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Osteosarcoma development following single inhalation exposure to americium-241 in beagle dogs.

Young, mature Beagle dogs underwent single inhalation exposure to respirable aerosols of 241AmO2 to determine the radiation dose distribution to tissues. The dogs were serially sacrificed to assess the clearance of 241Am from the lung, the rate of translocation to internal organs, the pattern of retention in the organs, and the rates and modes of excretion. Americium dioxide was relatively soluble in the lung, leading to the translocation of significant quantities of 241Am to bone and liver, thus delivering radiation doses to these tissues nearly equal to that received by the lung. Osteoblastic osteosarcomas developed in four dogs surviving more than 1000 days after exposure. Histologically, all of the osteosarcomas were associated with areas of radiation osteodystrophy characterized by bone infarction, peritrabecular new bone formation, marrow fibrosis, and microresorptive cavities. The retention and translocation of inhaled 241Am in dogs is similar to that of man, indicating that 241Am inhaled by humans may potentially result in significant risk of bone tumor development.

Americium↗

Subchronic inhalation exposure to acetone vapor and scheduled controlled operant performance in male rats.

Groups of adult male rats (10/group) were used to assess whether subchronic inhalation exposure to 0, 1000, 2000, or 4000 ppm of acetone vapor altered schedule-controlled operant performance. Rats were exposed to acetone vapor for 6 h/day, 5 days/wk, for a 13-wk period. Extensive training prior to the exposure series established a stable baseline of lever-pressing on a multiple fixed-ratio-fixed-interval (FR 20-FI 120 s) schedule of food presentation. Operant sessions occurred prior to each daily exposure to avoid confounding the detection of enduring behavioral effects with transient acute effects. FI response rate, FI index of curvature, and FR running rate of response were not affected during or after the 13-wk exposure series. FR post-reinforcement pause duration for the control group increased during the course of the study more than that of the 2000 ppm and 4000 ppm groups, which changed only slightly relative to pretreatment baseline. Based on the performance of historical controls that had FR pause durations similar to those of acetone-treated groups, the differences in FR pause duration were probably due to drift of the concurrent control group and were not related to acetone treatment. Prolonged exposure to up to 4000 ppm acetone vapor does not appear to have enduring effects on nervous system functions that mediate the performance of a complex, learned task.

Acetone↗

Perfluorooctanoic acid: relationship between repeated inhalation exposures and plasma PFOA concentration in the rat.

A large database exists describing the pharmacokinetic behavior of perfluorooctanoic acid (PFOA) following oral exposure. The objective of this study was to examine the concentration- and time-dependence of the pharmacokinetics of inhaled PFOA in rat plasma to determine equivalent inhalation and oral (from literature values) exposure levels. The study was comprised of two separate experiments: a single 6-h inhalation exposure and repeated inhalation exposures for 3 weeks (6h per day, 5 days per week). In both experiments, male and female rats were exposed nose-only to aerosol atmospheres of either 0, 1, 10, or 25mg/m(3) PFOA. In the single exposure experiment, blood was drawn via the tail vein pre-exposure, four times concurrent to exposure, and six times post-exposure up to 24h. In the repeated exposure experiment, blood was collected immediately before and after exposure 3 days per week. Plasma PFOA concentrations were quantitated by liquid chromatography-mass spectrometry (LC-MS). Following the single exposures, plasma PFOA concentrations were directly proportional to airborne concentrations in both male and female rats. Elimination of PFOA from the plasma was sex-dependent, with female rats eliminating PFOA much more rapidly than male rats. Following repeated PFOA exposure, there was little daily PFOA carryover observed in plasma samples from female rats, while males demonstrated an accumulative pattern over the 3-week period. Peak post-exposure PFOA plasma concentrations in female rats averaged 1, 2, and 4 microg/mL when exposed to 1, 10, and 25mg/m(3) PFOA, respectively, and returned to baseline levels by the time of the next pre-exposure sample collection. Male rats reached steady state plasma concentrations of 8, 21, and 36 microg/mL (ppm) after 3 weeks of exposure to 1, 10, and 25mg/m(3) PFOA, respectively. These results demonstrate that the pharmacokinetic properties of inhaled PFOA in male and female rats are similar to those observed in male and female rats following oral dosing with PFOA. It is thus possible to use this internal dose metric (plasma PFOA) for route-to-route dose extrapolation, with inhalation exposures of 1, 10, and 25mg/m(3) PFOA corresponding to oral doses of approximately 0.3, 1.0, and 2.0mg/kg in rats.

Administration, Inhalation↗

Pulmonary absorption and disposition of [14C]thiophene in rats following nose-only inhalation exposure.

The absorption, disposition, and metabolism of [14C]thiophene was investigated in rats following nose-only inhalation exposure at 8000 ppm for 1 h. Under these exposure conditions, it was estimated that approximately 16.3% (493 mumol) of the inhaled thiophene was absorbed from the respiratory system. Within 72 h following exposure, a total of 488 mumol of thiophene equivalents (99% of that retained) was excreted, of which 360.4 mumol (73.9% of the total excreted radioactivity) was in expired air, 120.7 mumol (24.8%) was in urine, 3 mumol (0.6%) was in feces, and 3.7 mumol (0.8%) was in the cage wash. Excretion took place primarily within the first 8 h, during which 91% of the total radioactivity excreted was collected. The thiophene equivalents remaining in tissues at 72 h were estimated to total 5.1 mumol (1.0% of the retained radioactivity). Exhaled radioactivity was identified as thiophene. No 14CO2 was detected in the expired air. After 1 h following exposure, the elimination of thiophene equivalents from plasma was monophasic, with a half-time of 3.6 h. The elimination of thiophene equivalents from blood cells was biphasic, with half-times of 2.9 h and 9.1 d. The blood cells/plasma concentration ratios of thiophene equivalents ranged from 3 to 13, with the higher ratio observed at the 12-h time interval. At 72 h after exposure, blood cells contained the highest concentration of thiophene equivalents, approximately fourfold higher than that of the liver, which contained the second highest concentration. Kidney, heart, and lung contained similar but lower concentrations than liver, while brain, fat, and skeletal muscles contained the lowest concentrations. In summary, this study demonstrates that thiophene was absorbed from the respiratory system, and the majority of the absorbed thiophene was eliminated unchanged in the exhaled air, while a smaller fraction was metabolized and eliminated in urine.

Absorption↗

POCK model simulations of pulmonary quartz dust retention data in extended inhalation exposures of rats.

In recent years, a physiology-oriented multicompartmental kinetics (POCK) model was developed to simulate pulmonary retention data of biopersistent, noncytotoxic aerosols in long-term inhalation exposures of rats. Experimental data were successfully simulated for submicrometer-sized aerosols like carbon black, diesel soot, and titanium dioxide and for a micrometer-sized xerographic toner aerosol (Stöber et al., 1994, 1995). This article describes for various rat strains successful POCK model simulations of experimental pulmonary retention data of micrometer-sized aerosols of biopersistent cytotoxic SiO2 modifications like quartz and quartzite. In the past, the POCK model was not applied to cytotoxic aerosols and dusts. Cytotoxicity was considered incompatible with the model assumption of a constant macrophage lifetime independent of the macrophage aerosol load. The few relevant experimental retention studies with biopersistent silica found in the open literature showed particulate lung burdens up to some 15 mg per rat lung. Apparently, at these loads, pulmonary burdens could be simulated because the fraction of alveolar macrophages killed by the cytotoxic particles was possibly still small compared to the total number of viable macrophages. Of necessity, however, the classical alveolar clearance in these studies was exclusively performed by alveolar macrophages that were burdened with cytotoxic particles, and the cells appeared to suffer from a substantial initial decrease of their inherent mobility. Thus a sizeable reduction of the alveolar clearance rate coefficient in comparison to nontoxic aerosol was found. The results for the model parameters of several different exposure studies are shown and interpreted in comparison to nontoxic titanium dioxide retention parameters.

Administration, Inhalation↗

Effects of a single inhalative exposure to formaldehyde on the open field behavior of mice.

The effects of formaldehyde on the explorative behavior and locomotor activity of mice after a single inhalative exposure were examined in an open field. Adult male mice were exposed to approximately 1.1 ppm, 2.3 ppm, or 5.2 ppm formaldehyde vapour for 2 hours and the open field test was carried out two hours after the end of exposure (trial 1) and repeated 24 hours thereafter (trial 2). The following behavioral parameters were quantitatively examined: numbers of crossed floor squares (inner, peripheral, total), sniffing, grooming, rearing, climbing, and incidence of fecal boli. The results of the first trial revealed that the motion activity was significantly reduced in all exposed groups. In the 1.1 ppm group, the frequency of rearing was reduced and that of floor sniffing increased. The exposure to the two higher formaldehyde concentrations caused a significant decrease in total numbers of floor squares crossed by the subjects, air sniffing, and rearing. The open field test on the next day (trial 2) showed that the frequencies of floor sniffing, grooming, and rearing in all formaldehyde groups were significantly altered. In the 2.5 ppm group, an increased incidence of fecal boli was observed. From the results obtained, we conclude that the exposure of male mice to formaldehyde vapour affects their locomotor and explorative activity in the open field, and that some open field parameters are still altered in the exposed animals even after 24 hours.

Animals↗

Inhalation toxicity of propineb. Part I: Results of subacute inhalation exposure studies in rats.

This article addresses results from repeated 1- and 4-wk inhalation exposure studies in Wistar rats with solid aerosol (dust) atmospheres of propineb, a zinc bisdithiocarbamate homopolymer that is used as an agrochemical fungicide. Groups of 10 rats/sex were exposed nose-only to mean concentrations of 3.97, 11.24, and 21.95 mg propineb/m(3) using an exposure regimen of 6 h/day, 5 days/wk for 4 wk. Concentrations were selected based on results from a pilot study in which rats were exposed under identical conditions on 5 consecutive days for 6 h/day to mean concentrations of 10.1, 19.9, 38.1, and 78.7 mg/m(3). Both studies demonstrated that with respect to muscular effects female rats were remarkably more susceptible as compared to males. Female rats exposed to 11.24 mg/m(3) and above displayed characteristic signs of toxicity that included weakness and flaccid paralysis of hindlegs and ensuing immobilization that was considered to be the cause of emaciation and ensuing mortality in some rats. There was an apparent reciprocal relationship of concentration and the manifestation of clinical evidence of muscular dysfunction; that is, the onset in female rats exposed to 11.24, 21.95, 38.1, and 78.7 mg/m(3) was on days 15, 8, 4, and 3, respectively. In contrast, none of the male rats elaborated comparable effects up to 38.1 mg/m(3). Neuromuscular measures included leg grip strength and supplemented the clinical findings, whereas the landing foot splay was only minimally affected. Hematology and clinical pathology endpoints, including those addressing thyroidal function, were unobtrusive up to and including 78.7 mg/m(3). Lung weights were significantly increased in groups exposed to 21.95 mg/m(3) and above, especially in male rats. The microscopic examinations made in the 4-wk study demonstrated an increased incidence of intraalveolar material and enlarged, foamy alveolar macrophages at 3.97 mg/m(3) and above. Especially in female rats an atrophy of thigh muscle fibers, including increased nuclei and focal degeneration, occurred at 11.24 mg/m(3) and above. TTCA (2-thiazolidinethione-4-carboxylic acid) in urine, a metabolite and biomarker of exposure to CS(2), which is a putative breakdown product of propineb, was proportionally higher in the female rats exposed to 11.24 mg/m(3) and above. This biomarker appears to accumulate with time. This finding provides indirect evidence that the etiopathologic cause of neuromuscular changes is related to intermediary levels of CS(2). The data of this investigation suggest that the toxicity of inhaled propineb is characterized by two independent effects, namely, responses occurring at the alveolar level and muscular weakness, especially in female rats. With respect to the latter finding, the no-observed-adverse-effect level (NOAEL) of the 4-wk study is 3.97 mg/m(3). Further study is needed to clarify whether the pulmonary response observed at this exposure level is consistent with an adaptive or an early adverse effect.

Administration, Inhalation↗

Levels and sources of personal inhalation exposure to volatile organic compounds.

Personal exposures to VOCs of 12 urban dwellers were measured directly via personal monitoring and indirectly via static monitoring combined with personal activity diaries. Over 5-10 days, day-to-day variations in personal exposures of individuals were substantial, with statistically significant (p<0.05) deviation from the normal distribution observed for daily exposures to one or more VOCs for several subjects. Daytime concentrations generally exceeded night time, with day:night mean concentration ratios for each sampling day >1 for most VOCs, with the maximum (3.85) occurring for 1,3-butadiene. Exposure in the home contributed 50-80% of overall individual exposure to 1,3-butadiene and benzene. For most VOCs, while absolute values of direct and indirect exposure estimates were significantly different (p<0.05), linear regression of direct and indirect exposure estimates revealed statistically significant correlation (p<0.01), confirming previous observations that indirect monitoring can provide satisfactory estimates of personal inhalation exposure to VOCs. ETS, the use of vehicles, and heating (but not cooking) all made appreciable contributions to personal exposure to all target VOCs.

Air Pollutants↗

Relative developmental toxicities of acrylates in rats following inhalation exposure.

The developmental toxicities of seven acrylates were studied in Sprague-Dawley rats after inhalation exposure for 6 h/day, during days 6 to 20 of gestation. The exposure concentrations were: for acrylic acid, 50, 100, 200, or 300 ppm; for methyl acrylate, 25, 50, or 100 ppm; for ethyl acrylate, 25, 50, 100, or 200 ppm; for butyl acrylate, 100, 200, or 300 ppm; for ethylhexyl acrylate, 50, 75, or 100 ppm; for hydroxyethyl acrylate, 1, 5, or 10 ppm; and for hydroxypropyl acrylate, 1, 5, or 10 ppm. No treatment-related increases in embryo/fetal mortality or fetal malformations were observed after exposure to any of these acrylates. Fetal toxicity, indicated by reduced fetal body weight, was observed after exposure to 300 ppm acrylic acid, 100 ppm methyl acrylate, 200 ppm ethyl acrylate, and 200 or 300 ppm butyl acrylate in the presence of overt signs of maternal toxicity. While there was evidence of maternal toxicity, no significant developmental toxic effects were observed after exposure to ethylhexyl acrylate, hydroxyethyl acrylate, or hydroxypropyl acrylate at any concentration. These results indicate that inhaled acrylic acid, methyl acrylate, ethyl acrylate, butyl acrylate, ethylhexyl acrylate, hydroxyethyl acrylate, and hydroxypropyl acrylate are not selectively toxic to the embryo or fetus.

Acrylates↗

Inhalation exposure to respiratory sensitising chemicals down-regulates guinea pig IgE and pulmonary responses.

Inhalation exposure of the guinea pig to the respiratory sensitising chemicals trimellitic anhydride (TMA) or diphenylmethane di-isocyanate down-regulated the IgE antibody response to subsequent systemic challenge with alum-precipitated hapten-protein conjugate. The suppression was isotype and hapten specific, challenge with unrelated hapten-protein conjugate resulting in high-titre IgE and IgGl antibody responses. Preliminary results indicate that the down-regulation of the IgE response to TMA markedly reduced the capacity of the animals to undergo a bronchoconstriction response following challenge with an aerosol of TMA, suggesting that the initial route of exposure may have profound effects upon the development of occupational respiratory allergy.

Administration, Inhalation↗

Bias in air sampling techniques used to measure inhalation exposure.

Factors have been evaluated which contribute to the lack of agreement between inhalation exposure estimates obtained by time-weighted averaging of samples taken with mini hi-volume samplers, and those measured by time integrating, low-volume, lapel mounted, personal monitors. Measurements made with real-time aerosol monitors on workers at a Be-Cu production furnace show that part of the discrepancy results from variability of the aerosol concentration within the breathing zone. Field studies of sampler inlet bias, the influences of the electrostatic fields around polystyrene filter holders, and resuspension of dust from work clothing, were done in three areas of a Be plant. No significant differences were found in Be air concentrations measured simultaneously by open and closed face cassettes, and "mini hi-volume" samplers mounted on a test stand. No significant influence on Be collection was detected between either positively or negatively charged monitors and charge neutralized control monitors. The effect of contaminated work clothing on dust collection by lapel mounted monitors is most important. Beryllium release from the fabrics affected air concentrations measured by fabric mounted monitors more than it affected concentrations measured by monitors positioned above the fabrics. The latter were placed 16 cm from the vertically mounted fabrics, to simulate the position of the nose or mouth. We conclude that dust resuspended from work clothing is the major source of the observed discrepancy between exposures estimated from lapel mounted samplers and time-weighted averages.

Aerosols↗

Modeling accumulations of particles in lung during chronic inhalation exposures that lead to impaired clearance.

Chronic inhalation of insoluble particles of low toxicity that produce substantial lung burdens of particles, or inhalation of particles that are highly toxic to the lung, can impair clearance. This report describes model calculations of accumulations in lung of inhaled low-toxicity diesel exhaust soot and high-toxicity Ga2O3 particles. Lung burdens of diesel soot were measured periodically during a 24-mo exposure to inhaled diesel exhaust at soot concentrations of 0, 0.35, 3.5, and 7 mg m-3, 7 h d-1, 5 d wk-1. Lung burdens of Ga2O3 were measured for 1 y after a 4-wk exposure to 23 mg Ga2O3 m-3, 2 h d-1, 5 d wk-1. Lung burdens of Ga2O3 were measured for 1 y both studies using inhaled radiolabeled tracer particles. Simulation models fit the observed lung burdens of diesel soot in rats exposed to the 3.5- and 7-mg m-3 concentrations of soot only if it was assumed that clearance remained normal for several months, then virtually stopped. Impaired clearance from high-toxicity particles occurred early after accumulations of a low burden, but that from low-toxicity particles was evident only after months of exposure, when high burdens had accumulated in lung. The impairment in clearances of Ga2O3 particles and radiolabeled tracers was similar, but the impairment in clearance of diesel soot and radiolabeled tracers differed in magnitude. This might have been related to differences in particle size and composition between the tracers and diesel soot. Particle clearance impairment should be considered both in the design of chronic exposures of laboratory animals to inhaled particles and in extrapolating the results to people.

Administration, Inhalation↗

Developmental toxic effects of ethylbenzene or toluene alone and in combination with butyl acetate in rats after inhalation exposure.

First, the developmental toxic potential of n-butyl acetate (BA) was examined in Sprague-Dawley rats following whole body inhalation exposure, 6 h day(-1), from day 6 to 20 of gestation, at concentrations of 0, 500, 1000, 2000 and 3000 ppm. Maternal toxicity was evidenced by significant decreases in body weight gain at 2000 and 3000 ppm, and by reduced food consumption at 1000 ppm and higher concentrations. The effects on prenatal development were limited to a significant decrease in fetal weight at 3000 ppm. Thus, inhaled BA was not a selective developmental toxicant. In the second part of this study, the developmental toxic effects of simultaneous exposures to ethylbenzene (EB) and BA, or to toluene (TOL) and BA were evaluated. Pregnant rats were administered EB (0, 250 or 1000 ppm) and BA (0, 500 or 1500 ppm), or TOL (0, 500 or 1500 ppm) and BA (0, 500, 1500 ppm), separately and in combinations, using a 2 x 2 factorial design. The maternal weight gain was reduced after exposure to 1000 ppm EB, to 1500 ppm BA, or to 1500 ppm TOL, either alone or in binary combinations. A significant reduction of fetal weight was associated with exposure to 1000 ppm EB alone, to either mixtures of EB with BA, or to 1500 ppm TOL alone or combined with BA at either concentration. No embryolethal or teratogenic effects were observed whatever the exposure. There was no evidence of interaction between EB and BA or between TOL and BA in causing maternal or developmental effects.

Abnormalities, Drug-Induced↗

Some biotransformation enzymes responsible for polycyclic aromatic hydrocarbon metabolism in rat nasal turbinates: effects on enzyme activities of in vitro modifiers and intraperitoneal and inhalation exposure of rats to inducing agents.

Respiratory tract biotransformation of many xenobiotics found in inhaled environmental pollutants is generally considered essential for the mutagenic, carcinogenic, and/or toxic response of lung tissue to these xenobiotics. Typical environmental pollutants contain known carcinogens adsorbed onto particles which can deposit in the nasal pharyngeal region of the respiratory tract. The purpose of this study was to characterize the metabolic capacity of rat nasal tissue. Both oxidative and nonoxidative enzyme activities were investigated which included aryl hydrocarbon hydroxylase (AHH), epoxide hydrolase (EH), uridine 5'-diphosphate-glucuronyltransferase (UDPGT), and glutathione transferase. Specific enzyme activities of AHH, EH, UDPGT, and glutathione transferase were 0.023, 6.4, 20.4, and 24.8 nmol product per mg protein per min, respectively. Benzo(a)pyrene was metabolized by AHH to dihydrodiols, quinones, and phenols in quantities which were about 10 times greater than those reported for rat lung microsomes. Small, but detectable, quantities of benzo(a)pyrene tetrols were also measured in reaction flasks in which rat nasal tissue was incubated with benzo(a)-pyrene. Attempts to increase the microsomal enzyme activities of AHH, EH, and UDPGT by pretreating rats with various inducing agents by both i.p. injection (phenobarbital, 3-methylcholanthrene, Aroclor 1254, and 2,3,7,8-tetrachlorodibenzo-p-dioxine) and inhalation exposure (BaP) resulted in rat nasal monooxygenases only being induced (2-fold) after pretreatment with 2,3,7,8-tetrachlorodibenzo-p-dioxine. Phenobarbital increased enzyme activities of EH and UDPGT by about 50%. These data suggest that rat nasal tissue may contain multiple forms of cytochrome P-450 and of EH and UDPGT. The results from this study support the notion that nasal tissue may be important in determining the metabolic fate of inhaled xenobiotics.

Animals↗

Degeneration and regeneration of the olfactory epithelium following inhalation exposure to methyl bromide: pathology, cell kinetics, and olfactory function.

The effects of acute inhalation exposure to methyl bromide (MeBr) on the olfactory epithelium of male F-344 rats was investigated by morphologic examination of animals killed at varying timepoints during and following exposure to 200 ppm MeBr 6 hr/day for 5 days. Cell replication rate and histopathology were used to assess the kinetics of repair. In addition, olfactory function, using the buried food pellet test, was assessed and the result compared with morphological recovery. Extensive destruction of the olfactory epithelium was evident in animals killed directly after a single 6-hr exposure to MeBr. Histologic features of these lesions indicate that the primary, or most severe, effect of MeBr exposure was on the sustentacular cells and mature sensory cells; basal cells were generally unaffected. By Day 3, despite continued exposure, there was replacement of the olfactory epithelium by a squamous cell layer that increased in thickness and basophilic cytoplasmic staining over the next 2 days of exposure. One week postexposure, the epithelial region was covered by a layer of polyhedral, basophilic cells, and from 2 to 10 weeks postexposure, the epithelium exhibited progressive reorganization to reform the original olfactory epithelium pattern. By Week 10, 75-80% of the olfactory epithelium appeared morphologically normal. Cell replication showed a single peak of olfactory epithelial cell proliferation at Day 3 of exposure, with a labeling index of 14.5% compared to 0.7% in controls. Cell replication rates returned gradually to control levels by Week 10 postexposure. Behavioral tests of olfactory function in animals after a single 6-hr exposure to 200 ppm MeBr demonstrated a loss of the sense of smell, with recovery of this function by Day 6. Exposure to 90 ppm caused no observable effect on olfactory function or morphology. These findings demonstrate that the olfactory mucosa is highly sensitive to the toxic effects of MeBr and that olfactory epithelial cell proliferation, and possible regeneration, begins and occurs rapidly even in the face of continued exposure. Cell replication was most prominent in the layer of basal cells adjacent to the basal lamina, supporting proposals by other workers that the progenitors of both sustentacular cells and neurons reside in this location. Of interest is the fact that functional recovery occurs prior to complete morphological reorganization, indicating the shortcoming of utilizing olfactory morphology as an index of functional integrity.

Administration, Inhalation↗

The influence of sarin on various physiological functions in rats following single or repeated low-level inhalation exposure.

Long-term effects of low doses of highly toxic organophosphorus agent sarin on various hematological and biochemical markers and physiological functions were studied in rats exposed to sarin by inhalation. The results indicate that low-level sarin-exposed rats show long-term increase in studied markers of stress and decrease in synthesis of DNA de novo without the disturbance of the functions of cholinergic nervous system. Moreover, sarin at low doses is able to induce some neurotoxic effects including an increase in the excitability of central nervous system in rats at 3 mo following inhalation exposure. Relatively long-term spatial discrimination impairments in rats exposed to low-level sarin was demonstrated too. Therefore, nerve agents such as sarin seem to be harmful not only at high, clinically symptomatic doses but also at low doses without acute clinical manifestation of overstimulation of cholinergic nervous system because of long-term manifestation of alteration of neurophysiological and neurobehavioral functions in sarin-exposed rats.

Administration, Inhalation↗

Nasal tumors in rats following long-term inhalation exposure to 1,4-dichlorobutene-2 (DCB).

This study was conducted to elucidate the time- and dose-response relationships of long-term, low-level 1,4-dichlorobutene-2 (DCB) inhalation exposure to nasal tumor induction in rats. Male Crl:CD BR rats were exposed 6 hours per day, 5 days week to 0, 0.1, 0.3, or 1.0 ppm DCB for up to 19 months; some rats were sacrificed at various time intervals during the study. After 19 months of exposure, surviving rats were held without treatment for an additional 5 months. Tissues from the respiratory tract, lymph nodes, and brain were evaluated microscopically. Compound-related non-neoplastic lesions were observed in the nasal cavities of rats in the 1.0 ppm group after three months of exposure and in the other two groups after twelve months of exposure. The lesions were progressive in severity and frequency. A statistically significant increase in benign nasal tumors (adenomas) occurred in rats from all three DCB-exposed groups. The adenomas occurred in the respiratory region of the nasal cavity and were first observed in the 1.0 ppm group at study month 10. Malignant nasal tumors occurred in the olfactory region of the nasal cavity and were statistically increased at 1.0 ppm.

Adenocarcinoma↗

Combustion-derived nanoparticles: a review of their toxicology following inhalation exposure.

This review considers the molecular toxicology of combustion-derived nanoparticles (CDNP) following inhalation exposure. CDNP originate from a number of sources and in this review we consider diesel soot, welding fume, carbon black and coal fly ash. A substantial literature demonstrates that these pose a hazard to the lungs through their potential to cause oxidative stress, inflammation and cancer; they also have the potential to redistribute to other organs following pulmonary deposition. These different CDNP show considerable heterogeneity in composition and solubility, meaning that oxidative stress may originate from different components depending on the particle under consideration. Key CDNP-associated properties of large surface area and the presence of metals and organics all have the potential to produce oxidative stress. CDNP may also exert genotoxic effects, depending on their composition. CDNP and their components also have the potential to translocate to the brain and also the blood, and thereby reach other targets such as the cardiovascular system, spleen and liver. CDNP therefore can be seen as a group of particulate toxins unified by a common mechanism of injury and properties of translocation which have the potential to mediate a range of adverse effects in the lungs and other organs and warrant further research.

Journal Article↗