| Literature DB >> 35346202 |
Wenfeng Lu1,2, Qi Tian3, Ruijun Xu4, Chenghui Zhong2, Lan Qiu2, Han Zhang2, Chunxiang Shi5, Yuewei Liu6, Yun Zhou7,8.
Abstract
BACKGROUND: Pneumonia is a major contributor to hospital admission for patients with chronic obstructive pulmonary disease (COPD). However, evidence for acute effects of ambient air pollution exposure on pneumonia hospital admission among patients with COPD is scarce. We aimed to examine the association between short-term exposure to ambient air pollution and pneumonia hospital admission among patients with COPD.Entities:
Keywords: Air pollution; COPD patients; Hospital admission; Pneumonia
Mesh:
Substances:
Year: 2022 PMID: 35346202 PMCID: PMC8962484 DOI: 10.1186/s12931-022-01989-9
Source DB: PubMed Journal: Respir Res ISSN: 1465-9921
Baseline characteristics of study population in Guangdong province, China during 2016–2019
| Baseline Characteristic | Values |
|---|---|
| Pneumonia hospital admissions, n (ICD-10 code: J12-J18) | 6473 |
| Case days, n | 9431 |
| Control days, n | 31,914 |
| Sex, n (%) | |
| Male | 6438 (68.3) |
| Female | 2993 (31.7) |
| Age at hospital admission | |
| Mean (SD) | 79.1 (8.6) |
| Median (IQR) | 80.0 (12.0) |
| n (%) | |
| < 85 year | 6682 (70.9) |
| ≥ 85 year | 2749 (29.1) |
| Season at hospital admission, n (%) a | |
| Warm | 4246 (45.0) |
| Cool | 5185 (55.0) |
| No. of hospital admission, n | |
| 1 | 4836 (74.7) |
| 2 | 1021 (15.8) |
| ≥ 3 | 616 (9.5) |
| Main type of pneumonia, n (%) | |
| Bacterial pneumonia (ICD-10 code: J15) | 3260 (34.6) |
| Pneumonia, organism unspecified (ICD-10 code: J18) | 6152 (65.4) |
ICD International Classification of Diseases, SD standard deviation, IQR interquartile range
aWarm season: from May to October; Cool season: November to December, January to April
Distribution of air pollutants and meteorological conditions on case days in Guangdong, China during 2016–2019
| Variable | Mean | SD | P5 | P25 | Median | P75 | P95 | IQR |
|---|---|---|---|---|---|---|---|---|
| Air pollutant | ||||||||
| PM2.5, μg/m3 | 32.1 | 17.9 | 11.5 | 19.2 | 28.0 | 40.9 | 65.2 | 21.7 |
| PM10, μg/m3 | 53.8 | 27.3 | 21.5 | 34.1 | 46.9 | 68.0 | 108.1 | 33.9 |
| SO2, μg/m3 | 8.2 | 3.7 | 4.1 | 5.4 | 7.3 | 9.9 | 15.2 | 4.5 |
| NO2, μg/m3 | 46.5 | 21.0 | 19.4 | 32.7 | 42.4 | 55.9 | 86.4 | 23.2 |
| CO, mg/m3 | 0.85 | 0.23 | 0.55 | 0.70 | 0.80 | 0.95 | 1.27 | 0.26 |
| O3, μg/m3 | 94.9 | 50.5 | 20.7 | 58.4 | 89.0 | 125.8 | 190.3 | 67.4 |
| Meteorological condition | ||||||||
| Temperature, °C | 23.8 | 5.4 | 14.4 | 19.8 | 24.3 | 28.3 | 31.2 | 8.5 |
| Relative humidity, % | 76.6 | 13.2 | 50.1 | 69.4 | 80.3 | 86.7 | 91.8 | 17.2 |
SD standardized deviation, P the 5th percentile, P the 25th percentile, P the 75th percentile, P the 95th percentile, IQR interquartile range, PM particulate matter with an aerodynamic diameter ≤ 2.5 µm, PM particulate matter with an aerodynamic diameter ≤ 10 µm, SO sulfur dioxide, NO nitrogen dioxide, CO carbon monoxide, O ozone
Spearman’s correlation coefficients between air pollutants and meteorological conditions on case daysa
| PM2.5 | PM10 | SO2 | NO2 | CO | O3 | Temperature | |
|---|---|---|---|---|---|---|---|
| PM10 | 0.96 | – | – | – | – | – | – |
| SO2 | 0.60 | 0.63 | – | – | – | – | – |
| NO2 | 0.67 | 0.69 | 0.43 | – | - | - | - |
| CO | 0.55 | 0.50 | 0.26 | 0.60 | – | – | – |
| O3 | 0.34 | 0.39 | 0.36 | 0.07 | − 0.15 | – | – |
| Temperature | − 0.28 | − 0.21 | − 0.03 | − 0.27 | − 0.43 | 0.46 | – |
| Relative humidity | − 0.50 | − 0.52 | − 0.53 | − 0.16 | − 0.15 | − 0.43 | 0.26 |
PM particulate matter with an aerodynamic diameter ≤ 2.5 µm, PM particulate matter with an aerodynamic diameter ≤ 10 µm, SO sulfur dioxide, NO nitrogen dioxide, CO carbon monoxide, O ozone
aAll pairwise correlation coefficients were statistically significant (p < 0.001)
Fig. 1Adjusted ORs (95% CIs) for pneumonia hospital admission among COPD patients with air pollutants exposure. ORs for PM2.5, PM10, SO2, NO2, CO, and O3 at different lag periods were estimated using conditional logistic regression models, adjusting for temperature, relative humidity and number of admission records. OR odds ratio, CI confidence interval, COPD chronic obstructive pulmonary disease, PM particulate matter with an aerodynamic diameter ≤ 2.5 µm, PM particulate matter with an aerodynamic diameter ≤ 10 µm, SO sulfur dioxide, NO nitrogen dioxide, CO carbon monoxide, O ozone
Fig. 2Exposure–response curves between air pollutant exposures and pneumonia hospital admission among COPD patients. Adjusted ORs (95% CIs) for PM2.5 (lag 2), PM10 (lag 2), SO2 (lag 03), NO2 (lag 03), CO (lag 2), and O3 (lag 04) were estimated for continuous exposures excluding those less and greater than 1% by using conditional logistic regression models, adjusting for temperature, relative humidity, and number of hospital admission. OR odds ratio, CI confidence interval, COPD chronic obstructive pulmonary disease, PM particulate matter with an aerodynamic diameter ≤ 2.5 µm, PM particulate matter with an aerodynamic diameter ≤ 10 µm, SO sulfur dioxide, NO nitrogen dioxide, CO carbon monoxide, O ozone