Related Experiment Video
Updated: Sep 8, 2026

Alternative Therapy for Acute Exacerbation of Chronic Obstructive Pulmonary Disease: Moving Cupping Along Meridians
Published on: September 27, 2024
Seasonal Patterns and Short-Term Environmental Associations with AECOPD Hospitalizations in Shijiazhuang, China,
Siqin Han1, Zaixing Jia1, Jialun Chen1
1The First Department of Pulmonary and Critical Care Medicine, The Second Hospital of Hebei Medical University, Hebei Key Laboratory of Respiratory Critical Care Medicine, Hebei Institute of Respiratory Diseases, Shijiazhuang Hebei, China.
Objective:
To examine the seasonal distribution of AECOPD hospitalizations in Shijiazhuang (2020-2024), the lag associations of air pollutants (PM2.5, PM10, NO2, O3, SO2, CO) and meteorological factors (mean temperature, diurnal temperature range) across seasons, and to explore the season-specific models for high-incidence admission days as an exploratory environmental-surveillance analysis rather than a ready-to-deploy clinical early-warning system.
Methods:
This city-wide retrospective time-series study analyzed 22,468 AECOPD admissions in Shijiazhuang from January 1, 2020 to December 31, 2024, using hospitalization front-page records covering all tertiary, secondary, and community hospitals in the city, obtained from the municipal medical insurance database (inpatient admissions only; ED discharges without admission were not included). Each year was divided by solar terms into spring (3/7-6/7), summer (6/8-9/7), autumn (9/8-12/7), and winter (12/8-3/6), with daily air pollution and meteorological data matched to admissions. Univariate and multivariate Poisson generalized linear regression (GLM) assessed single-day lag associations (lags 0-7 as eight separate lags); multivariable models and prediction features used the 7-day mean of lags 0-6 (admission day + preceding 6 days), not an 8-day lag0-7 average. Using each factor's 7-day cumulative window as input, we built logistic regression, random forest, and gradient boosting models and evaluated high-incidence-day prediction via fivefold time-series cross-validation, treating the many lag × pollutant × season tests as exploratory. Sensitivity analyses added during revision included collinearity diagnostics (VIF/correlation matrix), quasi-Poisson models with smooth time, a distributed-lag nonlinear temperature model (DLNM), COVID-period analyses, humidity/heating checks, alternative lag windows, and a near-term exposure prediction re-run.
Results:
AECOPD admissions peaked in winter and were the lowest in summer (winter 6,009; spring 5,854; autumn 5,554; summer 5,051); the male-to-female ratio was ∼3.7:1 and mean age 71.7 ± 9.1 years. After multivariate adjustment, each 10 µg/m³ rise in winter PM10 and NO2 was associated with a 6.9% (IRR 1.069, 95%CI 1.052-1.085) and 8.9% (1.089, 1.050-1.129) higher admission rate, respectively. A 1 °C fall in mean temperature corresponded to a 4.4% increase (IRR 0.958, 0.947-0.969) and a 1 °C wider diurnal range to a 5.5% increase (1.055, 1.034-1.077). O3 was positively associated in summer and autumn (1.035, 1.015-1.056; 1.022, 1.005-1.039). Apparent protective multipollutant IRRs (e.g., winter PM2.5) were interpreted cautiously given collinearity. Prediction discrimination was the modest even when above chance: winter random forest fivefold CV AUC of 0.653 ± 0.112; other seasons ranged 0.50-0.62. Overall, environmental exposures were weak predictors of high-incidence days. Diagnostic re-analyses (Section 3.4), after reconciling the panel to the locked 22,468-admission cohort, showed acceptable collinearity (all VIF < 5, addressed with single-pollutant models), overdispersion handled by quasi-Poisson, and nonlinear temperature effects by DLNM (cold-induced excess, heat-related reduction), alongside a 2022 admission trough (∼50-54% of 2020/2024) and a near-term exposure re-run (same-day and lags 1-3 features) that reproduced the modest winter discrimination (AUC ≈0.66); against a calendar-only baseline the incremental value of the environmental block was small (overall ΔAUC ≈ +0.02 to +0.045), indicating the exposures are primarily explanatory rather than operationally predictive.
Conclusion:
AECOPD admissions show high winter incidence, with PM10, NO2, CO, low temperature, and a wide diurnal range as the main winter associated factors, and summer-autumn O3 exposure warranting attention. The 7-day cumulative-exposure model showed only the modest discrimination in winter (AUC ≈0.65) and is best viewed as an exploratory, hypothesis-generating surveillance analysis rather than a preliminary operational early-warning tool.