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Stroke Research and Treatment
Volume 2012 (2012), Article ID 824724, 7 pages
Sulfur Dioxide and Emergency Department Visits for Stroke and Seizure
1Population Studies Division, Health Canada, Ottawa, ON, Canada K1A 0K9
2Department of Emergency Medicine, Providence Health Care and St. Paul’s Hospital, Vancouver, BC, Canada V6Z 1Y6
Received 10 December 2011; Revised 10 January 2012; Accepted 10 January 2012
Academic Editor: Halvor Naess
Copyright © 2012 Mieczysław Szyszkowicz et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.
The purpose of this study was to assess an association between ambient sulfur dioxide and the number of emergency department (ED) visits for ischemic stroke and seizure. The study used data collected in a Vancouver (Canada) hospital in the years 1999–2003. Daily ED visits diagnosed as ministroke, stroke, or seizure were investigated using the case-crossover technique. Conditional logistic regression models were applied to estimate the odds ratios (ORs) and their respective 95% confidence intervals (CIs). The models included temperature and relative humidity in the form of natural splines. The results were reported for an increase in interquartile range ((IQR), ppb for SO2). Positive and statistically significant associations were obtained for SO2 and ischemic stroke for all patients (; CI 1.02, 1.23; lag 3) and for female patients (; CI 1.01, 1.33; lag 0). In the case of ED visits for seizure, for female patients the results were also statistically significant (; CI 1.02, 1.28; lag 1 and ; CI 1.05, 1.32; lag 2). These findings suggest that cases of ischemic cerebrovascular accidents are associated with acute exposure to ambient sulfur dioxide.
The toxic, oxidative, and irritating properties of gaseous air pollutants are recognized health hazards [1, 2]. Ambient sulfur dioxide (SO2) is considered a risk factor for ischemic stroke and seizure, yet the mechanism of its effects on the brain is not currently readily understood. The gas when breathed in dissolves in the mucus lining of the upper respiratory tracts and thus affects their mechanical function, which may result in bronchoconstriction [3–5]. Connections between this syndrome and short-term exposure to SO2 have been reported . Clinical assays suggested a synergism between this action of SO2 and a prior exposure to ozone . But SO2 exposure arguably exacerbates the states of cardiopulmonary and cardiovascular diseases and increases the risk of premature death from circulatory system causes, including ischemic stroke [8–13]. The involvement of SO2 may be challenged on the basis that it tends to be correlated with toxic combustion particles , yet pathophysiologic images of animal stroke model after inhalation of SO2 show brain injuries similar to those caused by cerebral ischemia .
Understanding how exposure to SO2 causes the onset of brain ischemia would be helpful in preventing devastating health effects. Air pollution may affect the brain through multiple pathways, which are better understood in the case of photochemical pollutants causing neurodegeneration [2, 16], yet the pathway may include depression and symptoms of depression, which are risk factors for cerebral ischemia and stroke [17–24]. The ischemic injury caused by pollutants and the onset of stroke in patients affected by depression may involve the same pathophysiologic mechanism of action . However, studies have found no associations between the presence of depressive symptoms and the risk of stroke in women, while SO2 associations are only found for women .
The present study contributes to the observations of the impact of four gaseous pollutants and two types of particulate matter on ED presentations of ischemic stroke and seizure. A seizure is often caused by conditions that reduce the supply of oxygen to brain cells, so this diagnosis is also included in the analysis . This study mainly focused on sulfur dioxide exposure and ED visits for stroke or seizure. While the impact of the pollutants on the central nervous system is convoluted, a general pattern appears: sulfur dioxide contributes significantly to the occurrences or symptoms of cerebrovascular ischemia and seizure.
2. Materials and Methods
2.1. Study Population
The study population includes all patients serviced in the period from January 1999 to February 2003 by St. Paul’s Hospital located in downtown Vancouver, BC. During that time the hospital was providing emergency health services for approximately 53,000 patients per year, with an admission rate of 15%. A total of 194,443 visits with subsequent diagnoses were registered. The emergency physicians recorded the discharge diagnoses in ED charts using standardized medical vocabulary. The cases were identified using the corresponding standardized strings. The presentations of mini-stroke and stroke were recorded as transient ischemic attack () and cerebrovascular accident-ischemic (), respectively. These two diagnosed health conditions were combined and summarized to 1002 (females = 449) cases. ED visits with the diagnosis of seizure were retrieved and totaled 2120 (females = 597) cases.
2.2. Meteorological Data
Environment Canada supplied hourly data for temperature, relative humidity, and atmospheric pressure for the city of Vancouver. We used the daily means of two weather parameters: temperature (dry bulb) and relative humidity. Each of these was calculated as an average of 24 hourly measurements.
2.3. Air Pollution Data
Hourly data for gaseous pollutants (concentrations of CO, NO2, SO2, and O3) and particulate matter (PM, PM10, and PM2.5-PMs of less than 10 and 2.5 μm in aerodynamic diameter, resp.) supplied by Environment Canada were obtained from a number of fixed continuous monitoring stations in the greater Vancouver area. During the study period (4 years and 2 months), the number of monitoring stations that reported air pollution data ranged from 4 to 11. The distances of stations from the hospital varied from 3 to 43 kilometers. The measurements of the common daily exposure were obtained by first averaging the 24 hourly readings in each functioning station and next averaging across the stations.
2.4. Statistical Methods
Case-crossover methods are suitable for the estimation of odds of acute health effects triggered by acute and transient exposures . The design is an adaptation of the case-control approach where the case serves as his/her own control. For each presented case of ischemia or seizure, the patient’s exposure to pollutants on the case day (the day of admission or an earlier day when considering a lagged effect) was compared to the exposure on referent days when the patient has not been affected. The referent days were selected in a way to match year, month, and day of week of the case day, so that each case had 3 or 4 controls.
Conditional logistic regression analysis was used to estimate the odds ratios (ORs) with 95% confidence intervals (CIs) associated with an increase by conventional unit in the concentrations of pollutants. In order to compensate for possible nonlinear effects of the weather conditions (temperature, relative humidity), natural splines of the weather parameters, with 3 degrees of freedom, were incorporated into the regression models. Potential links between a pollutant and a health outcome were evaluated with single-pollutant models in order to assess the stability of the method and the causal nature of the association. The analysis was performed for all realistic combinations of the gaseous pollutants and PMs, individually lagged with different 0- to 7-day lags. The calculations were performed using the PHREG procedure in SAS.
In addition, we constructed the sequence of the age groups as follows: (0, 29), (1, 30), and so on up to (56, 85). Thus, each age group spans 30 years. It was chosen arbitrarily and was driven by number of ED visits. For larger number of cases the groups may have shorter span. The first age group (0, 29) contains the patients not older than 30 years. The next (1, 30) has patients older than 1 year of age and younger than 31, and so on. For each age group the calculations were performed separately for the health outcomes considered here, that is, stroke and seizure. This analysis was performed only for females and the same-day exposure (lag 0) to sulfur dioxide. The results were compared with similar calculations done for female ED visits for depression and anxiety.
3. Results and Discussion
The mean value of temperature during the study period was 7.7°C, with a standard deviation (SD) of 11.4. Relative humidity had a mean value of 70.7%, with SD = 12.5. These values reflect the generally tepid and humid weather in the city of Vancouver and its surroundings. For the gaseous pollutants, the point statistics are as shown in Table 1.
In the case of particulate matter, the corresponding statistics are as shown in Table 2.
The average pollution levels in Vancouver are comparable to those in other large urban regions in Canada, but Vancouver’s ozone level is among the lowest in Canada [29, 30]. Mostly suburban areas had higher ozone levels and were showing larger-range variation than that for downtown Vancouver, where the St. Paul’s Hospital is located.
The results for ED visits for stroke are reported in Figure 1. The figure has three parts (in a horizontal direction) and shows the estimated ORs and their corresponding 95% CIs for six considered air pollutants (lagged by 0–7 days) for all (a), male (b), and female (c) patients, respectively. The results are shown numerically and are also represented graphically as barlines. The results were positive and significant for all patients for exposure to CO (lag 4) and SO2 (lag 3), and none was significant in the case of male patients. For female patients the results were statistically significant () for CO (lag 0), PM10 (lag 1), and SO2 (lag 0). Table 3 presents the results from multipollutant models. In these models different combinations of lagged exposure were used. For example in the two-pollutant model SO2 (lag 3) + O3 (lag 6), early exposure to ozone (6 days before the event) increases effect of sulfur dioxide, and in this case OR = 1.16 (95% CI: 1.05, 1.29). In this case weather parameters were used with lag 0.
Figure 2 is constructed in a similar manner as Figure 1 and represents the results for ED visits for seizure. As in all cases, the results are reported for an increase in concentration of the air pollutant represented by its one IQR. The results were positive and significant for all patients and for male patients and exposure to PM10 (lag 1, lag 4). For female patients, the association was significant for SO2 (lag 1 and 2) and ozone (lag 7).
Figure 3 represents the results for ED visits for stroke, seizure, depression, and anxiety for age groups of length 30 years. The results are shown for SO2 exposure on the same day as the health event. The pattern of responses (OR values and their respective 95% CIs) is very similar for seizure and depression. For anxiety, the pattern is weak but slightly similar for both mentioned health conditions .
Figure 4 illustrates levels of the gaseous air pollutants (CO, NO2, SO2, and O3) and daily number of ED visits for stroke (a) and for seizure (b). The figure indicates periodicity of carbon monoxide, nitrogen dioxide, and ozone. It also suggests that levels of ambient sulfur dioxide are decreasing.
The acute and often severe nature of symptoms of stroke and seizure results in the affected individuals first seeking help in the ED rather than in a doctor’s office. This allows the frequency of ED visits for these disorders to be considered an adequate measure of the actual occurrences of the disorders in the examined population . The presented results show that ambient sulfur dioxide constitutes a cerebrovascular health hazard, particularly for the female population. The findings in this study corroborate those in other studies on sulfur dioxide neurophysiologic effects . They suggest that inhalation of SO2, rather than O3, may initiate a cerebral ischemic accident, causing specific pathophysiological effects on the brain. The mechanism has no analogy to the way bronchoconstriction occurs in vulnerable subjects exposed to SO2, where rather acidic compounds derived from CO and SO2 appear as agents of toxicity [33–38]. This suggests that SO2 may follow its own biochemical pathway of breaking through or penetrating the brain’s protective barrier. The consequences appear to be stronger in the female population than in the male population. This calls for more clinical inquiry into the sulfur dioxide mediation mechanism in developing abnormal brain neural activity or brain ischemia.
The results of the current study should be considered in the context of its limitations. Regional estimates of exposure may not have correlated with patient-level exposures prior to visits to the ED, which would bias the risk estimates towards the null. Possible correlation between health outcome severity and patient age and sex was not captured due to the limited number of observations. Some patients may have repeat visits to the emergency department for follow-up, and those visits would not be correlated to concentrations of air pollutants. While time-stable confounders (e.g., genetics and chronic diseases) are controlled for by the case-crossover study design, confounders that fluctuate in time may not have been controlled. Weather parameters (i.e., temperature and humidity) were adjusted in the analysis; however, measurements of acid aerosol concentrations were not available. Thus, future studies will be needed to replicate our findings and confirm that the increased risks of cerebral ischemia manifestations as stroke and seizures were due to the specific combinations of exposures.
This study suggests novel modifiable risk factors for ischemic stroke and seizure. Increases in concentrations of ambient sulfur dioxide were associated with increased probability of emergency department visit for ischemic cerebral accidents or transient ischemia. If these findings are confirmed, prevention of some cases of stroke or seizure may be achieved by improving air quality, or by better regulating the allowable levels of exposures to ambient gases in the workplaces.
The authors appreciate the efforts of Health Canada in securing these data and funding data acquisition.
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