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Research Report (Health Effects Institute)[JOURNAL]

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Inhalation toxicology of urban ambient particulate matter: acute cardiovascular effects in rats.

Vincent R, Kumarathasan P, Goegan P … +8 more , Bjarnason SG, Guénette J, Bérubé D, Adamson IY, Desjardins S, Burnett RT, Miller FJ, Battistini B

Res Rep Health Eff Inst · 2001 Oct · PMID 11833973

Wistar rats were exposed for 4 hours by nose-only inhalation to clean air, resuspended Ottawa ambient particles (EHC-93*, 48 mg/m3), the water-leached particles (EHC-93L, 49 mg/m3), diesel soot (5 mg/m3), or carbon black... Wistar rats were exposed for 4 hours by nose-only inhalation to clean air, resuspended Ottawa ambient particles (EHC-93*, 48 mg/m3), the water-leached particles (EHC-93L, 49 mg/m3), diesel soot (5 mg/m3), or carbon black (5 mg/m3). Continuous data for physiologic endpoints (heart rate, blood pressure, body temperature, animal's activity) were captured by telemetry before and after exposure. Blood was sampled from jugular cannulas 1 to 3 days before exposure and at 2 and 24 hours after exposure, and by heart puncture on termination at 32 hours (histology group) or 48 hours (telemetry group) after exposure. Lung injury was assessed by 3H-thymidine autoradiography after the rats were killed. We measured endothelins (plasma ET-1, big ET-1, ET-2, ET-3) to assess the vasopressor components; nitric oxide (NO)-related metabolites (blood nitrate, nitrite, nitrosyl compounds, and plasma 3-nitrotyrosine) to assess the vasodilator components; and catecholamines (epinephrine, norepinephrine, L-DOPA, dopamine) and oxidative stressors (m- and o-tyrosine) for additional insight into possible stress components. Lung cell labeling was uniformly low in all treatment groups, which indicates an absence of acute lung injury. Inhalation of EHC-93 caused statistically significant elevations (P < 0.05) of blood pressure on day 2 after exposure, plasma ET-1 at 32 hours after exposure, and ET-3 at 2, 32, and 48 hours after exposure. In contrast, the modified EHC-93L particles, from which soluble components had been extracted, did not affect blood pressure. The EHC-93L particles caused early elevation (P < 0.05) of the plasma levels of ET-1, ET-2, and ET-3 at 2 hours after exposure, but the endothelins returned to basal levels 32 hours after exposure. Exposure to diesel soot, but not carbon black, caused an elevation (P < 0.05) of plasma ET-3 at 36 hours after exposure; blood pressure was not affected by diesel soot. Our results indicate that inhalation of the urban particles EHC-93 can affect blood levels of ET-1 and ET-3 and cause a vasopressor response in Wistar rats without causing acute lung injury. Furthermore, the potency of the particles to influence hemodynamic changes appears to be modified by removing polar organic compounds and soluble elements. Because the pathophysiologic significance of elevated endothelins has been clinically established in humans, our observations suggest a novel mechanism by which inhaled particles may cause cardiovascular effects. These findings in rats contribute to the weight of evidence in favor of a biologically plausible epidemiologic association between ambient particulate matter and cardiovascular morbidity and mortality in human populations.

MTBE inhaled alone and in combination with gasoline vapor: uptake, distribution, metabolism, and excretion in rats.

Benson JM, Barr EB, Krone JR

Res Rep Health Eff Inst · 2001 May · PMID 11504149

The purpose of these studies was to extend previous evaluation of methyl tert-butyl ether (MTBE)* tissue distribution, metabolism, and excretion in rats to include concentrations more relevant to human exposure (4 and 40... The purpose of these studies was to extend previous evaluation of methyl tert-butyl ether (MTBE)* tissue distribution, metabolism, and excretion in rats to include concentrations more relevant to human exposure (4 and 40 ppm) and to determine the effects of coinhalation of the volatile fraction of unleaded gasoline on the tissue distribution, metabolism, and excretion of MTBE. Groups of male F344 rats were exposed nose-only for 4 hours to 4, 40, or 400 ppm 14C-MTBE or to 20 or 200 ppm of the light fraction of unleaded gasoline (LFG) containing 4 or 40 ppm 14C-MTBE, respectively. To evaluate the effects of repeated inhalation of LFG on MTBE tissue distribution, metabolism, and excretion, rats were exposed for 4 hours on each of 7 consecutive days to 20 or 200 ppm LFG with MTBE (4 or 40 ppm) followed on the eighth day by a similar exposure to LFG containing 14C-MTBE. Subgroups of rats were evaluated for respiratory parameters, initial body burdens, rates and routes of excretion, and tissue distribution and elimination. The concentrations of MTBE and its chief metabolite, tert-butyl alcohol (TBA), were measured in blood and kidney immediately after exposure, and the major urinary metabolites-2-hydroxyisobutyric acid (IBA) and 2-methyl-1,2-propanediol (2MePD)-were measured in urine. Inhalation of MTBE alone or as a component of LFG had no concentration-dependent effect on respiratory minute volume. The initial body burdens of MTBE equivalents achieved after 4 hours of exposure to MTBE did not increase linearly with exposure concentration. MTBE equivalents rapidly distributed to all tissues examined, with the largest percentages distributed to liver. The observed initial body burden did not increase linearly between 4 and 400 ppm. At 400 ppm, elimination half-times of MTBE equivalents from liver increased and from lung, kidney, and testes decreased compared with the two smaller doses. Furthermore, at 400 ppm the elimination half-time for volatile organic compounds (VOCs) in breath was significantly shorter and the percentage of the initial body burden of MTBE equivalents eliminated as VOCs in breath increased significantly. These changes probably reflect a saturation of blood with MTBE at 400 ppm and strongly suggest that the uptake and fate of MTBE are notably different at exposure concentrations above and below 400 ppm. Single and repeated coexposure to 20 and 200 ppm LFG with MTBE had opposite effects on the total body burden of MTBE equivalents present at the end of exposures compared with those achieved after 4 and 40 ppm MTBE exposures: 20 ppm LFG increased and 200 ppm LFG significantly decreased the burdens of MTBE equivalents present. The effects of coexposure to LFG on blood levels of MTBE equivalents paralleled the effects on body burden. These differences in overall uptake of MTBE equivalents cannot be attributed to alterations of minute volume. The reason for the increase in overall uptake after 20-ppm LFG exposure is not clear. Decreased MTBE absorption (uptake) after single and repeated coexposure to 200 ppm LFG may be due to a decrease in solubility of MTBE in blood caused by inhalation of other hydrocarbons. Investigations on the blood/air partition coefficient of MTBE in the absence and presence of LFG would be needed to confirm this hypothesis. Single and repeated coexposure to either 20 or 200 ppm LFG significantly decreased the percentage of the initial body burden from MTBE equivalents in tissues, including liver, kidney, and testes, immediately and 72 hours after

Human cytochrome P450 isozymes in metabolism and health effects of gasoline ethers.

Hong JY, Wang YY, Mohr SN … +2 more , Bondoc FY, Deng C

Res Rep Health Eff Inst · 2001 May · PMID 11504148

To reduce the production of carbon monoxide and other pollutants in motor vehicle exhaust, methyl tert-butyl ether (MTBE*), ethyl tert-butyl ether (ETBE), and tert-amyl methyl ether (TAME) are added to gasoline as oxygen... To reduce the production of carbon monoxide and other pollutants in motor vehicle exhaust, methyl tert-butyl ether (MTBE*), ethyl tert-butyl ether (ETBE), and tert-amyl methyl ether (TAME) are added to gasoline as oxygenates for more complete combustion. Among them, MTBE is the most widely used. The possible adverse effect of MTBE in humans is a public concern, but the human enzymes responsible for metabolism of these gasoline ethers and the causes or factors for increased sensitivity to MTBE in certain individuals are totally unknown. This information is important to understanding the health effects of MTBE in humans and to assessing the human relevance of pharmacokinetics and toxicity data obtained from animals. In the present study, we demonstrated that human liver is active in metabolizing MTBE to tert-butyl alcohol (TBA), a major circulating metabolite and an exposure marker of MTBE. The activity is localized in the microsomal fraction but not in the cytosol. Formation of TBA in human liver microsomes is NADPH-dependent and is significantly inhibited by carbon monoxide, which inhibits cytochrome P450 (CYP) enzymes. These results provide strong evidence that CYP enzymes play a critical role in the metabolism of MTBE in human livers. Human liver is also active in the oxidative metabolism of 2 other gasoline ethers, ETBE and TAME. We observed a large interindividual variation in metabolizing these gasoline ethers in 15 microsomal samples prepared from normal human livers. The activity level (pmol metabolite/min/mg) ranged from 204 to 2,890 for MTBE; 179 to 3,134 for ETBE; and 271 to 8,532 for TAME. The microsomal activities in metabolizing MTBE, ETBE, and TAME correlated highly with each other (r = 0.91 to 0.96), suggesting that these ethers are metabolized by the same enzyme(s). Correlation analysis of the ether-metabolizing activities with individual CYP enzyme activities in the human liver microsomes showed that the highest degree of correlation was with CYP isoform 2A6 (CYP2A6)+ (r = 0.94 for MTBE, 0.95 for ETBE, and 0.90 for TAME), which is constitutively expressed in human livers and known to be polymorphic. CYP2A6 displayed the highest turnover number in metabolizing gasoline ethers among a battery of human CYP enzymes expressed in human B-lymphoblastoid cells. CYP2A6 coexpressed with human CYP reductase by a baculovirus expression system was also more active than CYP isoform 2E1 (CYP2E1) in the metabolism of MTBE, ETBE, and TAME. Kinetic studies on MTBE metabolism with human liver microsomes (n = 3) exhibited an apparent Michaelis constant (Km) of 28 to 89 microM and a maximum rate of metabolism (Vmax) of 215 to 783 pmol/min/mg. Metabolism of MTBE, ETBE, and TAME by human liver microsomes was inhibited by coumarin, a known substrate of human CYP2A6, in a concentration-dependent manner. Monoclonal antibody against human CYP2A6 caused a significant inhibition (75% to 95%) of the metabolism of MTBE, ETBE, and TAME in human liver microsomes. Taken together, these results clearly indicate that, in human liver, CYP2A6 is a major enzyme responsible for metabolism of MTBE, ETBE, and TAME. Although CYP2E1 metabolizes diethyl ether and was previously suggested to be involved

Biotransformation of MTBE, ETBE, and TAME after inhalation or ingestion in rats and humans.

Dekant W, Bernauer U, Rosner E … +1 more , Amberg A

Res Rep Health Eff Inst · 2001 May · PMID 11504147

The biotransformation of methyl tert-butyl ether (MTBE), ethyl tert-butyl ether (ETBE), and tert-amyl methyl ether (TAME) was studied in humans and in rats after inhalation of 4 and 40 ppm of MTBE, ETBE, and TAME, respec... The biotransformation of methyl tert-butyl ether (MTBE), ethyl tert-butyl ether (ETBE), and tert-amyl methyl ether (TAME) was studied in humans and in rats after inhalation of 4 and 40 ppm of MTBE, ETBE, and TAME, respectively, for 4 hours, and the biotransformation of MTBE and TAME was studied after ingestion exposure in humans to 5 and 15 mg in water. tert-Butyl alcohol (TBA), a TBA conjugate, 2-methyl-1,2-propanediol, and 2-hydroxyisobutyrate were found to be metabolites of MTBE and ETBE. tert-Amyl alcohol (TAA), free and glucuronidated 2-methyl-2,3-butanediol (a glucuronide of TAA), 2-hydroxy-2-methyl butyrate, and 3-hydroxy-3-methyl butyrate were found to be metabolites of TAME. After inhalation, MTBE, ETBE, and TAME were rapidly taken up by both rats and humans; after termination of exposure, clearance from blood of the ethers by exhalation and biotransformation to urinary metabolites occurred with half-times of less than 7 hours in rats and humans. Biotransformation of MTBE and ETBE was similar in humans and rats after inhalation exposure. 2-Hydroxyisobutyrate was recovered as a major product in urine. All metabolites of MTBE and ETBE excreted with urine were eliminated with half-times of less than 20 hours. Biotransformation of TAME was qualitatively similar in rats and humans, but the metabolic pathways were different. In humans, 2-methyl-2,3-butanediol, 2-hydroxy-2-methyl butyrate, and 3-hydroxy-3methyl butyrate were recovered as major urinary products. In rats, however, 2-methyl-2,3-butanediol and its glucuronide were major TAME metabolites recovered in urine. After ingestion of MTBE and TAME, both compounds were rapidly absorbed from the gastrointestinal tract. Hepatic first-pass metabolism of these ethers was not observed, and a significant part of the administered dose was transferred into blood and cleared by exhalation. Metabolic pathways for MTBE and TAME and kinetics of excretion were identical after ingestion and inhalation exposures. Results of studies presented here suggest (1) that excretion of MTBE, ETBE, and TAME in rats and humans is rapid, (2) that biotransformation and excretion of MTBE and ETBE are identical in rats, and (3) that biotransformation and excretion of TAME is quantitatively different in rats and humans.

Characterization and mechanisms of chromosomal alterations induced by benzene in mice and humans.

Eastmond DA, Schuler M, Frantz C … +4 more , Chen H, Parks R, Wang L, Hasegawa L

Res Rep Health Eff Inst · 2001 Jun · PMID 11504146

Elevated frequencies of chromosomal aberrations have been observed in the lymphocytes of benzene-exposed workers. Similar changes occurring in the bone marrow may play an important role in the development of leukemia. Th... Elevated frequencies of chromosomal aberrations have been observed in the lymphocytes of benzene-exposed workers. Similar changes occurring in the bone marrow may play an important role in the development of leukemia. The objective of this research has been to characterize chromosomal alterations induced by benzene in mice and humans and to investigate the potential role of inhibition of topoisomerase II in the myelotoxic effects of benzene. The research is presented in three sections corresponding to the specific aims of the project: genotoxicity studies in the mouse, topoisomerase II studies, and initial studies using a new fluorescence in situ hybridization (FISH) approach to detect chromosome alterations in benzene-exposed workers. The results of the mouse experiments indicate that both chromosome breakage and aneuploidy are induced in the bone marrow of B6C3F1 mice following benzene administration. Chromosome breakage is the predominant effect, and this occurs primarily in the mouse euchromatin. Significant breakage within the mouse heterochromatin was also observed, as was aneuploidy. Breakage in the mouse bone marrow erythrocytes increased as a function of both dose and duration of benzene administration. The aneuploidy resulting from benzene exposure in mice was a relatively infrequent event, with increases of both chromosome loss and hyperdiploidy being observed. In the topoisomerase studies, benzene or its metabolites were shown to inhibit topoisomerase II enzyme activity in an isolated enzyme system, in a human bone marrow-derived leukemia cell line, and in vivo in the bone marrow of treated mice. The decreased activity was probably due to the rapid degradation of the topoisomerase II protein in the treated cells. In the human biomonitoring studies, the feasibility of using FISH with tandem DNA probes to detect chromosome alterations in interphase granulocytes and lymphocytes of benzene-exposed workers was demonstrated. The results from the two worker studies were somewhat inconsistent, however. In the study of Estonian workers, characterized by lower exposures and a smaller sample size, the benzene-exposed workers exhibited elevated frequencies of breakage in the lq12 region as compared with those seen in controls. A suggestive trend toward increased hyperdiploidy was also seen, although the frequencies in the exposed workers were low and within the range of our laboratory's historical control frequencies. In the larger study of more highly exposed Chinese workers, no increase in breakage affecting the 1q12 region was seen among the exposed workers. A trend toward increased hyperdiploidy of chromosome 1 was seen in the exposed workers when the concentration of urinary benzene metabolites was used in conjunction with the frequency of hyperdiploidy observed in the lymphocytes of the individual workers. The results of these studies indicate that benzene exposure is characterized by chromosome breakage, primarily within the euchromatin, and modest increases in aneuploidy. These findings also provide the first direct evidence that benzene is capable of inhibiting the enzymatic activity of topoisomerase II in vivo, providing additional support for the hypothesis that inhibition of topoisomerase II contributes to benzene-induced toxicity and leukemogenesis.

Respiratory epithelial penetration and clearance of particle-borne benzo[a]pyrene.

Gerde P, Muggenburg BA, Lundborg M … +2 more , Tesfaigzi Y, Dahl AR

Res Rep Health Eff Inst · 2001 Apr · PMID 11488545

Exposure to diesel exhaust is a suspected risk factor for human lung cancer. The carbonaceous core of the soot particles found in diesel exhaust and the condensed organic compounds adsorbed (or bound) onto the surface of... Exposure to diesel exhaust is a suspected risk factor for human lung cancer. The carbonaceous core of the soot particles found in diesel exhaust and the condensed organic compounds adsorbed (or bound) onto the surface of the particles are both possible contributors to this suspected risk. The extent and rate at which organic procarcinogens desorb from soot particles in the lungs after environmental and workplace exposures and the degree of metabolic activation in the lungs are also not known. We explored the relationship between a model polynuclear aromatic hydrocarbon (PAH)* and a typical carrier particle by measuring the rate of release, extent of release, and metabolic fate of benzo[a]pyrene (BaP) bound onto the carbonaceous core of diesel soot after bolus aerosol exposures of the dog's peripheral lung and trachea. Exogenous BaP was bound onto preextracted diesel soot at a surface concentration corresponding to 25% of a monomolecular layer. After deposition in the alveolar region, a fraction of BaP was rapidly desorbed from the soot and quickly absorbed into the circulating blood. Release rates then decreased drastically. When the BaP coating reached approximately 16% of a monolayer, it was not bioavailable and remained on the particles after 5.6 months in the lung. The bioavailability of BaP on particles retained in lymph nodes was markedly higher, however: after 5.6 months the surface coating of BaP was reduced to 10% of a monolayer. Fractions of BaP that remained bound to the soot surface during this 5.6 months had a low reactivity-nearly 30% of the radioactive compounds extracted from recovered soot particles were still BaP, the parent compound. In contrast, the rapidly released fraction of BaP, which was quickly absorbed through the alveolar epithelium after inhalation, appeared mostly unmetabolized in the circulation, along with low concentrations of phase I and phase II BaP metabolites. Within approximately 1 hour, however, this rapidly absorbed fraction of BaP was metabolized, most likely in the liver, with the metabolite spectrum being dominated by conjugated phase II metabolites. The fraction of BaP desorbed from particles deposited on the epithelium of the conducting airways was absorbed by the epithelium but slowly penetrated the capillary bed. The absorbed BaP was rapidly metabolized in the airway epithelium, as indicated by the influx of tritiated water (3H2O) from the lungs into the circulation. The results suggest that the dosimetry of inhaled, highly lipophilic BaP during typical exposures is bimodal. The larger fraction of bioavailable BaP deposited in the alveolar region was absorbed mostly unaltered into the blood through the alveolar type I cells and was metabolized systemically. A smaller fraction of bioavailable BaP was deposited on the airway mucosa and rapidly metabolized, most likely in the airway epithelium. The substrate levels of BaP in the epithelium of the conducting airways exceeded the systemic levels by up to two orders of magnitude. This dramatic site-of-entry to systemic duality in the dosimetry of inhaled BaP is likely to be similar in most mammalian species and should be considered in risk assessment models for PAHs in humans.

Respiratory tract toxicity in rats exposed to Mexico City air.

Moss OR, Gross EA, James RA … +7 more , Janszen DB, Ross PW, Roberts KC, Howard AM, Harkema JR, Calderón-Garcidueñas L, Morgan KT

Res Rep Health Eff Inst · 2001 Mar · PMID 11488544

The rat has been used extensively as a health sentinel, indicator, or monitor of environmental health hazards, but this model has not been directly validated against human exposures. Humans in Mexico City show upper resp... The rat has been used extensively as a health sentinel, indicator, or monitor of environmental health hazards, but this model has not been directly validated against human exposures. Humans in Mexico City show upper respiratory tract lesions and evidence of pulmonary damage related to their environmental inhalation exposure. In this study, male and female F344 rats were exposed (23 hr/day) in Mexico City to local Mexico City air (MCA)* for up to seven weeks. Controls were maintained at the same location under filtered air. Prior to these exposures, several steps were taken. First, the nasal passages of normal male rats shipped from the United States and housed in Mexico City were examined for mycoplasma infection; no evidence of infection was found. In addition, a mobile exposure and monitoring system was assembled and, with an ozone (O3) exposure atmosphere, was tested along with supporting histopathology techniques and analysis of rat nasal and lung tissues. Last, the entire exposure model (equipment and animals) was transported to Mexico City and validated for a three-week period. During the seven-week study there were 18 one-hour intervals during which the average O3 concentration of MCA in the exposure chamber exceeded the US National Ambient Air Quality Standard (NAAQS) of 0.120 ppm 03 (hourly average, not to be exceeded more than once per year). This prolonged exposure of healthy F344 rats to MCA containing episodically low to moderate concentrations of 03 (as well as other urban air pollutants) did not induce inflammatory or epithelial lesions in the nasal airways or lung as measured by qualitative histologic techniques or quantitative morphometric techniques. These findings agree with those of previous controlled O3 inhalation studies, but they are in contrast to reports indicating that O3-polluted MCA causes significant nasal mucosal injury in adults and children living in southwestern Mexico City. Taken together, these findings may suggest that human airways are markedly more susceptible to the toxic effects of MCA than are the airways of the F344 rat.

The National Morbidity, Mortality, and Air Pollution Study. Part II: Morbidity and mortality from air pollution in the United States.

Samet JM, Zeger SL, Dominici F … +5 more , Curriero F, Coursac I, Dockery DW, Schwartz J, Zanobetti A

Res Rep Health Eff Inst · 2000 Jun · PMID 11354823

Epidemiologic time-series studies conducted in a number of cities have identified, in general, an association between daily changes in concentration of ambient particulate matter (PM) and daily number of deaths (mortalit... Epidemiologic time-series studies conducted in a number of cities have identified, in general, an association between daily changes in concentration of ambient particulate matter (PM) and daily number of deaths (mortality). Increased hospitalization (a measure of morbidity) among the elderly for specific causes has also been associated with PM. These studies have raised concerns about public health effects of particulate air pollution and have contributed to regulatory decisions in the United States. However, scientists have pointed out uncertainties that raise questions about the interpretation of these studies. One limitation to previous time-series studies of PM and adverse health effects is that the evidence for an association is derived from studies conducted in single locations using diverse analytic methods. Statistical procedures have been used to combine the results of these single location studies in order to produce a summary estimate of the health effects of PM. Difficulties with this approach include the process by which cities were selected to be studied, the different analytic methods applied to each single study, and the variety of methods used to measure or account for variables included in the analysis. These individual studies were also not able to account for the effects of gaseous air pollutants in a systematic manner.

Association of particulate matter components with daily mortality and morbidity in urban populations.

Lippmann M, Ito K, Nádas A … +1 more , Burnett RT

Res Rep Health Eff Inst · 2000 Aug · PMID 11246487

Indices of atmospheric particulate matter (PM) have been reported to be associated with daily mortality and morbidity in a large number of recent time-series studies. However, the question remains as to which components... Indices of atmospheric particulate matter (PM) have been reported to be associated with daily mortality and morbidity in a large number of recent time-series studies. However, the question remains as to which components of PM are responsible for the reported associations. Multiple PM components rarely are measured simultaneously. To investigate PM effects on mortality and morbidity, we used the multiple PM components measured in Windsor, Ontario, at a site only a few miles from downtown Detroit, Michigan. This study focused primarily on two study periods in which multiple PM components were measured in Windsor: 1985 to 1990, when levels of total suspended particles (TSP), sulfate from TSP (TSP-SO4(2-)), PM less than 10 microns in diameter (PM10), and nonthoracic TSP (TSP-PM10) were measured throughout the year; and 1992 to 1994, when data on PM10, PM2.5 (PM less than 2.5 microns in diameter), PM10-2.5 (PM10 minus PM2.5), particle acidity (H+), and artifact-free sulfates (SO4(2-)) were available for mostly summer months. Mortality data were analyzed for the 1985 to 1990 study period, and data on both mortality and hospital admissions of elderly patients were analyzed for the 1992 through 1994 period. Poisson regressions were used to estimate the effects of these PM components and gaseous criteria pollutants on mortality (nonaccidental, circulatory, respiratory, and nonaccidental without circulatory and respiratory) and on hospital admissions of elderly patients (for pneumonia, chronic obstructive pulmonary disease [COPD], ischemic heart disease, dysrhythmias, heart failure, and stroke), adjusting for temperature and humidity, trends and seasonal cycles, and day of the week. Both PM10 and TSP were associated significantly with respiratory mortality for the 1985 to 1990 period, with similar relative risk (RR) estimates for PM10 (RR = 1.123; 95% confidence interval [CI] 1.0361-1.218) and TSP (RR = 1.109; 95% CI 1.028-1.197), per 5th to 95th percentile increment. The effect-size estimates for TSP-SO4(2-) and TSP-PM10 were smaller and less significant. In two-pollutant models, simultaneous inclusion of gaseous pollutants with PM10 or TSP reduced PM coefficients by 0 to 34%. The effect-size estimates for total mortality, circulatory mortality, and total minus circulatory and respiratory mortality were less than those for respiratory mortality. Ozone (O3) and nitrogen dioxide (NO2) also were associated significantly with total and circulatory mortality, but a simultaneous consideration of these pollutants with PM10 reduced PM10 coefficients only slightly, or even increased them. In these results, pollution coefficients often were positive at multiple lag days (0-day through 3-day lags were examined), but for PM indices, 1-day lag coefficients were most significant. However, when all combinations of multiple-day average exposures were examined, for cases in which multiple lag days were positive, the choice of single-day or multiple-day average exposure did not appreciably change the estimated effect sizes. An examination of temporal correlation showed that the order of spatial uniformity as expressed by the median site-to-site correlation was O3 (0.83), PM10 (0.78), TSP (0.71), NO2 (0.70), carbon monoxide (CO) (0.50), and sulfur dioxide (SO2) (0.49), which suggests less exposure error for O3 and PM10 than for the other measured pollutants. Thus, these results suggest that spatially homogeneous pollution indices show higher associations with measured health outcomes.

Identifying subgroups of the general population that may be susceptible to short-term increases in particulate air pollution: a time-series study in Montreal, Quebec.

Goldberg MS, Bailar JC, Burnett RT … +7 more , Brook JR, Tamblyn R, Bonvalot Y, Ernst P, Flegel KM, Singh RK, Valois MF

Res Rep Health Eff Inst · 2000 Oct · PMID 11244610

This study was undertaken in order to shed light on which groups of the general population may be susceptible to the effects of ambient particles. The objectives of the study were (1) to determine whether concentrations... This study was undertaken in order to shed light on which groups of the general population may be susceptible to the effects of ambient particles. The objectives of the study were (1) to determine whether concentrations of particles in the ambient air of Montreal, Quebec, were associated with daily all-cause and cause-specific mortality in the period 1984 to 1993, and (2) to determine whether groups of the population had higher than average risks of death from exposure to particles. From the network of fixed-site air pollution monitors in Montreal we obtained daily mean levels of various measures of particles, gaseous pollutants, and weather variables measured at Dorval International Airport. We also used measurements of sulfate from an acid rain monitoring station 150 km southeast of the city (Sutton, Quebec). We estimated associations for particulate matter (PM) with an aerodynamic diameter of 10 microns or smaller (PM10), or 2.5 microns or smaller (PM2.5), total suspended particles (TSP), coefficient of haze (COH), an extinction coefficient, and sulfate. Because substantial data for fine particles were missing, we developed a regression model to predict PM2.5 and to predict sulfate from PM2.5. In the main body of the report, we present results for COH, predicted PM2.5, and sulfate. Detailed results for all pollutants are included in Appendices H through O, which are available on request from Health Effects Institute and from the HEI web site at www.healtheffects.org. To address the first objective, we made use of the underlying causes of death among all 140,939 residents of Montreal who died between 1984 and 1993. We regressed the logarithm of daily counts of cause-specific mortality on the daily mean levels for a variety of measures of particles, accounting for seasonal and subseasonal fluctuations in the mortality time series, overdispersion, and weather factors. To address the second objective, we developed algorithms to define conditions that subjects had prior to death, with the focus on cardiopulmonary diseases. These algorithms were based on information retained on the databases of the universal Quebec Health Insurance Plan (QHIP). The databases include records of all procedures (e.g., type of surgery), physician visits, and consultations carried out by all physicians in Quebec. For persons > or = 65 years and for all recipients of social assistance the prescription database contains records of all pharmaceuticals dispensed (type of medication, dose, quantity). For each group of conditions defined, we used the same statistical model that was used in the analyses of all nonaccidental causes of death. In the analyses of cause-specific mortality, we found evidence of associations for all nonaccidental causes of death and specific causes of death--cancer, coronary artery disease, respiratory diseases, and diabetes--that were consistent across most metrics of ambient air particle concentrations, evaluated as the 3-day mean of particle concentrations measured on the day of death (lag 0) and on each of the two days before death (lag 1, lag 2). Associations for all cardiovascular diseases combined were found only with sulfate. As well, we generally found increased daily mortality for persons 65 years of age and over. The results for all nonaccidental causes of death are similar to findings from other studies; the mean percent increase in mortality for a 100 micrograms/m3 increase in daily TSP at lag 0 was 6.7%. In the analyses of the groups defined from the QHIP data, there was little evidence of associations with air pollutants among persons who before death were classified as having acute or chronic upper respiratory diseases, airways diseases, hypertension, acute coronary artery diseases, and cerebrovascular diseases. On the other hand, we found consistent increases across most types of ambient particles for persons who had cancer, acute lower respiratory diseases, any form of cardiovascular disease, chronic coronary artery diseases, and congestive heart failure. As well, we found an association for individuals who did not have any cardiovascular disease, lower respiratory diseases, and cancer. This latter group consisted of persons who had no interactions with the health care system one year before death (12%) and individuals with a wide variety of potentially fatal diseases (52%), including neurological conditions (12%), diabetes (8%), cardiac dysrhythmias (8%), dementia (6%), organic psychotic disorders (6%), and anemias (4%). As statistical power was reduced in the analyses presented above, differences between groups (e.g., < 65 and > or = 65 year age groups) were not usually statistically significant. The association with diabetes has not been reported previously, and this needs to be replicated in other studies. (ABSTRACT TRUNCATED)

Acute pulmonary effects of ultrafine particles in rats and mice.

Oberdörster G, Finkelstein JN, Johnston C … +4 more , Gelein R, Cox C, Baggs R, Elder AC

Res Rep Health Eff Inst · 2000 Aug · PMID 11205815

Ambient fine particles consist of ultrafine particles (< 100 nm) and accumulation-mode particles (approximately 100 to 1,000 nm). Our hypothesis that ultrafine particles can have adverse effects in humans is based on res... Ambient fine particles consist of ultrafine particles (< 100 nm) and accumulation-mode particles (approximately 100 to 1,000 nm). Our hypothesis that ultrafine particles can have adverse effects in humans is based on results of our earlier studies with particles of both sizes and on the finding that urban ultrafine particles can reach mass concentrations of 40 to 50 micrograms/m3, equivalent to number concentrations of 3 to 4 x 10(5) particles/cm3. The objectives of the exploratory studies reported here were to (1) evaluate pulmonary effects induced in rats and mice by ultrafine particles of known high toxicity (although not occurring in the ambient atmosphere) in order to obtain information on principles of ultrafine particle toxicology; (2) characterize the generation and coagulation behavior of ultrafine particles that are relevant for urban air; (3) study the influence of animals' age and disease status; and (4) evaluate copollutants as modifying factors. We used ultrafine Teflon (polytetrafluoroethylene [PTFE]*) fumes (count median diameter [CMD] approximately 18 nm) generated by heating Teflon in a tube furnace to 486 degrees C to evaluate principles of ultrafine particle toxicity that might be helpful in understanding potential effects of ambient ultrafine particles. Teflon fumes at ultrafine particle concentrations of approximately 50 micrograms/m3 are extremely toxic to rats when inhaled for only 15 minutes. We found that neither the ultrafine Teflon particles alone when generated in argon nor the Teflon fume gas-phase constituents when generated in air were toxic after 25 minutes of exposure. Only the combination of both phases when generated in air caused high toxicity, suggesting the existence of either radicals on the particle surface or a carrier mechanism of the ultrafine particles for adsorbed gas-phase compounds. We also found rapid translocation of the ultrafine Teflon particles across the epithelium after their deposition, which appears to be an important difference from the behavior of larger particles. Furthermore, the pulmonary toxicity of the ultrafine Teflon fumes could be prevented by adapting the animals with short 5-minute exposures on 3 days prior to a 15-minute exposure. This shows the importance of preexposure history in susceptibility to acute effects of ultrafine particles. Aging of the fresh Teflon fumes for 3.5 minutes led to a predicted coagulation resulting in particles greater than 100 nm that no longer caused toxicity in exposed animals. This result is consistent with greater toxicity of ultrafine particles compared with accumulation-mode particles. When establishing dose-response relationships for intratracheally instilled titanium dioxide (TiO2) particles of the size of the urban ultrafine particles (20 nm) and of the urban accumulation-mode particles (250 nm), we observed significantly greater pulmonary inflammatory response to ultrafine TiO2 in rats and mice. The greater toxicity of the ultrafine TiO2 particles correlated well with their greater surface area per mass. Ultrafine particles of carbon, platinum, iron, iron oxide, vanadium, and vanadium oxide were generated by electric spark discharge and characterized to obtain particles of environmental relevance for study. The CMD of the ultrafine carbon particles was approximately 26 nm, and that of the metal particles was 15 to 20 nm, with geometric standard deviations (GSDs) of 1.4 to 1.7. For ultrafine carbon particles, approximately 100 micrograms/m3 is equivalent to 12 x 10(6) particles/cm3. Homogeneous coagulation of these ultrafine particles in an animal exposure chamber occurred rapidly at 1 x 10(7) particles/cm3, so that particles quickly grew to sizes greater than 100 nm. Thus, controlled aging of ultrafine carbon particles allowed the generation of accumulation-mode carbon particles (due to coagulation growth) for use in comparative toxicity studies. We also developed a technique to generate ultrafine particles consisting of the stable isotope 13C by using 13C-graphite electrodes made in our laboratory from amorphous 13C powder. These particles are particularly useful tools for determining deposition efficiencies of ultrafine carbon particles in the respiratory tracts of laboratory animals and the translocation of particles to extrapulmonary sites. For compromised animals, we used acute and chronic pulmonary emphysema; a low-dose endotoxin inhalation aimed at priming target cells in the lung was also developed. Other modifying factors were age and copollutant (ozone) exposure. Exposure concentrations of the generated ultrafine particles for acute rodent inhalation studies were selected on the basis of lung doses predicted to occur in people inhaling approximately 50 micrograms/m3 urban ultrafine particles. Concentrations that achieved the same predicted lung burden per unit alveolar surface were used in rodents. (ABSTRACT TRUNCATED)

The National Morbidity, Mortality, and Air Pollution Study. Part I: Methods and methodologic issues.

Samet JM, Dominici F, Zeger SL … +2 more , Schwartz J, Dockery DW

Res Rep Health Eff Inst · 2000 Jun · PMID 11098531

The Health Effects Institute, established in 1980, is an independent and unbiased source of information on the health effects of motor vehicle emissions. HEI supports research on all major pollutants, including regulated... The Health Effects Institute, established in 1980, is an independent and unbiased source of information on the health effects of motor vehicle emissions. HEI supports research on all major pollutants, including regulated pollutants (such as carbon monoxide, ozone, nitrogen dioxide, and particulate matter) and unregulated pollutants (such as diesel engine exhaust, methanol, and aldehydes). To date, HEI has supported more than 200 projects at institutions in North America and Europe and has published over 100 research reports. Typically, HEI receives half its funds from the US Environmental Protection Agency and half from 28 manufacturers and marketers of motor vehicles and engines in the US. Occasionally, funds from other public and private organizations either support special projects or provide resources for a portion of an HEI study. Regardless of funding sources, HEI exercises complete autonomy in setting its research priorities and in reaching its conclusions. An independent Board of Directors governs HEI. The Institute's Research and Review Committees serve complementary scientific purposes and draw distinguished scientists as members. The results of HEI-funded studies are made available as Research Reports, which contain both the Investigators' Report and the Review Committee's evaluation of the work's scientific quality and regulatory relevance.

Reproductive and offspring developmental effects following maternal inhalation exposure to methanol in nonhuman primates.

Burbacher T, Shen D, Grant K … +4 more , Sheppard L, Damian D, Ellis S, Liberato N

Res Rep Health Eff Inst · 1999 Oct · PMID 10941406

INTRODUCTION: In an effort to improve air quality and decrease dependence on petroleum, the federal government, industry, and other groups have encouraged development of alternative fuels such as methanol to substitute f... INTRODUCTION: In an effort to improve air quality and decrease dependence on petroleum, the federal government, industry, and other groups have encouraged development of alternative fuels such as methanol to substitute for gasoline or diesel fuel. Methanol is also a candidate to provide the hydrogen for fuel cells, which are being developed for a variety of power sources (including motor vehicle engines). Before people are exposed to increased concentrations of methanol, the potential health effects of such exposures require study. Methanol, a simple alcohol containing one carbon atom, occurs naturally in plants and animals and participates in human metabolism. People regularly consume low doses of methanol in fruits, vegetables, and fermented beverages as well as soft drinks and foods sweetened with aspartame (which breaks down to methanol in the gastrointestinal tract). Despite its ubiquitous presence, methanol can be highly toxic if sufficient quantities are consumed. Ingestion of methanol (usually in the form of wood alcohol or tainted alcoholic beverages) can result in metabolic acidosis, blindness, and even death. Although the body has the capacity to metabolize the low doses of methanol to which people are regularly exposed, it cannot handle high doses because too much methanol overwhelms the body's ability to remove a toxic metabolite (formate). When formate accumulates, methanol poisoning occurs. One factor that regulates the rate at which formate is removed is the liver level of a derivative of the vitamin folic acid. People who are deficient in folic acid (including 15% to 30% of pregnant women) may be particularly susceptible to the toxic effects of methanol. If methanol were to be widely adopted as a fuel, environmental exposures would increase through ingestion of contaminated drinking water, inhalation of vapors from evaporative and other emissions, and dermal contact. Current concentrations of methanol in ambient air are very low, 1 to 30 parts per billion (ppb). If all motor vehicles in the United States were converted to 100% methanol fuel, methanol levels in ambient air are estimated to increase approximately 1,000-fold (to 1 to 10 ppm in cities) and in a worst-case situation could occasionally reach concentrations as high as 200 ppm in enclosed spaces (HEI 1987). Inhaling these concentrations of methanol for short periods of time is not predicted to affect formate production and thus should not present a health risk. However, little is known about the consequences of long-term inhalation of methanol vapors, especially in susceptible populations of pregnant women and developing fetuses. HEI, therefore, developed a research program to address this information gap. APPROACH: Dr. Thomas Burbacher and colleagues of the University of Washington studied the effects of long-term exposure to methanol vapors on metabolism and reproduction in adult female monkeys (Macaca fascicularis) and developmental effects in their offspring, who were exposed prenatally to methanol. The investigators exposed adult female monkeys (11 to 12 animals/group) to one of four concentrations of methanol vapors (0, 200, 600, and 1,800 ppm) for 2.5 hours a day, seven days a week during the following periods: (1) before breeding, (2) during breeding, and (3) during pregnancy. They collected blood from the adults at regular intervals to monitor methanol levels (which served as a marker of internal dose) and formate concentrations. They also conducted pharmacokinetic studies to determine whether methanol disposition (which includes absorption, distribution, metabolism, and excretion) was altered as a result of repeated methanol exposures and to assess pregnancy-related changes. Because high doses of methanol damage the central nervous system, the infants (8 to 9 animals/group) were examined at regular intervals during the first nine months of life to assess their growth and neurobehavioral development. RESULTS: Exposure to methanol vapors did n

1,3-butadiene: cancer, mutations, and adducts. Part V: Hemoglobin adducts as biomarkers of 1,3-butadiene exposure and metabolism.

Swenberg JA, Christova-Gueorguieva NI, Upton PB … +5 more , Ranasinghe A, Scheller N, Wu KY, Yen TY, Hayes R

Res Rep Health Eff Inst · 2000 Mar · PMID 10925842

1,3-Butadiene (BD) is an important chemical used largely in the manufacture of synthetic rubber and thermoplastic resins. In addition, it has been identified in cigarette smoke, automobile exhaust, and gasoline vapor. Th... 1,3-Butadiene (BD) is an important chemical used largely in the manufacture of synthetic rubber and thermoplastic resins. In addition, it has been identified in cigarette smoke, automobile exhaust, and gasoline vapor. The objective of this research was to develop highly sensitive and specific assays for the detection and quantitation of hemoglobin adducts of three BD metabolites: 1,2-epoxy-3-butene (BDO), 1,2,3,4-diepoxybutane (BDO2), and 1,2-dihydroxy-3,4-epoxybutane (BDO-diol). We have successfully developed an assay for both N-(2-hydroxy-3-butenyl)valine (HBVal) and N-(2,3,4-trihydroxybutyl)valine (THBVal) in hemoglobin. The six adducts measured were the two diastereomers (isomers I and II) of HBVal and the four diastereomers of THBVal (isomers I through IV, which were eluted as three peaks, 1, 2, and 3). HBVal and THBVal were measured in control and exposed B6C3F1 mice and Sprague-Dawley rats (1,000 ppm BD for 13 weeks at 6 hours/day, 5 days/week). In a second set of animal exposures, total THBVal was determined in B6C3F1 female mice (n = 5) exposed to 1,250 ppm BD for 1, 5, or 10 days (6 hours/day, 5 days/week). THBVal adducts were also monitored in occupationally exposed Chinese workers and nonoccupationally exposed U.S. laboratory workers. This study utilized the modified Edman degradation method of Törnqvist and colleagues (1986). Briefly, the samples were subjected to Edman degradation, Centricon-30 ultrafiltration, washing on C18 columns, and acetylation for isomers of THBVal only, followed by gas chromatography-mass spectrometry (GC-MS) quantitation. For the HBVal assay, an authentic internal standard globin alkylated with [2H6]BDO was used; for the THBVal assay, a synthesized external standard, THB[13C5]Val, was used after Edman degradation. The mean +/- SD amounts of total HBVal measured in exposed mice (in pmol/g globin) were 16,560 +/- 3,910 for female mice (n = 4) and 12,400 +/- 2,030 for male mice (n = 5). The corresponding values for rats were 8,690 +/- 930 for female rats (n = 5) and 5,480 +/- 2,880 for male rats (n = 3). The total amount of THBVal (eluted peaks 1, 2, and 3) in male mice (n = 5) was 78,900 +/- 13,700; and in females (n = 2) was 56,100 +/- 100. In male rats (n = 3), the detected value was 9,650 +/- 1,620 and in females (n = 3) the value was 21,600 +/- 6,780. In control male mice (n = 4), the total level of THBVal isomers was approximately 27 pmol/g globin. In a control male rat, total THBVal was approximately 15 pmol/g globin. In the time course study, the amount of THBVal adducts increased linearly with exposure, resulting in values of 4,200 +/- 830, 19,760 +/- 1,780, and 35,940 +/- 3,460 pmol/g globin following 1, 5, or 10 days of exposure to 1,250 ppm BD, respectively. Detection of HBVal in human samples was difficult due to low concentrations of adducts and a high background in the chromatograms. In a pooled sample from 4 individuals, we performed multiple separations with high-pressure liquid chromatography (HPLC) of the derivatized adducts and detected 4.6 pmol/g globin (that is, 2.7 and 1.9 pmol/g globin for isomers I and II, respectively). We measured the amounts of THBVal in both nonoccupationally exposed U.S. laboratory workers and occupationally exposed workers from a polybutadiene plant in China. The mean total amount of THBVal among the U.S. laboratory workers was 36 +/- 23 pmol/g globin for nonsmokers (n = 7) and 40 +/- 9 for smokers (n = 4), compared with a mean total amount of 39 +/- 13 pmol/g globin in a control set of Chinese workers (n = 25). These control values are overestimations of the true values because the amounts of THBVal in globin samples from other unexposed individuals (15 of 51) were below our limit of detection. BD-exposed Chinese workers had a total amount of 88 +/- 59 pmol/g globin THBVal. The difference between smokers and nonsmokers was not significant, whereas the difference between control and exposed Chinese workers was highly significant (p < 0.001).

1,3-butadiene: cancer, mutations, and adducts. Part IV: Molecular dosimetry of 1,3-butadiene.

Blair IA, Oe T, Kambouris S … +1 more , Chaudhary AK

Res Rep Health Eff Inst · 2000 Mar · PMID 10925841

Analysis of N7-guanine adducts derived from 1,3-butadiene (BD) was conducted with use of liquid chromatography-mass spectrometry (LC-MS) in combination with stable isotope methods. The N7-guanine adducts were shown to un... Analysis of N7-guanine adducts derived from 1,3-butadiene (BD) was conducted with use of liquid chromatography-mass spectrometry (LC-MS) in combination with stable isotope methods. The N7-guanine adducts were shown to undergo spontaneous depurination from DNA in vitro in both calf-thymus DNA and TK6-cell DNA. A comparison was made between BD-derived N7-guanine adduct concentrations both in liver DNA and urine of rats and mice exposed to BD. This has provided insight into the exposure of the animals to 1,2-epoxy-3-butene (BDO), 1,2,3,4-diepoxybutane (BDO2), and 1,2-dihydroxy-3,4-epoxybutane (BDO-diol), the three oxidative metabolites of BD thought to be responsible for BD-mediated carcinogenesis. The liver DNA of mice contained more of the two N7-guanine adducts of BDO--N7-2-hydroxy-3-butenyl-1-guanine (2HB1G) and N7-1-hydroxy-3-butenyl-2-guanine (1HB2G)--than the amounts in rats during the 10-day BD exposure and the 6 days after exposure that were monitored. An excess of 1HB2G over 2HB1G by a factor of approximately 10 in the rat liver and a factor of approximately 5 in the mouse liver was also observed. This regioselective difference was apparent during both the 10-day exposure and the 6 days after exposure. The half-lives of 2HB1G and 1HB2G were estimated as 4.3 days and 3.5 days, respectively, in the DNA of BD-exposed mice and rats. Higher amounts of 2HB1G and 1HB2G appeared in rat urine compared with mouse urine after the 10-day exposure to 1,250 ppm BD. Analysis of liver DNA for N7-guanine adducts derived from BDO2 revealed the presence of two diastereomeric forms of N7-(2,3,4-trihydroxybutyl)-1-guanine (THBG). One of the diastereomers [(+/-)-THBG] was formed by reaction of DNA with (+/-)-BDO2 or BDO-diol, and the other diastereomer (meso-THBG) was formed by reaction of DNA with meso-BDO2 or BDO-diol. There was more (+/-)-THBG and meso-THBG in liver DNA of mice compared with amounts in rats during the 10 days of BD exposure and the 6 days after exposure. A twofold excess of (+/-)-THBG over meso-THBG in rat liver was found at all of the time points monitored. After 10 days of exposure to BD, (+/-)-THBG in mouse liver was also present in an almost twofold excess over meso-THBG. At 6 days after exposure to BD, however, (+/-)-THBG and meso-THBG were present in almost equal amounts in mouse liver. Furthermore, amounts of the two THBG diastereomers in mouse liver 6 days after exposure to BD were almost fivefold greater than amounts in rat liver. The half-lives of (+/-)-THBG and meso-THBG appeared to be longer in mouse liver (4.1 days and 5.5 days, respectively) than in rat liver (3.6 days and 4.0 days, respectively). Higher amounts of (+/-)-THBG were excreted in rat urine compared with mouse urine. It is noteworthy that each of the N7-guanine adducts derived from BD was present in higher concentrations in the liver DNA of mice exposed to 1,250 ppm BD than in the liver DNA of rats exposed to the same dose. Conversely, each of the adducts was present in higher concentrations in the urine of rats compared with the urine of mice after exposure to 1,250 ppm BD.

1,3-butadiene: cancer, mutations, and adducts. Part III: In vivo mutation of the endogenous hprt genes of mice and rats by 1,3-butadiene and its metabolites.

Walker VE, Meng Q

Res Rep Health Eff Inst · 2000 Mar · PMID 10925840

1,3-Butadiene (BD), an important chemical used mainly in the production of synthetic rubber, is a potent carcinogen in mice, a weak carcinogen in rats, and a suspected carcinogen in humans. To provide a better understand... 1,3-Butadiene (BD), an important chemical used mainly in the production of synthetic rubber, is a potent carcinogen in mice, a weak carcinogen in rats, and a suspected carcinogen in humans. To provide a better understanding of the mutagenic mechanisms involved in interspecies differences in BD-induced carcinogenesis, studies were conducted in rodents to test two hypotheses: (a) the mutagenic potency of BD at the hypoxanthine-guanine phosphoribosyltransferase (hprt) locus of T lymphocytes (T cells) can be used to quantify interspecies differences in BD-induced carcinogenicity in exposed rodents and (b) comparison of the mutagenic potency and specificity of BD and racemic mixtures of two epoxy metabolites, 1,2-epoxy-3-butene (BDO) and 1,2,3,4-diepoxybutane (BDO2), at the hprt locus of T cells can be used to define the relative contribution of each intermediate to observed BD mutagenicity in each species. The first hypothesis was investigated by determining the effects of exposure duration and elapsed time after exposures on hprt mutant frequencies (MFs) in T cells from thymus and spleen of female B6C3F1 mice and F344 rats (4 to 5 weeks old). In this study, rodents were exposed by inhalation to 0 or 1,250 parts per million (ppm) BD for up to 2 weeks, or to 0 or 625 ppm BD for up to 4 weeks (with all exposures 6 hours/day, 5 days/week). The second hypothesis was examined by defining the effects of exposure concentration and elapsed time after exposures on the hprt MFs in splenic T cells from mice and rats exposed by inhalation to BD (0, 20, 62.5, or 625 ppm), BDO (0, 2.5, or 25 ppm), or BDO2 (0, 2, or 4 ppm) for 4 weeks (all exposures 6 hours/day, 5 days/week). The hprt MFs were measured weekly or biweekly using the T cell cloning assay for up to 10 weeks after the last exposure. The mutagenic potency of BD (represented by the difference in the areas under the mutant T cell "manifestation" curves [or the "change in MFs over time"] of exposed versus control animals) was significantly greater in mice (4.4-fold) than in rats following 2 weeks of exposure to 1,250 ppm BD. Mutagenic potency in mice was 8.5-fold greater than that in rats following 4 weeks of exposure to 625 ppm BD. These hprt MF data provide the first evidence that BD is mutagenic in the rat, albeit the mutagenic response was significantly less than that observed in similarly exposed mice. In addition, the MF data from the two exposure-duration studies indicate that both exposure concentration and exposure duration are important in determining the magnitude of the mutagenic response to BD. The relative contribution of BDO versus BDO2 to overall BD mutagenicity was evaluated by exposing mice and rats to carefully chosen concentrations of BD and racemic mixtures of BDO and BDO2 (that is, 62.5, 2.5, and 4.0 ppm, respectively) and comparing the mutagenic potency of each compound when comparable blood levels of metabolites were achieved. The resulting MF data indicate that (+/-)-BDO2 is a major contributor to the mutagenicity of BD in mice at lower BD exposure levels (< or = 62.5 ppm), whereas other metabolites and stereochemical configurations are responsible for mutations in BD-exposed rats and for the incremental mutagenic effects at higher exposure levels in mice. Molecular analysis of hprt cDNA from expanded T cell clones from control and BD-exposed mice demonstrated an increased frequency of large deletions in exposed animals (p = 0.016), presumably associated with in situ formation of (+/-)-BDO2, meso-BDO2, or both. Results of these mutagenicity experiments, along with data from collaborative studies of DNA adducts from the same animals, should provide a better understanding of the interspecies variation in carcinogenic response to BD and improve the extrapolation of rodent data to the estimation of cancer risk in exposed persons.

1,3-butadiene: cancer, mutations, and adducts. Part II: Roles of two metabolites of 1,3-butadiene in mediating its in vivo genotoxicity.

Recio L, Saranko CJ, Steen AM

Res Rep Health Eff Inst · 2000 Mar · PMID 10925839

1,3-Butadiene (BD) is carcinogenic in mice and rats, with mice being more susceptible than rats to its carcinogenic effects. 1,3-Butadiene is mutagenic in the bone marrow and spleen cells of B6C3F1 lacI transgenic mice.... 1,3-Butadiene (BD) is carcinogenic in mice and rats, with mice being more susceptible than rats to its carcinogenic effects. 1,3-Butadiene is mutagenic in the bone marrow and spleen cells of B6C3F1 lacI transgenic mice. The goal of this research was to assess the roles of two BD metabolites, 1,2-epoxy-3-butene (BDO) and 1,2,3,4-diepoxybutane (BDO2), in the mutagenicity and mutational spectrum of the parent compound BD by determining the mutagenicity and mutational spectra of BDO and BDO2 in human and rodent cells in vitro and in vivo. In human TK6 lymphoblastoid cells (TK6 cells), BDO exposure increased the frequency of G.C-->A.T transitions and A.T-->T.A transversions (Fisher exact test; p < 0.05). The most striking difference in the type of base-substitution mutations between BDO-exposed and BDO-unexposed TK6 cells was the 19-fold increase in A.T-->T.A transversions. 1,2,3,4-Diepoxybutane increased the frequency of A.T-->T.A transversions (Fisher exact test; p < 0.05) and the frequency of deletions in exposed TK6 cells compared with unexposed controls. Exposure of Rat2 lacI transgenic fibroblasts (Rat2 cells) to BDO increased the frequency of three types of base-substitution mutations: G.C-->A.T transitions, G.C-->T.A transversions, and A.T-->T.A transversions. Exposure of Rat2 cells to BDO2-induced dose-dependent increases in micronuclei at exposure levels that apparently did not induce mutagenicity at the lacI transgene. The lack of detectable mutagenicity at the lacI transgene in Rat2 cells exposed to BDO2 probably reflects the poor recovery of large deletions by this lambda phage-based mutagenicity assay. Inhalation exposure of B6C3F1 lacI transgenic mice (lacI mice) and F344 lacI transgenic rats (lacI rats) to BDO (29.9 parts per million [ppm]; 6 hours/day; 5 days/week for 2 weeks) did not increase the lacI mutant frequency (MF) in bone marrow or spleen cells of mice and rats, but in the cells of mouse lung (a tumor target organ for BD), significant mutagenicity was observed. An increased lacI MF was also observed in the bone marrow cells of rats exposed to BDO. Inhalation exposure of lacI mice and lacI rats to BDO2 (3.8 ppm; 6 hours/day; 5 days/week for 2 weeks) did not increase the lacI MF in bone marrow or spleen cells of mice or in the spleen cells of rats. An increased lacI MF was observed in the bone marrow cells of rats exposed to BDO2. In the present study, BDO specifically induced G.C-->A.T and A.T-->T.A transversions in vitro at both the endogenous hypoxanthine phosphoribosyltransferase (hprt) gene and the lacI transgene in Rat2 cells. It also induced an increased frequency of G.C-->T.A transversions in Rat2 cells. These types of mutations also occur at an increased frequency in mice exposed to the parent compound, BD. This finding demonstrates the induction of consistent mutational types across biological systems by BDO and indicates that BDO, but not BDO2, probably has a role in mediating the mutations recovered at the lacI transgene in animals exposed to the parent compound, BD. Therefore, it is apparent that in mice exposed to BD at carcinogenic levels, BDO and BDO2 act in concert to mediate the range of genotoxic responses. These data demonstrate that certain DNA adducts (guanine or adenine) may be useful biomarkers for BD genetic effects. However, other DNA lesions that can account for BDO2-induced deletions and chromosomal alterations also need to be considered as biomarkers for BD-induced genotoxicity.

1,3-butadiene: cancer, mutations, and adducts. Part I: Carcinogenicity of 1,2,3,4-diepoxybutane.

Henderson RF, Barr EB, Belinsky SA … +3 more , Benson JM, Hahn FF, Ménache MG

Res Rep Health Eff Inst · 2000 Mar · PMID 10925838

Reports in the literature suggest that one reason for the greater sensitivity of mice to the carcinogenicity of 1,3-butadiene (BD) is that exposed mice metabolize much more of the BD to 1,2,3,4-diepoxybutane (BDO2) than... Reports in the literature suggest that one reason for the greater sensitivity of mice to the carcinogenicity of 1,3-butadiene (BD) is that exposed mice metabolize much more of the BD to 1,2,3,4-diepoxybutane (BDO2) than do exposed rats. The purpose of this study was to determine the tumorigenicity of BDO2 in rats and in mice exposed to the same concentration of the agent. Female B6C3F1 mice and Sprague-Dawley rats, 10 to 11 weeks old, 56 per group, were exposed by inhalation to 0, 2.5, or 5.0 ppm BDO2, 6 hours/day, 5 days/week for 6 weeks. Preliminary dosimetry studies in rodents exposed for 6 hours to 12 ppm BDO2 indicated that blood levels would be expected to be approximately 100 and 200 pmol/g at the two exposure concentrations in the rat and twice those levels in the mouse. During the 6-week exposure, the mice at the high exposure level showed signs of labored breathing during the last week, and four mice died. In the others, however, the respiratory symptoms disappeared after exposure ended. Rats showed no clinical signs of toxicity during exposure but developed labored breathing after the end of the exposure leading to the death of 13 rats within 3 months. At the end of the exposure, some animals (8 per group) were evaluated for the acute toxicity resulting from the BDO2 exposure. The remaining exposed rats and mice were held for 18 months for observation of tumor development. At the end of the exposure, rats had no biologically significant alteration in standard hematological parameters, but mice had a dose-dependent increase in neutrophils and decrease in lymphocytes. In both species the significant histopathologic lesions were in the nose, concentrated around the main airflow pathway. Necrosis, inflammation, and squamous metaplasia of the nasal mucosa, as well as atrophy of the turbinates, were all present at the end of exposure to 5.0 ppm. Within 6 months, necrosis and inflammation subsided, but squamous metaplasia remained in the mice. In rats that died after exposure, squamous metaplasia was seen in areas of earlier inflammation and, in other rats, extended beyond those areas with time. The metaplasia was severe enough to restrict and occlude the nasopharyngeal duct. Later, keratinizing squamous cell carcinomas developed from the metaplastic foci in rats but not mice. At the end of 18 months, the only significant increase in neoplasia in the exposed rats was a dose-dependent increase in neoplasms of the nasal mucosa (0/47, 12/48, and 21/48 for the control, 2.5 ppm, and 5.0 ppm exposures, respectively). Neoplasia of the nasal mucosa did not increase significantly in the mice; neoplastic lesions in the mice were observed in reproductive organs, lymph nodes, bone, liver, Harderian gland, pancreas, and lung. The only significant increase in neoplasms in a single organ in the mice was in the Harderian gland (0/40, 2/42, and 5/36 for the control, 2.5 ppm, and 5.0 ppm exposures, respectively). This tumor accounts for the apparent trend toward an increase in total neoplastic lesions in mice as a function of dose (10/40, 7/42, and 16/36 for control, 2.5 ppm, and 5.0 ppm exposures, respectively). These findings indicate that the metabolite of BD, BDO2, is carcinogenic in the respiratory tract of rats. An increase in respiratory tract tumors was not observed in similarly exposed mice despite the fact that preliminary studies indicated mice should have received twice the dose to tissue compared with the rats. High cytosolic activity of detoxication enzymes in the mouse may account, in part, for the differences in response.

Effects of concentrated ambient particles in rats and hamsters: an exploratory study.

Gordon T, Nadziejko C, Chen LC … +1 more , Schlesinger R

Res Rep Health Eff Inst · 2000 Apr · PMID 10897487

Considerable controversy surrounds the biological plausibility of adverse effects from exposure to ambient particulate matter (PM)*, chiefly because these adverse effects have been observed at particle mass concentration... Considerable controversy surrounds the biological plausibility of adverse effects from exposure to ambient particulate matter (PM)*, chiefly because these adverse effects have been observed at particle mass concentrations below those that have been shown to produce effects in healthy animals and human volunteers in the laboratory. To address this research gap, we examined the potential for concentrated ambient PM to produce pulmonary and cardiovascular changes in compromise rodent models. Normal healthy and monocrotaline-treated rats received single or multiple exposures to concentrated ambient PM, and their responses were tested using functional, cellular, biochemical, and histological endpoints. Analyses determined that no changes in pulmonary function or structure occurred after exposure to concentrated ambient PM. Cardiac arrhythmias did not increase after PM exposure in normal or monocrotaline-treated rats. Increased atrial conduction time, accompanied by a decrease in the duration of the T wave portion of the electrocardiogram (ECG) waveform, was observed in PM-exposed monocrotaline-treated rats in one experiment. In addition, on several but not all exposure days, small yet statistically significant increases in heart rate and peripheral blood cell differential counts were observed in normal and monocrotaline-treated rats within 6 hours after exposure to concentrated ambient PM. The observed changes in cardiovascular parameters in rats returned to control values by 24 hours after exposure. In a hamster cardiomyopathy model, no adverse cardiac or pulmonary changes were detected after exposure to concentrated ambient PM. Thus, these studies found that cardiopulmonary effects could be produced in rats, but not in hamsters with cardiomyopathy, exposed to concentrated ambient PM. None of the changes occurred on every exposure day and none appeared to be life threatening. Thus, the cardiac changes may reflect changes in homeostasis that could affect individuals who are critically ill, and these findings do not resolve the biological plausibility of adverse health effects associated with ambient PM in epidemiologic studies.

Mechanisms of morbidity and mortality from exposure to ambient air particles.

Godleski JJ, Verrier RL, Koutrakis P … +10 more , Catalano P, Coull B, Reinisch U, Lovett EG, Lawrence J, Murthy GG, Wolfson JM, Clarke RW, Nearing BD, Killingsworth C

Res Rep Health Eff Inst · 2000 Feb · PMID 10817681

The studies reported here assessed pathophysiologic mechanisms that result from exposure to concentrated ambient particles (CAPs) in animals with and without cardiopulmonary compromise. These studies were carried out to... The studies reported here assessed pathophysiologic mechanisms that result from exposure to concentrated ambient particles (CAPs) in animals with and without cardiopulmonary compromise. These studies were carried out to determine the biologic plausibility of epidemiologic observations of increases in particulate air pollution associated with increases in human morbidity and mortality. Dogs were exposed two at a time to CAPs or filtered air via tracheostomy for six hours per day on three consecutive days. The electrocardiogram (ECG) and breathing pattern were recorded continuously, and indicators of inflammation were also assessed. In one experimental design, normal dogs were exposed in pairs to CAPs and subsequently to filtered air or to filtered air and subsequently CAPs (the double CAPs/double sham design). Comparisons were made between the CAPs measurements and each dog's own sham responses. In another design, one dog was exposed to CAPs while the chambermate received a sham exposure; these experiments were followed by crossover of the protocol the subsequent week (the crossover design). Comparisons were made between the CAPs exposure and both the chambermate's sham and each dog's own sham responses. The crossover experiments were conducted in normal animals and in animals who had undergone balloon occlusion of the left anterior descending (LAD) coronary artery to induce myocardial compromise. The effects of CAPs in animals with induced chronic bronchitis were part of the original specific aims; because these studies were not fully pursued, the results are presented only in Appendix A. In normal dogs, analyses of all double CAPs and crossover studies revealed low frequency (LF) and high frequency (HF) powers for heart rate variability (HRV) that were significantly higher for CAPs exposure compared to sham exposure. Variation in day-to-day exposure concentrations, aerosol composition, and pathophysiologic responses were also found. The crossover design, continuous measures of aerosol mass, and biologic responses were incorporated in the development of a statistical model that allowed isolation of changes associated with CAPs from changes due to animal variations. Comparison of individual exposures with this model revealed a range from no response in any measured parameter to statistically significant changes in cardiac autonomic balance, pulmonary air flow, and breathing pattern. On days in which dogs showed statistically significant changes in responses, the findings were consistent in both cardiac and respiratory parameters. Days associated with significant increases in LF and HF HRV, LF/ HF HRV ratio, and heart rate standard deviation (HR SD) were also associated with decreases in average heart rate. These same days had decreases in respiratory frequency, tidal volume, minute volume, and peak flows with corresponding increases in respiratory cycle times and enhanced pause (Pauenh), a measure of bronchoconstriction. These cardiac and respiratory changes suggest an effect mediated via both the sympathetic nervous system and the vagus nerve. Alternatively, days associated with increased heart rate had decreases in the HR SD; decreases or no change in HF and LF HRV; increases in respiratory flows and volumes; and decreases in breathing cycle times, all suggesting only sympathetic nervous system mediation. When all data from the crossover design experiments were assessed with this model, the heart rate and respiratory rate were significantly decreased in relation to both cumulative and actual exposure and the LF HRV, LF/HF HRV ratio, HR SD, and all other respiratory parameters were significantly increased (p < 0.0001 for all). When cardiac data were grouped by days in which the air mass trajectory came from the north or northwest (versus west, south, east, or northeast), significant increases in HR SD and HF HRV and significant decreases in average heart rate were associated with the northwest trajectory. (ABSTRACT TRUNCATED)
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