“… Intervention | Evidence of Reduced Exposure |
Face masks 1 study | PM 2.5 (−30% PM 2.5, −71% PM 10 ) Surgical mask during motorcycle commute vs. no mask Sulawesi, Indonesia ( Patel et al., 2016 ) |
Ventilation 2 studies | PM 2.5 (−38%); Black carbon (−68%) High-efficiency ventilation, public transit vs. autos Los Angeles, USA (Hong, 2019) |
PM 2.5 (−70%) Air filtration with natural ventilation, primary school classrooms China (Z. Tong, Li, Westerdahl and Freeman, 2020 ) |
Filters 3 studies | ∼5 DALYs avoided; cost: 10 USD In-duct carbon filters used in HVAC in heavy HVAC usage climates United States ( Aldred et al., 2016 ) |
NO 2 (−27%) HEPA or carbon filter air purifiers, HHs using unvented gas appliances Baltimore, USA ( Paulin et al., 2014 ) |
PM 2.5 (−40 μg/m 3 ) Indoor filters Beijing, China (W. Zhang, Li, Xu and Liu, 2018 ) |
Air quality alerts/indices 4 studies | Respiratory disease symptoms reported (−16.4%) Alert system, broadcasted to all users in area (auto-enroll) South Korea ( Hahm and Yoon, 2021 ) |
Hospital admissions for respiratory tract infections (−16%) and pneumonia (−12%) Air Quality Health Index alerts Hong Kong, China ( Mason et al., 2020 ; Mason et al., 2019 ) |
Significant reduction in cardiovascular disease–related mortality Stringent thresholds vs. relaxed thresholds used in air quality warnings Paris, France ( Alari et al., 2021 ) |
Traffic separation/transport mode 3 studies | PM 2.5 (4 × reduction); PM 10 (13x reduction) Car versus motorcycle commute Sulawesi, Indonesia ( Patel et al., 2016 ) |
Black carbon (−0.37 μg/m 3 ); carbon monoxide (−0.16 ppm) Bicycle commute, routes w/low auto traffic exposure Berkeley, USA ( Jarjour et al., 2013 ) |
Significant decrease in PM 2.5 exposure Children’s school commute by bus vs. walking Canada ( |
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