Number Concentration and Mass Concentration as Determinants of Biological Response to Inhaled Irritant Particles

Characterization of particle number concentrations and PM2.5 in a school: influence of outdoor air pollution on indoor air

BACKGROUND, AIM AND SCOPE

The impact of air pollution on school children's health is currently one of the key foci of international and national agencies. Of particular concern are ultrafine particles which are emitted in large quantities, contain large concentrations of toxins and are deposited deeply in the respiratory tract.

MATERIALS AND METHODS

In this study, an intensive sampling campaign of indoor and outdoor airborne particulate matter was carried out in a primary school in February 2006 to investigate indoor and outdoor particle number (PN) and mass concentrations (PM(2.5)), and particle size distribution, and to evaluate the influence of outdoor air pollution on the indoor air.

RESULTS

For outdoor PN and PM(2.5), early morning and late afternoon peaks were observed on weekdays, which are consistent with traffic rush hours, indicating the predominant effect of vehicular emissions. However, the temporal variations of outdoor PM(2.5) and PN concentrations occasionally showed extremely high peaks, mainly due to human activities such as cigarette smoking and the operation of mower near the sampling site. The indoor PM(2.5) level was mainly affected by the outdoor PM(2.5) (r = 0.68, p < 0.01), whereas the indoor PN concentration had some association with outdoor PN values (r = 0.66, p < 0.01) even though the indoor PN concentration was occasionally influenced by indoor sources, such as cooking, cleaning and floor polishing activities. Correlation analysis indicated that the outdoor PM(2.5) was inversely correlated with the indoor to outdoor PM(2.5) ratio (I/O ratio; r = -0.49, p < 0.01), while the indoor PN had a weak correlation with the I/O ratio for PN (r = 0.34, p < 0.01).

DISCUSSION AND CONCLUSIONS

The results showed that occupancy did not cause any major changes to the modal structure of particle number and size distribution, even though the I/O ratio was different for different size classes. The I/O curves had a maximum value for particles with diameters of 100-400 nm under both occupied and unoccupied scenarios, whereas no significant difference in I/O ratio for PM(2.5) was observed between occupied and unoccupied conditions. Inspection of the size-resolved I/O ratios in the preschool centre and the classroom suggested that the I/O ratio in the preschool centre was the highest for accumulation mode particles at 600 nm after school hours, whereas the average I/O ratios of both nucleation mode and accumulation mode particles in the classroom were much lower than those of Aitken mode particles.

RECOMMENDATIONS AND PERSPECTIVES

The findings obtained in this study are useful for epidemiological studies to estimate the total personal exposure of children, and to develop appropriate control strategies for minimising the adverse health effects on school children.

In vitro assessment of the inflammatory response of respiratory endothelial cells exposed to particulate matter

Particulate matter (PM) is a ubiquitous environmental pollutant that has been associated with increased risk of cardiopulmonary mortality and morbidity in urban communities. An increasing body of evidence suggests that inflammation induced by PM may play an important role in the development of cardiovascular diseases. However, airway epithelial cell lines, instead of vascular endothelial cells, are commonly used to investigate the effects of PM with respect to cardiovascular effects. Thus, the present study was conducted using primary human vascular endothelial cells (HMVEC-LB1), human white blood cells (WBC), and their cocultures to evaluate their inflammatory responses to various PM exposures. Enzyme-linked immunosorbent assay (ELISA) kits were used to measure the concentrations of interleukin (IL)-6, soluble intercellular adhesion marker (sICAM-1), and soluble vascular cell adhesion marker (sVCAM-1) in HMVEC-LB1, WBC, and their cocultures after exposure to size-fractionated PM. Pretreatment of cells with inhibitors was performed in order to examine pathways involved in PM-induced cellular responses. IL-6 levels increased significantly in HMVEC-LB1 cells exposed to PM in both a time- and concentration-dependent manner. However, particle exposure for up to 24 h failed to induce any detectable production of sICAM-1 or sVCAM-1 in HMVEC-LB1 cells. IL-6 production in response to size-fractioned PM exposures failed to show evidence of relative importance of particle sizes in their abilities to induce proinflammatory responses. Lastly, cocultures with WBC significantly enhanced particle induced IL-6 release in HMVEC-LB1 cells in a synergistic manner. The present study suggests that HMVEC-LB1 cells can be successfully used as an in vitro model to examine effects of PM exposure.

Urban air particulate inhalation alters pulmonary function and induces pulmonary inflammation in a rodent model of chronic bronchitis

Epidemiological studies have reported increased morbidity in human populations following inhalation of elevated levels of urban particulate matter. These responses are especially prevalent in populations with chronic obstructive pulmonary diseases, including chronic bronchitis. Toxicological studies have reported altered pulmonary function and increased pulmonary inflammation following particulate inhalation in the laboratory setting. However, most of these studies have utilized artificial particles that may not accurately mimic outdoor air pollutant conditions. Few studies have utilized actual urban air particle samples in inhalation studies. In the present study, the effects of inhaled concentrated urban air particulates on pulmonary function and pulmonary inflammation are addressed. Normal rats and rats with chronic bronchitis induced by approximately 200 ppm SO(2) for 6 wk were subsequently subjected to filtered air or concentrated air particles (CAPs). Twelve rats per group in 4 groups (48 rats total) were exposed for 5 h/day for 3 consecutive days. The CAPs aerosol levels were 206, 733, and 607 microg/m(3) (MMAD = 0.18 microm, sigma(g) = 2.9) on days 1, 2, and 3, respectively. Following the final day of exposure, pulmonary function parameters, including peak expiratory flow (PEF), tidal volume (TV), respiratory frequency (RF), and minute volume (MV), were measured and compared to preexposure baseline levels. Twenty-four hours following the final day of exposure, bronchoalveolar lavage was performed for total cell counts, differential cell counts, and total lavage protein levels. Pulmonary responses to CAPs in chronic bronchitic animals indicated a significant increase in tidal volume as well as peak expiratory flow. In CAPs-exposed animals without underlying bronchitis, significantly increased tidal volume was observed. Significant pulmonary inflammation was observed in the CAPs-exposed animals, particularly those with chronic bronchitis. Significant increases in neutrophils, lymphocytes, and total lavage protein were observed. These results suggest two distinct mechanistic responses to inhaled particles: a stress-type pulmonary function response marked by increases in flow and volume, that is, deeper breathing; and acute pulmonary inflammation marked by cellular influx, particularly neutrophils. From these data it is concluded that inhaled urban air particles alter pulmonary breathing parameters and increase pulmonary inflammation.

Interaction of gaseous and particulate pollutants in the respiratory tract: mechanisms and modulators

Human contact with air pollution usually involves exposure to more than one chemical, and biological responses to the inhalation of polluted atmospheres likely depend upon the interplay between individual materials. Thus, characterizing effects from exposures to mixtures of air pollutants is necessary for adequate quantitation of health risks. Exposure to gas/particle mixtures may result in respiratory tract responses which are additive, or reflect synergistic or antagonistic interactions. The occurrence and type of interaction depends upon numerous factors, including the biological endpoint being examined and the specific exposure conditions, such as concentration, duration, and the physicochemical characteristics of the exposure atmosphere. It is, therefore, not always possible to predict solely from the presence of certain pollutants in a complex atmosphere exactly whether there will be an interaction and, if so, what type it will be. This complicates attempts to relate responses observed in laboratory studies of mixtures to those which may occur under ambient patterns of exposure, an extrapolation needed for human risk assessment.