Adverse health effects associated with household air pollution: a systematic review, meta-analysis, and burden estimation study.
Journal
The Lancet. Global health
ISSN: 2214-109X
Titre abrégé: Lancet Glob Health
Pays: England
ID NLM: 101613665
Informations de publication
Date de publication:
11 2020
11 2020
Historique:
received:
19
02
2020
revised:
17
06
2020
accepted:
13
07
2020
entrez:
18
10
2020
pubmed:
19
10
2020
medline:
28
10
2020
Statut:
ppublish
Résumé
3 billion people worldwide rely on polluting fuels and technologies for domestic cooking and heating. We estimate the global, regional, and national health burden associated with exposure to household air pollution. For the systematic review and meta-analysis, we systematically searched four databases for studies published from database inception to April 2, 2020, that evaluated the risk of adverse cardiorespiratory, paediatric, and maternal outcomes from exposure to household air pollution, compared with no exposure. We used a random-effects model to calculate disease-specific relative risk (RR) meta-estimates. Household air pollution exposure was defined as use of polluting fuels (coal, wood, charcoal, agricultural wastes, animal dung, or kerosene) for household cooking or heating. Temporal trends in mortality and disease burden associated with household air pollution, as measured by disability-adjusted life-years (DALYs), were estimated from 2000 to 2017 using exposure prevalence data from 183 of 193 UN member states. 95% CIs were estimated by propagating uncertainty from the RR meta-estimates, prevalence of household air pollution exposure, and disease-specific mortality and burden estimates using a simulation-based approach. This study is registered with PROSPERO, CRD42019125060. 476 studies (15·5 million participants) from 123 nations (99 [80%] of which were classified as low-income and middle-income) met the inclusion criteria. Household air pollution was positively associated with asthma (RR 1·23, 95% CI 1·11-1·36), acute respiratory infection in both adults (1·53, 1·22-1·93) and children (1·39, 1·29-1·49), chronic obstructive pulmonary disease (1·70, 1·47-1·97), lung cancer (1·69, 1·44-1·98), and tuberculosis (1·26, 1·08-1·48); cerebrovascular disease (1·09, 1·04-1·14) and ischaemic heart disease (1·10, 1·09-1·11); and low birthweight (1·36, 1·19-1·55) and stillbirth (1·22, 1·06-1·41); as well as with under-5 (1·25, 1·18-1·33), respiratory (1·19, 1·18-1·20), and cardiovascular (1·07, 1·04-1·11) mortality. Household air pollution was associated with 1·8 million (95% CI 1·1-2·7) deaths and 60·9 million (34·6-93·3) DALYs in 2017, with the burden overwhelmingly experienced in low-income and middle-income countries (LMICs; 60·8 million [34·6-92·9] DALYs) compared with high-income countries (0·09 million [0·01-0·40] DALYs). From 2000, mortality associated with household air pollution had reduced by 36% (95% CI 29-43) and disease burden by 30% (25-36), with the greatest reductions observed in higher-income nations. The burden of cardiorespiratory, paediatric, and maternal diseases associated with household air pollution has declined worldwide but remains high in the world's poorest regions. Urgent integrated health and energy strategies are needed to reduce the adverse health impact of household air pollution, especially in LMICs. British Heart Foundation, Wellcome Trust.
Sections du résumé
BACKGROUND
3 billion people worldwide rely on polluting fuels and technologies for domestic cooking and heating. We estimate the global, regional, and national health burden associated with exposure to household air pollution.
METHODS
For the systematic review and meta-analysis, we systematically searched four databases for studies published from database inception to April 2, 2020, that evaluated the risk of adverse cardiorespiratory, paediatric, and maternal outcomes from exposure to household air pollution, compared with no exposure. We used a random-effects model to calculate disease-specific relative risk (RR) meta-estimates. Household air pollution exposure was defined as use of polluting fuels (coal, wood, charcoal, agricultural wastes, animal dung, or kerosene) for household cooking or heating. Temporal trends in mortality and disease burden associated with household air pollution, as measured by disability-adjusted life-years (DALYs), were estimated from 2000 to 2017 using exposure prevalence data from 183 of 193 UN member states. 95% CIs were estimated by propagating uncertainty from the RR meta-estimates, prevalence of household air pollution exposure, and disease-specific mortality and burden estimates using a simulation-based approach. This study is registered with PROSPERO, CRD42019125060.
FINDINGS
476 studies (15·5 million participants) from 123 nations (99 [80%] of which were classified as low-income and middle-income) met the inclusion criteria. Household air pollution was positively associated with asthma (RR 1·23, 95% CI 1·11-1·36), acute respiratory infection in both adults (1·53, 1·22-1·93) and children (1·39, 1·29-1·49), chronic obstructive pulmonary disease (1·70, 1·47-1·97), lung cancer (1·69, 1·44-1·98), and tuberculosis (1·26, 1·08-1·48); cerebrovascular disease (1·09, 1·04-1·14) and ischaemic heart disease (1·10, 1·09-1·11); and low birthweight (1·36, 1·19-1·55) and stillbirth (1·22, 1·06-1·41); as well as with under-5 (1·25, 1·18-1·33), respiratory (1·19, 1·18-1·20), and cardiovascular (1·07, 1·04-1·11) mortality. Household air pollution was associated with 1·8 million (95% CI 1·1-2·7) deaths and 60·9 million (34·6-93·3) DALYs in 2017, with the burden overwhelmingly experienced in low-income and middle-income countries (LMICs; 60·8 million [34·6-92·9] DALYs) compared with high-income countries (0·09 million [0·01-0·40] DALYs). From 2000, mortality associated with household air pollution had reduced by 36% (95% CI 29-43) and disease burden by 30% (25-36), with the greatest reductions observed in higher-income nations.
INTERPRETATION
The burden of cardiorespiratory, paediatric, and maternal diseases associated with household air pollution has declined worldwide but remains high in the world's poorest regions. Urgent integrated health and energy strategies are needed to reduce the adverse health impact of household air pollution, especially in LMICs.
FUNDING
British Heart Foundation, Wellcome Trust.
Identifiants
pubmed: 33069303
pii: S2214-109X(20)30343-0
doi: 10.1016/S2214-109X(20)30343-0
pmc: PMC7564377
pii:
doi:
Types de publication
Journal Article
Meta-Analysis
Research Support, Non-U.S. Gov't
Systematic Review
Langues
eng
Sous-ensembles de citation
IM
Pagination
e1427-e1434Subventions
Organisme : British Heart Foundation
ID : PG/19/40/34422
Pays : United Kingdom
Organisme : British Heart Foundation
ID : FS/16/14/32023
Pays : United Kingdom
Organisme : British Heart Foundation
ID : FS/19/17/34172
Pays : United Kingdom
Organisme : Wellcome Trust
ID : WT103782AIA
Pays : United Kingdom
Organisme : Wellcome Trust
ID : 201492/Z/16/Z
Pays : United Kingdom
Organisme : British Heart Foundation
ID : SP/15/8/31575
Pays : United Kingdom
Organisme : World Health Organization
ID : 001
Pays : International
Organisme : British Heart Foundation
ID : FS/18/25/33454
Pays : United Kingdom
Organisme : British Heart Foundation
ID : CH/09/002
Pays : United Kingdom
Organisme : British Heart Foundation
ID : CH/09/002/26360
Pays : United Kingdom
Organisme : British Heart Foundation
ID : RE/18/5/34216
Pays : United Kingdom
Informations de copyright
Copyright © 2020 The Author(s). Published by Elsevier Ltd. This is an Open Access article under the CC BY 4.0 license. Published by Elsevier Ltd.. All rights reserved.
Références
BMJ. 2015 Mar 24;350:h1295
pubmed: 25810496
Annu Rev Public Health. 2014;35:185-206
pubmed: 24641558
Pediatrics. 2002 Aug;110(2 Pt 1):285-91
pubmed: 12165580
Environ Health. 2013 Sep 11;12(1):77
pubmed: 24020494
Circulation. 2018 Sep 11;138(11):1100-1112
pubmed: 29967196
Ecohealth. 2015 Mar;12(1):42-56
pubmed: 25724593
J Perinatol. 2011 Apr;31 Suppl 1:S49-56
pubmed: 21448204
Pediatrics. 2010 Sep;126(3):443-56
pubmed: 20732945
Environ Health Perspect. 2013 Jul;121(7):784-90
pubmed: 23674502
Lancet. 2007 Sep 15;370(9591):965-78
pubmed: 17876909
Environ Health Perspect. 2014 Apr;122(4):397-403
pubmed: 24518036
Lancet. 2018 Nov 10;392(10159):1923-1994
pubmed: 30496105
Nat Clin Pract Cardiovasc Med. 2009 Jan;6(1):36-44
pubmed: 19029991
PLoS One. 2019 May 16;14(5):e0216550
pubmed: 31095592
Lancet. 2017 Sep 16;390(10100):1345-1422
pubmed: 28919119
Epidemiol Rev. 2010;32:70-81
pubmed: 20378629
PLoS Med. 2009 Jul 21;6(7):e1000097
pubmed: 19621072
Environ Int. 2018 Nov;120:354-363
pubmed: 30119008
Lancet. 2017 Jan 14;389(10065):167-175
pubmed: 27939058
Lancet. 2011 Nov 12;378(9804):1717-26
pubmed: 22078686
Circulation. 2016 Jun 14;133(24):2360-9
pubmed: 27297340
Int J Environ Res Public Health. 2010 Aug;7(8):3270-97
pubmed: 20948960
Int J Epidemiol. 2013 Dec;42(6):1724-37
pubmed: 23962958
Am J Obstet Gynecol. 2007 Feb;196(2):147.e1-8
pubmed: 17306659
Trop Med Int Health. 2010 May;15(5):508-19
pubmed: 20345556
PLoS One. 2016 Mar 16;11(3):e0149669
pubmed: 26982804
Data Brief. 2018 Oct 27;21:1292-1295
pubmed: 30456246
Trop Med Int Health. 2013 Jan;18(1):101-8
pubmed: 23130953
Proc Natl Acad Sci U S A. 2018 Dec 4;115(49):12401-12406
pubmed: 30455309
Energy Sustain Dev. 2018 Oct;46:71-81
pubmed: 30333687