Department of Epidemiology and Biostatistics, Faculty of Health Sciences in Bytom, Medical University of Silesia, 40-055 Katowice, Poland.
Department of Epidemiology, Faculty of Medical Sciences in Katowice, Medical University of Silesia, 40-055 Katowice, Poland.
Int J Environ Res Public Health. 2020 May 20;17(10):3591. doi: 10.3390/ijerph17103591.
The main aim of this work is the estimation of health risks arising from exposure to ozone or other air pollutants by different statistical models taking into account delayed health effects. This paper presents the risk of hospitalization due to bronchitis and asthma exacerbation in adult inhabitants of Silesian Voivodeship from 1 January 2016 to 31 August 2017. Data were obtained from the daily register of hospitalizations for acute bronchitis (code J20-J21, International Classification of Diseases, Tenth Revision - ICD-10) and asthma (J45-J46) which is governed by the National Health Fund. Meteorological data and data on tropospheric ozone concentrations were obtained from the regional environmental monitoring database of the Provincial Inspector of Environmental Protection in Katowice. The paper includes descriptive and analytical statistical methods used in the estimation of health risk with a delayed effect: Almon Distributed Lag Model, the Poisson Distributed Lag Model, and Distributed Lag Non-Linear Model (DLNM). A significant relationship has only been confirmed by DLNM for bronchitis and a relatively short period (1-3 days) from exposure above the limit value (120 µg/m). The relative risk value was RR = 1.15 (95% CI 1.03-1.28) for a 2-day lag. However, conclusive findings require the continuation of the study over longer observation periods.
这项工作的主要目的是通过不同的统计模型,考虑到滞后的健康影响,来评估暴露于臭氧或其他空气污染物所带来的健康风险。本文介绍了 2016 年 1 月 1 日至 2017 年 8 月 31 日期间,西里西亚省成年居民因支气管炎和哮喘恶化而住院的风险。数据来自急性支气管炎(J20-J21,国际疾病分类,第十版 - ICD-10)和哮喘(J45-J46)的每日住院登记,这些疾病由国家卫生基金管理。气象数据和对流层臭氧浓度数据来自卡托维兹省级环境保护监察局的区域环境监测数据库。本文包括用于估算具有滞后效应的健康风险的描述性和分析性统计方法:阿尔蒙分布式滞后模型、泊松分布式滞后模型和分布式滞后非线性模型(DLNM)。仅通过 DLNM 为支气管炎和相对较短的暴露期(1-3 天)确认了与超过限值(120μg/m)相关的显著关系。滞后 2 天时,相对风险值为 RR=1.15(95%置信区间为 1.03-1.28)。然而,得出明确的结论需要在更长的观察期内继续进行研究。