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Physiologically based estimation of in vivo rates of bromodichloromethane metabolism.

Bromodichloromethane (BDCM) is a rodent carcinogen formed by chlorination of drinking water containing bromide and organic precursors. BDCM is a member of the class of disinfection by-products known as trihalomethanes (THMs), compounds that have been shown to be carcinogenic in rodents. A physiologically-based pharmacokinetic (PBPK) model has been developed and applied to provide estimates of the rates of metabolism of BDCM in vivo in rats. The model consists of five compartments (liver, kidney, fat and slowly and rapidly perfused tissues). Tissue partition coefficients were determined using a modified vial equilibration technique and rates of metabolism were estimated by fitting data obtained from stable metabolite (bromide ion, (Br-)) analysis following 4 h constant concentration BDCM inhalation exposure (50-3200 ppm) and closed chamber gas uptake experiments. Metabolism was described using a single saturable pathway representing a high capacity, high affinity process (Vmaxc = 12.8 mg/h/kg; Km = 0.5 mg/l). Rate constants obtained from Br- data adequately described data from gas uptake experiments and literature data on exhalation of 14CO and 14CO2 produced following oral gavage with 14C-BDCM. Pretreatment with trans-dichloroethylene (t-DCE), an inhibitor of CYP2E1, increased the apparent Km from 0.5 to 225 mg/l indicating that CYP2E1 is the major P450 isoform involved in the bioactivation of BDCM to reactive intermediates.

Animals↗

NTP Toxicology and Carcinogenesis Studies of Nickel Subsulfide (CAS No. 12035-72-2) in F344 Rats and B6C3F1 Mice (Inhalation Studies).

Nickel subsulfide is used in the manufacture of lithium batteries and is a major component in the refining of certain nickel ores. Nickel subsulfide was nominated as part of a class study of nickel compounds, for which there was little information on the toxic and carcinogenic effects of inhalation exposure. Male and female F334/N rats and B6C3F1 mice were exposed to nickel subsulfide (at least 97% pure; the mean value for the mass median aerodynamic diameter at each exposure concentration ranged from 2.0 to 2.2 mm by inhalation 6 hours per day, 5 days per week, for 16 days, 13 weeks, or 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium, and mouse peripheral blood samples were analyzed for frequency of micronucleated normochromatic erythrocytes. 16-DAY STUDY IN RATS: Groups of five male and five female F344/N rats were exposed to atmospheres containing 0, 0.6, 1.2, 2.5, 5, or 10 mg nickel subsulfide/m(3) (equivalent to 0, 0.44, 0.88, 1.83, 3.65, and 7.33 mg nickel/m(3)) 6 hours per day, 5 days per week for a total of 12 exposure days during a 16-day period. Additionalmgroups of three male and three female rats were exposed to 0, 0.6, 2.5, or 10 mg/m(3) for tissue burden studies. One male exposed to 10 mg nickel subsulfide/m(3) in the core study died on day 14; all other rats survived until the end of the study. Final mean body weights and mean body weight gains of males exposed to 5 or 10 mg nickel subsulfide/m(3) and females exposed to 2.5, 5, or 10 mg/m(3) were significantly lower than those of the controls. Clinical findings of toxicity on day 5 of the study included labored respiration in 10 mg/m(3) males and 5 and 10 mg/m(3) females and dehydration in 5 and 10 mg/m(3) females. Absolute and relative lung weights of 2.5, 5, and 10 mg/m(3) males and all exposed groups of females were significantlymgreater than those of the controls, as was the absolute lung weight of 1.2 mg/m(3) males. Inflammation of the lung and atrophy of the nasal olfactory epithelium occurred in all exposed mgroups. The concentrations of nickel in the lungs of exposedmgroups of rats increased with exposure concentration (males, 7 to 67 mg nickel/g lung; females, 9 to 77 mg/g lung). 16-DAY STUDY IN MICE: Groups of five male and five female B6C3F1 mice were exposed to atmospheres containing 0, 0.6, 1.2, 2.5, 5, or 10 mg nickel subsulfide/m(3) for 6 hours per day, 5 days per week for a total of 12 exposure days during a 16-day period. Additional groups of three male and three female mice were exposed to 0, 0.6, 2.5, or 10 mg/m(3) for tissue burden studies. All male and female mice exposed to 10 mg nickel subsulfide/m(3) in the core study died before the end of the study; the death of one female was accidental. One control male, one control female, and one 1.2 mg/m(3) male also died before the end of the study. Final mean body weights and mean body weight gains of 5 mg/m(3) males were significantly lower than those of the controls. Clinical findings at day 5 included labored respiration in 10 mg/m(3) males and females. The absolute lung weight of 5 mg/m(3) males, the absolute and relative lung weights of 10 mg/m(3) males and 5 mg/m(3) females, and the relative lung weight of 10 mg/m(3) females were significantly greater than those of the controls. Inflammation of the lung occurred in 2.5, 5, and 10 mg/m(3) male and female mice, fibrosis of the lung occurred in 5 mg/m(3) males and females, and lymphoid hyperplasia of the bronchial lymph nodes and atrophy of the nasal olfactory epithelium occurred in 1.2, 2.5, 5, and 10 mg/m(3) males and females. Nickel concentrations in the lung of exposed male and female mice were greater than those of the controls (males, 10 to 20 mg nickel/g lung; females, 8 to 20 mg/g lung) 13-WEEK STUDY IN RATS: Groups of 10 male and 10 female F344/N rats were exposed to atmospheres containing 0, 0.15, 0.3, 0.6, 1.2, or 2.5 mg nickel subsulfide/m(3) (equivalent to 0, 0.11, 0.22, 0.44, 0.88, and 1.83 mg nickel/m(3)) 6 hours per day, 5 days per week for 13 weeks. Additional groups of 18 male and 18 female female rats were exposed to 0, 0.15, 0.6, or 2.5 mg/m(3) for tissue burden studies. All core study rats survived until the end of the study. Final mean body weights and mean body weight gains of 2.5 mg/m(3) males were significantly lower than those of the controls; final mean body weights of all other exposure groups were similar to those of the controls. Chemical-related clinical findings included labored respiration in 2.5 mg/m(3) males and females during weeks 2 through 7. In general, neutrophil and erythrocyte counts, hematocrit values, and hemoglobin concentrations were minimally increased in exposed rats. Absolute and relative lung weights of all exposed groups were significantly greater than those of the controls. Increases in the number of alveolar macrophages, interstitial infiltrates, or incidences of chronic inflammation of the lung occurred in all groups exposed to nickel subsulfide concentrations of 0.3 mg/m(3) or greater; the severity of these lesions generally increased with increasing exposure concentration. Increases in the number of alveolar macrophages were observed in 0.15 mg/m(3) males and females. Lymphoid hyperplasia of the bronchial and mediastinal lymph nodes was observed in rats exposed to 0.3 mg/m(3) or greater. Most 0.6, 1.2, and 2.5 mg/m(3) males and females had atrophy of the nasal olfactory epithelium, and the severity generally increased with increasing exposure concentration. Nickel concentrations in the lung increased with exposure concentration and were greater than those in the controls in rats exposed for 13 weeks (males, 5 to 18 mg nickel/g lung; females, 5 to 17 mg/g lung). 13-WEEK STUDY IN MICE: Groups of 10 male and 10 female B6C3F1 mice were exposed to atmospheres containing 0, 0.15, 0.3, 0.6, 1.2, or 2.5 mg nickel subsulfide/m(3) for 6 hours per day, 5 days per week for 13 weeks. Additional groups of six male and six female mice were exposed to 0, 0.15, 0.6, or 2.5 mg/m(3) for tissue burden studies. Final mean body weights of all exposure groups were similar to those of the controls. No chemical-related clinical findings were observed. Lymphocyte counts in 1.2 and 2.5 mg/m(3) males were minimally greater than that of the controls. Hemoglobin concentrations and erythrocyte counts in 0.3, 0.6, 1.2, and 2.5 mg/m(3) females were minimally greater than those of the controls. Absolute and relative lung weights of 1.2 and 2.5 mg/m(3) males and females were significantly greater than those of the controls. An increase in alveolar macrophages was present in mice from the 0.3 mg/m(3) and higher exposure groups. Chronic inflammation and fibrosis were observed in the lung of 1.2 and 2.5 mg/m(3) males and females. Interstitial infiltrates of lymphocytes were observed in mice exposed to 0.6, 1.2, or 2.5 mg/m(3). Lymphoid hyperplasia of the bronchial lymph nodes was observed in groups exposed to 1.2 or 2.5 mg/m(3). Atrophy of the nasal olfactory epithelium occurred in 0.6, 1.2, and 2.5 mg/m(3) males and females, and incidences and severity generally increased with increasing exposure concentration. At 13 weeks, nickel concentrations in the lungs of exposed mice were greater than those of the controls (males, 3 to 17 g nickel/g lung; females, 6 to 23 mg/g lung), and these concentrations increased with increasing exposure concentration. 2-YEAR STUDY IN RATS: Survival, Body Weights, Clinical Findings, and Hematology: Groups of 63 male and 63 female F344/N rats were exposed to 0, 0.15, or 1 mg nickel subsulfide/m(3) (equivalent to 0, 0.11, or 0.73 mg nickel/m(3)) by inhalation for 6 hours per day, 5 days per week for 104 weeks. Survival of exposed males and female rats was similar to that of the controls. Mean body weights of males and females exposed to 0.15 mg/m(3) were similar to those of the controls. Mean body weights of rats exposed to 1 mg/m(3) were lower than those of the controls throughout the second year of the study. Chemical-related clinical findings included rapid and shallow breathing following exposure periods. Hematocrit values and hemoglobin concentrations in 1 mg/m(3) males and females and the erythrocyte count in 1 mg/m(3) males were mildly greater than those in the controls. Pathology Findings: In general, the absolute and relative lung weights of exposed males and females were significantly greater than those of the controls at 7 and 15 months. There were exposure-related increases in the incidences of alveolar/bronchiolar adenoma in males, alveolar/bronchiolar carcinoma in males and females, and alveolar/bronchiolar adenoma or carcinoma (combined) in males and females at 2 years. Nonneoplastic lung lesions generally observed in exposed males and females included fibrosis; chronic active inflammation; focal alveolar epithelial hyperplasia, macrophage hyperplasia, and proteinosis; bronchial lymphoid hyperplasia; and interstitial inflammation. At 2 years, there were significant exposure-related increases in the incidences of benign pheochromocytoma, malignant pheochromocytoma, and benign or malignant pheochromocytoma (combined) in males and of benign pheochromocytoma in females. The incidence of adrenal medulla hyperplasia in 1 mg/m(3) females was significantly greater than that of the controls At 2 years, the incidences of chronic active inflammation of the nose in 1 mg/m(3) females and of olfactory epithelial atrophy in 1 mg/m(3) males and females were significantly greater than those of the controls. The incidences of lymphoid hyperplasia of the bronchial lymph node in exposed males at 7 and 15 months and in exposed males and females at 2 years were significantly greater than those of the controls. Incidences of macrophage hyperplasia in the bronchial lymph node of exposed males at 15 months and exposed males and females at 2 years were greater than those of the controls. Tissue Burden Analyses: Nickel concentrations in the lungs of exposed rats were greater than those of the controls at 7 months (males, 6 to 9 mg nickel/g lung; females, 6 to 9 mg/g lung) and 15 months (males, 4 to 3 mg nickel/g lung; females, 4 to 7 mg/g lung). 2-YEAR STUDY IN MICE: Survival, Body Weights, Clinical Findings, and Hematology: Groups of 80 male and 80 female B6C3F1 mice were exposed to 0, 0.6, or 1.2 mg nickel subsulfide/m(3) (equivalent to 0, 0.44, or 0.88 mg nickel/m(3)) by inhalation for 6 hours per day, 5 days per week for 105 weeks. Survival of exposed male and female mice was similar to that of the controls. Mean body weights of 0.6 and 1.2 mg/m(3) males and females were less than those of the controls throughout the second year of the study. Chemical-related clinical findings in male and female mice included labored respiration following exposure periods. The hematocrit value and the segmented neutrophil, monocyte, lymphocyte, and total leukocyte counts in 1.2 mg/m(3) females were greater than those in the controls. Pathology Findings: Absolute and relative lung weights of exposed males and females were generally significantly greater than those of the controls at 7 and 15 months. The incidence of alveolar/bronchiolar carcinoma in 0.6 mg/m(3) females and the incidences of alveolar/bronchiolar adenoma or carcinoma (combined) in 0.6 mg/m(3) males and 0.6 and 1.2 mg/m(3) females were significantly less than those of the controls. In general, the incidences of chronic active inflammation; bronchialization (alveolar epithelial hyperplasia), macrophage hyperplasia and proteinosis; interstitial infiltration; and fibrosis in exposed groups of males and females were greater than those of the controls at 7 and 15 months and at 2 years. The incidences of atrophy of the nasal olfactory epithelium and inflammation of the nose in exposed mice were also generally greater than those of the controls. At 2 years, the incidences of degeneration of olfactory epithelium in exposed females were significantly less than that of the controls. The incidences of lymphoid hyperplasia of the bronchial lymph node in 1.2 mg/m(3) males at 15 months, in 0.6 and 1.2 mg/m(3) females at 15 months, and in 0.6 and 1.2 mg/m(3) males and females at 2 years were significantly greater than those of the controls. The incidences of macrophage hyperplasia in 1.2 mg/m(3) males at 7 and 15 months, in 0.6 and 1.2 mg/m(3) females at 15 months, and in 0.6 and 1.2 mg/m(3) males and females at 2 years were significantly greater than those of the controls. Tissue Burden Analyses: Nickel concentrations in the lungs of exposed mice were greater than those of the controls at 7 months (males, 10 to 11 mg nickel/g lung; females, 10 to 14 mg/g lung) and 15 months (males, 12 to 20 mg nickel/g lung; females, 15 to 26 mg/g lung). GENETIC TOXICOLOGY: Nickel subsulfide was considered to be equivocal in the Salmonella gene mutation assay overall. Sporadic weakly positive and equivocal responses were obtained in strain TA100 with and without S9 metabolic activation enzymes; all other strain/activation combinations gave negative results. No increase in the frequency of micronucleated erythrocytes was observed in peripheral blood samples from male or female mice exposed to nickel subsulfide by inhalation for 13 weeks. CONCLUSIONS: Under the conditions of these 2-year inhalation studies, there was clear evidence of carcinogenic activity of nickel subsulfide in male F344/N rats based on increased incidences of alveolar/bronchiolar adenoma, carcinoma, and adenoma or carcinoma (combined) and on increased incidences of benign, malignant, and benign or malignant (combined) pheochromocytoma of the adrenal medulla. There was clear evidence of carcinogenic activity of nickel subsulfide in female F344/N rats based on increased incidences of alveolar/bronchiolar carcinoma and alveolar/bronchiolar adenoma or carcinoma (combined) and an increased incidence of benign pheochromocytoma of the adrenal medulla. There was no evidence of carcinogenic activity of nickel subsulfide in male or female B6C3F1 mice exposed to 0.6 or 1.2 mg/m(3). Exposure of male and female rats to nickel subsulfide by inhalation for 2 years resulted in inflammation, hyperplasia, and fibrosis in the lung; inflammation and atrophy of the olfactory epithelium in the nose; and hyperplasia in the adrenal medulla (females). Exposure of male and female mice to nickel subsulfide by inhalation for 2 years resulted in inflammation, bronchialization, hyperplasia, and fibrosis in the lung and inflammation and atrophy of the olfactory epithelium in the nose. Synonyms: Heazlewoodite, nickel subsulphide, nickel sulfide (3:2), a-nickel sulfide (3:2) crystalline, nickel sulphide, nickel tritadisulphide, trinickel disulfide

Journal Article↗

Protective effect of equine butyrylcholinesterase in inhalation intoxication of rats with sarin: determination of blood and brain cholinesterase activities.

The effect of pretreatment with equine butyrylcholinesterase (EqBuChE) on cholinesterase inhibition in the blood and brain of rats following inhalation intoxication with low concentrations (1.25 microg/L for 60 min) of sarin were studied. Animals pretreated with different doses of equine butyrylcholinesterase showed significant increases in plasma butyrylcholinesterase activity. However, erythrocyte acetylcholinesterase activity was unchanged. The decrease in acetylcholinesterase and butyrylcholinesterase activity after inhalation intoxication was dependent on the dose of equine butyrylcholinesterase used for pretreatment and was always greater for erythrocyte acetylcholinesterase. Acetylcholinesterase activity in different brain regions was unchanged following pretreatment with equine butyrylcholinesterase. After inhalation exposure to sarin, acetylcholinesterase activity was diminished markedly in the pontomedullar area (51.5% of normal activity) and frontal cortex (72.0% of normal activity), and slightly in basal ganglia (91.4% of normal activity). Plasma levels of sarin were determined using fluoride-induced reactivation of inhibited enzyme. As expected, the amounts of sarin in plasma were almost identical in rats pretreated with EqBuChE as well as in untreated rats. In pretreated animals, the plasma amount of sarin did not depend on the dose of equine butyrylcholinesterase used for pretreatment. Our results demonstrate that equine butyrylcholinesterase pretreatment can be considered as an effective prophylaxis against nerve agents (at least with sarin) and seems to be an alternative or superior to prophylaxis provided by reversible cholinesterase inhibitors.

Administration, Inhalation↗

The flow-past chamber: an improved nose-only exposure system for rodents.

We have designed a nose-only inhalation exposure chamber in which fresh aerosol is flowed past each exposure port and exhaled air is immediately exhausted. This allows all animals in the chamber to be exposed to the same aerosol concentration. In tests comparing initial lung burdens (ILB) of animals exposed in a standard chamber with those of animals exposed in the flow-past chamber, coefficients of variation in ILBs were significantly smaller for the latter.

Aerosols↗

Exposure and risks from wearing asbestos mitts.

BACKGROUND: Very high fibre inhalation exposure has been measured while people were wearing personal protective equipment manufactured from chrysotile asbestos. However, there is little data that relates specifically to wearing asbestos gloves or mitts, particularly when used in hot environments such as those found in glass manufacturing. The aim of this study was to assess the likely personal exposure to asbestos fibres when asbestos mitts were used. RESULTS: Three types of work activity were simulated in a small test room with unused mitts and artificially aged mitts. Neither pair of mitts were treated to suppress the dust emission. The measured respirable fibre exposure levels ranged from <0.06 to 0.55 fibres/ml, with no significant difference in fibre exposure between aged and unused mitts. The use of high localised ventilation to simulate convective airflows from a furnace reduced exposure levels by about a factor of five. Differences between tasks were statistically significant, with simulated "rowing" of molten glass lowest and replacement of side seals on the furnace highest. Estimated lifetime cancer risk from 20 years exposure at the upper end of the exposure range measured during the study is less than 22 per 100,000. CONCLUSION: People who wore asbestos mitts were likely to have been exposed to relatively low levels of airborne chrysotile asbestos fibres, certainly much lower than the standards that were accepted in the 1960's and 70's. The cancer risks from this type of use are likely to be very low.

Journal Article↗

Interstitial lung disease: causes, treatment, and prevention.

The interstitial lung diseases (ILD) are a diverse group of lung disorders that involve primarily the parenchyma of the lung. Whether idiopathic or secondary to systemic disorders, inhaling exposures, or drugs, they inflame and scar the interstitium of the lungs and obliterate alveoli and capillary units. The scarring or fibrosis produces restrictive lung impairment while destruction of the alveoli, interstitium, and capillaries results in severe gas exchange abnormalities. Clinically, the ILD present subtly with progressive dyspnea on exertion and a dry cough. Rales or crackles on examination prompt chest radiography that may reveal bilateral infiltrates. These infiltrates are often treated as atypical pneumonias that fail to respond to antimicrobial therapy over weeks to months. Because of this and their infrequent presentation in the primary care setting, the diagnosis of ILD is commonly delayed. This paper highlights the natural history of the ILD in general, gives a broad overview of the pathophysiology in these diseases, and encourages greater awareness for the detection of ILD in primary care.

Biopsy↗

Health hazards of welding fumes.

Even in the twenty-first century, welding is still a common and a highly skilled occupation. The hazardous agents associated with welding processes are acetylene, carbon monoxide, oxides of nitrogen, ozone, phosgene, tungsten, arsenic, beryllium, cadmium, chromium, cobalt, copper, iron, lead, manganese, nickel, silver, tin, and zinc. All welding processes involve the potential hazards for inhalation exposures that may lead to acute or chronic respiratory diseases. According to literature described earlier it has been suggested that welding fumes cause the lung function impairment, obstructive and restrictive lung disease, cough, dyspnea, rhinitis, asthma, pneumonitis, pneumoconiosis, carcinoma of the lungs. In addition, welding workers suffer from eye irritation, photokeratitis, cataract, skin irritation, erythema, pterygium, non-melanocytic skin cancer, malignant melanoma, reduced sperm count, motility and infertility. Most of the studies have been attempted previously to evaluate the effects of welding fumes. However, no collectively effort illuminating the general effects of welding fumes on different organs or systems or both in human has not been published. Therefore, the aim of this review is to gather the potential toxic effects of welding fumes documented by individual efforts and provide informations to community on hazards of welding.

Air Pollutants, Occupational↗

Occupational obstructive airway diseases in Germany: Frequency and causes in an international comparison.

BACKGROUND: Occupational inhalative exposures contribute to a significant proportion of obstructive airway diseases (OAD), namely chronic obstructive pulmonary disease (COPD) and asthma. METHODS: The number of occupational OAD in the German industrial sector for the year 2003 are presented. Other analyses of surveillance data were retrieved from Medline. RESULTS: Most confirmed reports of OAD are cases of sensitizer induced occupational asthma (625 confirmed cases) followed by COPD in coal miners (414 cases), irritant induced occupational asthma (156 cases), and isocyanate asthma (54 cases). Main causes of occupational asthma in Germany comprise flour/flour constituents (35.9%), food/feed dust (9.0%), and isocyanates (6.5%). Flour and grain dust is a frequent cause of occupational asthma in most European countries and South Africa. Isocyanates are still a problem worldwide. CONCLUSIONS: Although wide differences in the estimated incidences between countries exist due to deficits in the coverage of occupational OAD, the high numbers necessitate improvement of preventive measures.

Asthma↗

Glutathione depletion in lung cells by low-molecular-weight aldehydes.

Use of oxygenates in gasoline in the United States may increase atmospheric levels of aldehydes. To assist in health assessments of inhalation exposure to aldehydes, we studied glutathione (GSH) depletion by low-molecular-weight n-alkanals and 2-alkenals, ubiquitous air pollutants, in adult rat lung (ARL) cells by laser cytometry. For each homologous series, the effective aldehyde concentration that depleted GSH by 50% (EC50) in ARL cells correlates with published values for the median lethal dose of the chemicals and with Hammett/Taft electronic parameters, sigma* for n-alkanals and sigma(+)p for 2-alkenals. n-Alkanals (EC50, 110-400 mmol/L) were 1000 times less effective in depleting GSH than were 2-alkenals (EC50, 2-180 micromol/L), of which acrolein was the most potent. Ability of the 2-alkenals to deplete GSH follows the second-order rate constant for adduct formation. Ability of n-alkanals to deplete GSH follows chain length. Within a homologous series of low-molecular-weight aldehydes, structure-activity relationships are useful for predicting the toxicity of the aldehydes in vitro and in vivo.

Air Pollutants↗

Characteristics and health impacts of volatile organic compounds in photocopy centers.

This study investigates the indoor air quality of typical photocopy centers in Taiwan to evaluate the human health risk following inhalation exposure. Both personal and area samplings were conducted at seven photocopy centers in the Tainan area from July 2002 to March 2003, which covered both summer and winter seasons in Taiwan. The benzene, toluene, ethylbenzene, xylenes, and styrene (BTEXS) measurements indicated no difference between personal and area samplings (P>0.05) and found that air conditioning improves indoor air quality. The additive factor at each photocopy center was significantly below 1.0, based on the current BTEXS permissible exposure limits in Taiwan. However, the mean benzene and styrene levels in the current study were 138 and 18 times, respectively, higher than those in another study conducted in the United States. Comparison of mass ratios of BTEXS with those of several chamber studies revealed that the photocopier is not the only volatile organic compound (VOC) source in photocopy centers. The lifetime cancer and noncancer risks for workers exposed to VOCs were also assessed. Results show that all seven centers in this study had a lifetime cancer risk exceeding 1x10(-6) (ranging from 2.5x10(-3) to 8.5x10(-5)). Regarding noncancer risk, levels of toluene, ethylbenzene, xylenes, and styrene were below the reference levels in all photocopy centers; however, the hazard indices for all still exceeded 1.0 (range 26.2-1.8) because of the high level of benzene in the photocopy centers.

Adult↗

Developmental toxicity study of tetramethylurea (TMU) in rats.

The developmental toxicity of tetramethylurea (TMU) was assessed in rats by inhalation exposure of the test material over days 6-20 of gestation. Groups of 25 mated female Crl:CD BR rats were exposed whole-body for 6 hours/day to concentrations of either 0, 2, 20 or 100 ppm TMU. The dams were euthanized on day 21 and the offspring were weighted, sexed, and examined for external, visceral, and skeletal alterations. Maternal toxicity was demonstrated at both 20 and 100 ppm. Maternal body weights, weight changes, and food consumption were statistically significantly reduced at these concentrations; effects were more pronounced at 100 ppm. There was evidence of developmental toxicity only at 100 ppm. The only finding was a decrease in mean fetal weight. No fetal malformations or variations occurred in fetuses derived from rats exposed to all 3 test concentrations (up to 100 ppm). The maternal no-observed-effect-level (NOEL) was 2 ppm, the fetal NOEL was 20 ppm. Thus, TMU was not considered to be uniquely toxic to the rat conceptus.

Administration, Inhalation↗

Does mean lung dose calculated after inhalation of alpha emitters actually reflect the risk of induction of malignant lung tumours?

A comparison of incidence of lung tumours in rats after inhalation exposure to aerosols containing alpha emitters which have different physico-chemical properties has been performed. Aerosols of radon and progeny, uranium ore dust, NpO2, PuO2 or Cm2O3 were considered for intercomparison with similar or different particle sizes. Dose-effect relationships for the frequency of malignant lung tumours appear linear up to a few Gy and then become infralinear at higher doses delivered to the lungs. The initial slope of the curves reflects the risk of induction of a lung tumour. The highest slopes of incidence were observed for radon and uranium ore dust (about 70 and 20% Gy(-1) respectively) for which the most homogeneous alpha dose distribution to the lungs is expected. In a general trend, increasing the alpha-activity of deposited particles (higher specific activity of constituent radioisotopes or larger particle size) decreases the risk. The comparison of the reported data shows that the risk per Gy at 'low doses' could vary over more than one order of magnitude depending on the physico-chemical properties of the aerosols.

Actinoid Series Elements↗

The single exposure method for inhalation challenge with allergen.

We carried out inhalation challenge with a single exposure to a high concentration of allergen (the single exposure method) on 92 asthmatic patients. With the use of the 3 Hz forced oscillation technique, we could continuously and graphically estimate total respiratory resistance (Rrs) throughout the test. The subjects inhaled aerosolized house dust allergen (1:5 w/v) for 1 min during tidal breathing. As soon as Rrs reached twice that of baseline value or after 10 min from the start of allergen exposure, subjects inhaled aerosolized bronchodilator for 3 min. To evaluate the Rrs response curve to inhaled allergen, we defined provocation time (PT35-Grs) as the time from the start of allergen exposure to the point at which total respiratory conductance (Grs) decreased 35% from its baseline value and appearance time (Ta) as the time from the start of allergen exposure to the beginning of an increase in Rrs. We presume that Ta may reflect bronchial sensitivity to allergen, since Ta significantly correlated with a unit of allergen causing a decrease in FEV1 of 20% (r = 0.66; p less than 0.05) in the dosimeter method. We demonstrated that the single exposure method is comparable to the dosimeter method in evaluating bronchial responses to inhaled allergen and also demonstrated the reproducibility of bronchial response to inhaled allergen with the single exposure method.

Adolescent↗

In vivo measurement of Pu dissolution parameters of MOX aerosols and related uncertainties in the values of the dose per unit intake.

The aim of this study was to compare dissolution parameter values for Pu from industrial MOX with different Pu contents. For this purpose, preliminary results obtained after inhalation exposure of rats to MOX containing 2.5% Pu are reported and compared to those obtained previously with MOX containing 5% Pu. Dissolution parameter values appear to increase when the amount of Pu decreases. Rapid fractions, f(r), of 4 x 10(-3) (s.d. = 2 x 10(-3)) and 1 x 10(-3) (s.d. = 6 x 10(-4)) and slow dissolution rates, s(s) of 2 x 10(-4) d(-1) (standard deviation, sigma = 5 x 10(-5)) and 5 x 10(-5) d(-1) (sigma = 1 x 10(-5)) were derived for MOX containing 2.5 and 5% of Pu, respectively. Simulations were performed to assess uncertainties on dose due to experimental errors. The relative standard deviations of the dose per unit intake (DPUI) due to f(r) (4-8%), are far less than those due to s(s) (about 20%), which is the main parameter altering the dose. Although quite different dissolution parameter values were derived, similar DPUIs were obtained for MOX aerosols containing 2.5 and 5% Pu which appear close to that for default Type S values.

Absorption↗

Acute lung injury from intratracheal exposure to fugitive residual oil fly ash and its constituent metals in normo- and spontaneously hypertensive rats.

We have recently shown that the spontaneously hypertensive (SH) rats with underlying cardiovascular disease exhibited greater pulmonary vascular leakage and oxidative stress than healthy normotensive (Wistar Kyoto, WKY) rats after a 3-day inhalation exposure to residual oil fly ash (ROFA) particles (Kodavanti et al., 2000). Since host responsiveness to a 3-day episodic ROFA inhalation could be different from a single acute exposure, we examined ROFA and its constituent metal (vanadium, V; nickel, Ni)-induced lung injury after a single intratracheal (IT) exposure. Male SH and WKY rats (12-13 wk) were IT instilled with either saline or ROFA (0.0, 0.83 or 3.33 mg/kg). The bronchoalveolar lavage fluid (BALF) was analyzed for lung injury markers at 24 and 96 h post-IT. Rats were also IT instilled with 0.0 or 1.5 micromol/kg of either VSO(4) or NiSO(4).6H(2)O in saline (equivalent to a dose of 2-3 mg ROFA), and assessed at 6 and 24 h post-IT. Basal levels of BALF protein, macrophages, and neutrophils, but not lactate dehydrogenase (LDH), were higher in control SH compared to control WKY rats. Lung histology of control SH rats exhibited mild focal alveolitis and perivascular inflammation; these changes were minimal in control WKY rats. ROFA-induced increases in BALF protein, and to a lesser extent in LDH, were greater in SH compared to WKY rats. ROFA IT was associated with the increases in BALF total cells in both strains (SH > WKY). BALF neutrophils increased at 24 h and macrophages at 96 h in a dose-dependent manner (SH > WKY). The increase in BALF neutrophils was largely reversed by 96 h in both rat strains. The V-induced increases in BALF protein and LDH peaked at 6 h post-IT and returned to control by 24 h in WKY rats. In SH rats, BALF protein and LDH were not affected by V. Ni caused BALF protein to increase in both strains at 6 and 24 h; however, the control values at 24 h were high in SH rats, and were not distinguishable from exposed rats. The Ni-induced increase in LDH activity was progressive over a 24-h time period (WKY > SH). The number of macrophages decreased following V and Ni exposure at 6 h, and this decrease was reversed by 24 h in both strains. V caused BALF neutrophils to increase only in WKY rats. The Ni-induced increase in BALF neutrophils was more dramatic and progressive than that of V, but was similar in both strains. Lung histology similarly revealed more severe and persistent edema, perivascular and peribronchiolar inflammation, and hemorrhage in Ni- than in V-exposed rats. This effect of Ni appeared slightly more severe in SH than in WKY rats. In summary, the acute single IT exposure to ROFA resulted in greater pulmonary protein leakage and inflammation in SH rats than in WKY rats. The metallic constituents of ROFA produced these effects in a strain-specific manner such that, at the dose level used, V caused pulmonary injury only in WKY rats, whereas Ni was toxic to both strains.

Acute Disease↗

Concentration and particle size of airborne toxic algae (brevetoxin) derived from ocean red tide events.

Red tides in the Gulf of Mexico are formed by blooms of the dinoflagellate Karenia brevis, which produces brevetoxins (PbTx). Brevetoxins can be transferred from water to air in the wind-powered whitecapped waves during red tide episodes. Inhalation exposure to marine aerosol containing PbTx causes respiratory problems. A liquid chromatograph/ tandem mass spectrometric method was developed for the detection and quantitation of several PbTxs in ambient samples collected during red tide events. This method was complemented by a previously developed antibody assay that analyzes the entire class of PbTx compounds. The method showed good linearity, accuracy, and reproducibility, allowing quantitation of PbTx compounds in the 10 pg/m3 range. Air concentrations of PbTxs and brevenal for individual samples ranged from 0.01 to 80 ng/m3. The particle size showed a single mode with a mass median diameter between 6 and 10 microm, which was consistent for all of the PbTx species that were measured. Our results imply that individual PbTxs were from the same marine aerosol or from marine aerosol that was produced from the same process. The particle size indicated the likelihood of high deposition efficiency in the respiratory tract with the majority of aerosol deposited in the upper airways and small but not insignificant deposition in the lower airways.

Aerosols↗

Subacute inhalation toxicity of 2-chloro-4-toluidine in rats.

This article addresses results from a 4-wk inhalation exposure study in Wistar rats with the vapor and/or aerosol atmospheres of 2-chloro-4-toluidine. Groups of 10 rats/sex were nose-only exposed to mean analytical concentrations of 19.1, 115.1, and 702.3 mg/m3 using an exposure regimen of 6 h/day and 20-22 exposures within a time period of 4 wk. These concentrations were selected based on results from a repeated 5 x 6 h/day pilot study using concentrations of 27.1, 104.8, 381.6, and 1283.7 mg/m3. In a single 4-h exposure study at the maximum tested concentration of 7620 mg/m3, 1 of 10 female rats succumbed (no mortality in males), while no mortality occurred at 3293 mg/m3. In the 1- and 4-wk studies mortality occurred at 1283.7 and 702.3 mg/m3, respectively. Rats exposed for 4 wk to 702.3 mg/m3 displayed characteristic signs of toxicity that included cyanosis, respiratory distress, and significantly decreased body weights. Rectal temperatures were significantly decreased at 115.1 mg/m3 and above. Dark and enlarged spleens occurred at 702.3 mg/m3. At this concentration, prominent treatment-related effects included methemoglobinemia, reticulocytosis, red blood cells with Heinz bodies, decreased hemoglobin, hematocrit, and red blood cell counts. Borderline evidence of erythrocytotoxicty was noticed at 115.1 mg/m3 (based on a minimal increase in Heinz bodies). Spleen and liver weights were significantly increased at 702.3 mg/m3, whereas the thymus weight was decreased at 115.1 mg/m3 and above. Microscopic changes were found in the spleen (hemosiderosis) at 702.3 mg/m3. An atrophy of the olfactory epithelium in the nasal cavities occurred at 115.1 mg/m3 and above. Clinical pathology revealed changes pathognostic of hepatic effects, although microscopic examinations did not reveal any specific changes. The no-observed-adverse-effect level (NOAEL) of the 4-wk study was 19.1 mg/m3 and is based on the predominant atrophic changes of the olfactory epithelium and the minimal to borderline erythrocytotoxic effects at 115.1 mg/m3.

Aerosols↗

Role of quorum sensing in the pathogenicity of Burkholderia pseudomallei.

Burkholderia pseudomallei is the causative agent of human and animal melioidosis. The role of quorum sensing (QS) in the in vivo pathogenicity of B. pseudomallei via inhalational exposure of BALB/c mice and intraperitoneal challenge of Syrian hamsters has not been reported. This investigation demonstrates that B. pseudomallei encodes a minimum of three luxI and five luxR homologues that are involved in animal pathogenicity. Mass spectrometry analysis of culture supernatants revealed that wild-type B. pseudomallei and the luxI mutants synthesized numerous signalling molecules, including N-octanoyl-homoserine lactone, N-decanoyl-homoserine lactone, N-(3-hydroxyoctanoyl)-L-homoserine lactone, N-(3-hydroxydecanoyl)-L-homoserine lactone and N-(3-oxotetradecanoyl)-L-homoserine lactone, which was further confirmed by heterologous expression of the B. pseudomallei luxI alleles in Escherichia coli. Mutagenesis of the B. pseudomallei QS system increased the time to death and reduced organ colonization of aerosolized BALB/c mice. Further, intraperitoneal challenge of Syrian hamsters with the B. pseudomallei QS mutants resulted in a significant increase in the LD50. Using semi-quantitative plate assays, preliminary analysis suggests that QS does not affect lipase, protease and phospholipase C biosynthesis/secretion in B. pseudomallei. The findings of the investigation demonstrate that B. pseudomallei encodes multiple luxIR genes, and disruption of the QS alleles reduces animal pathogenicity, but does not affect exoproduct secretion.

Adaptation, Physiological↗