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Table 1.

Number of hospitalizations for acute myocardial infarction in Alberta subgroups (1999–2009).

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Fig 1.

Seasonal trends of monthly average frequency of AMI hospitalizations and monthly average concentrations of air pollutants (April 1999 –March 2010).

Monthly frequency of AMI hospitalizations (1 unit = 100) were the average number of events by month. Monthly average concentration levels of CO (1 unit = 1 mg/m3), NO (1 unit = 10 μg/m3), NO2 (1 unit = 10 μg/m3), O3 (1 unit = 10 μg/m3), or PM2.5 (1 unit = 10 μg /m3) were averaged by month in which the daily mean concentrations linked to the event days.

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Table 2.

Step 2 multivariate analysis with full adjustment results (p-value ≤0.05).

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Table 3.

Step 3 Bootstrap model averaging results.

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Fig 2.

Adverse associations between air pollutants and AMI hospitalizations with frequency over 700 of 1,000 bootstrap replications.

AGECAT2 = age ≥65; NSTEMI = Non-ST Segment Elevation Myocardial Infarction; HTN = Hypertension. OR estimates calculated by bootstrap model averaging of 1,000 replications for an inter-quintile range increase of NO2_AVE (28.2 μg/m3), NO2_AVE12 (30.1 μg/m3), NO2_AVE6 (34.2 μg/m3). Freq represents frequency that a variable had p-value ≤0.05 from 1,000 model replications.

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Fig 3.

Comparison of 1-day lag NO2 concentration effects in subgroups defined by age and type of AMI.

AGECAT1 = age <65; AGECAT2 = age ≥65; STEMI = ST Segment Elevation Myocardial Infarction; NSTEMI = Non-ST Segment Elevation Myocardial Infarction. OR estimates calculated by bootstrap model averaging of 1000 replications for an inter-quintile range increase of NO2_AVE (28.2 μg/m3), NO2_AVE12 (30.1 μg/m3), NO2_AVE6 (34.2 μg/m3), NO2_MIN (16.9 μg/m3), NO2_MAX (39.5 μg/m3). Freq represents frequency that a variable had p-value ≤0.05 from 1,000 model replications.

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Fig 4.

Comparison of 1-day lag NO2 concentration effects in subgroups defined by age and hypertension condition.

AGECAT1 = age <65; AGECAT2 = age ≥65; HTN = Hypertension. NO-HTN = No Hypertension. OR estimates calculated by bootstrap model averaging of 1,000 replications for an inter-quintile range increase of NO2_AVE (28.2 μg/m3), NO2_AVE12 (30.1 μg/m3), NO2_AVE6 (34.2 μg/m3), NO2_MIN (16.9 μg/m3), NO2_MAX (39.5 μg/m3). Freq represents frequency that a variable had p-value ≤0.05 from 1,000 model replications.

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Fig 4 Expand