Radioactivity in urine, feces, exhaled volatiles and 14C-CO2 were measured during and up to 42 h after exposure. The total uptake of butadiene by rats and mice under these experimental conditions was 0.19 and 0.38 mmol (equivalent to 3.8 and 7.5 mCi) per kg body weight, respectively. In the rat, 40% of the recovered radioactivity was exhaled as 14C-CO2, 70% of which was trapped during the 6-h exposure period. In contrast, only 6% was exhaled as 14C-CO2 by mice, 3% during the 6-h exposure and 97% in the 42 h following cessation of exposure. The formation of 14C-CO2 from [2,3-14C]-labeled butadiene indicated a ready biodegradability of butadiene. Radioactivity excreted in urine accounted for 42% of the recovered radioactivity from rats and 71% from mice. Small amounts of radioactivity were recovered in feces, exhaled volatiles and carcasses. Although there was a large measure of commonality, the exposure to butadiene also led to the formation of different metabolites in rats and mice. These metabolites were not found after administration of [4-14C]-1,2-epoxy-3-butene to animals by i.p. injection. The results show that the species differences in the metabolism of butadiene are not simply confined to the quantitative formation of epoxides, but also reflect a species-dependent selection of metabolic pathways. No metabolites other than those formed via an epoxide intermediate were identified in the urine of rats or mice after exposure to 14C-butadiene. These findings may have relevance for the prediction of butadiene toxicity and provide a basis for a revision of the existing physiologically based pharmacokinetic models.

Chloroform is a nongenotoxic-cytotoxic liver and kidney carcinogen and nasal toxicant in some strains and sexes of rodents. Substantial evidence indicates that tumor induction is secondary to events associated with cytolethality and regenerative cell proliferation. Therefore, pathways leading to toxicity, such as metabolic activation, become critical information in mechanism-based risk assessments. The purpose of this study was to determine the degree to which chloroform-induced cytotoxicity is dependent on the cytochromes P450 in general and P450 2E1 in particular. Male B6C3F(1), Sv/129 wild-type (Cyp2e1+/+), and Sv/129 CYP2E1 knockout (Cyp2e1-/- or Cyp2e1-null) mice were exposed 6 h/day for 4 consecutive days to 90 ppm chloroform by inhalation. Parallel control and treated groups, excluding Cyp2e1-null mice, also received an i.p. injection (150 mg/kg) of the irreversible cytochrome P450 inhibitor 1-aminobenzotriazole (ABT) twice on the day before exposures began and 1 h before every exposure. Cells in S-phase were labeled by infusion of BrdU via an implanted osmotic pump for 3.5 days prior to necropsy, and the labeling index was quantified immunohistochemically. B6C3F(1) and Sv/129 wild-type mice exposed to chloroform alone had extensive hepatic and renal necrosis with significant regenerative cell proliferation. These animals had minimal toxicity in the nasal turbinates with focal periosteal cell proliferation. Administration of ABT completely protected against the hepatic, renal, and nasal toxic effects of chloroform. Induced pathological changes and regenerative cell proliferation were absent in these target sites in Cyp2e1-/- mice exposed to 90 ppm chloroform. These findings indicate that metabolism is obligatory for the development of chloroform-induced hepatic, renal, and nasal toxicity and that cytochrome P450 2E1 appears to be the only enzyme responsible for this cytotoxic-related metabolic conversion under these exposure conditions.