Location | Methodology/ Tool | Exposure | Outcome | Related Policy | Main opportunities | Main barriers | Author |
---|---|---|---|---|---|---|---|
Barcelona | Blue Active Tool | Physical activity | Mortality, morbidity, DALYs, health economic values | Riverside regeneration | First impact assessment on this topic in this city | Data quality & availability No stakeholder participation | Vert et al, 2019 [15] |
Barcelona | UTOPHIA | Transport-PA Air pollution (PM2.5) Noise (Lday 16h) Green space (%GS) Heat (daily mean Temperature) | Mortality | Local urban and transport planning policies | Holisitic approach in estimating the mortality burden associated with the multiple urban and transport planning related exposures Detailed exposure data on same spatial scale Quantification of expected impact, direction and magnitude of expected health effects | Uncertainty in causal inferences Mortality is ‘tip of the iceberg’, morbidity was not considered ‘Double-counting’ of cases (correlation of exposures) Risk of exposure and outcome misclassification Quantitative HIA cannot capture intrinsic motivations for behaviour change | Mueller et al 2017a [38] |
Barcelona | UTOPHIA | Transport-PA Air pollution (PM2.5) Noise (Lday 16h) Green space (%GS) Heat (daily mean Temperature) | Morbidity DALYs | Local urban and transport planning policies | Holistic approach in estimating the mortality burden associated with multiple exposures Detailed exposure data on same spatial scale Quantification of expected impact, direction and magnitude of expected health effects | Uncertainty in causal inferences DALY estimations & scaling from national to local level uncertainty Risk of exposure and outcome misclassification | Mueller et al. 2017b [39] |
Port Louis | Health Risk Assessment | Physical activity, travel mode, heat, air pollution | Mortality | Light Metro Express Rail | Smaller city: faster process, primary data collection feasible, less costly Collaboration of all relevant ministries and sectors Easily replicable model Scalability if time and financial resources exist | Data quality & availability, gap between policy concerns and citizens needs Lack of interest by local media | Thondoo et al. Unpublished |
Argentina: Rosario; Bolivia: El Alto; Brazil: Sao Paulo; Chile: Santiago de Chile; Colombia: Bogota, Cali and Medellin; Ecuador: Cuenca and Quito; Guatemala: Guatemala City; Mexico: Guadalajara, Mexico City and Puebla; Panama: Panama City; Peru: Lima | Blue Active Tool | Physical activity | Mortality, morbidity, DALYs, and mortality related economic values | Open streets | First multinational impact assessment on Open Streets Near collaboration with stakeholders Using the results for advocacy | Data availability and quality Lack of harmonize data between countries and cities Lack of collaboration between health sector and urban /transport planning | Velazquez-Cortez D, et al, unpublished |
Mexico City Bogota Istanbul Brisbane Paris | TAPAS tool | Physical activity, air pollution, traffic incidents | Mortality and mortality related economic values | Bus Rapid Transit | First impact assessment Policy popularity | Data availability and quality Lack of harmonized data between countries and cities Lack of collaboration between health sector and urban /transport planning | Rojas-Rueda D et al, unpublished |
Barcelona | TAPAS tool | Physical activity, air pollution, traffic incidents | Mortality and mortality related economic values | Tram expansion | Stakeholder collaboration Use analysis data to decision making process and political debate | Data quality & availability Lack of interest from different political parties at city council | Rojas-Rueda D et al, [40] |
Barcelona | TAPAS tool | Physical activity, air pollution, traffic incidents | Mortality | Bike sharing systems | First assessment Results helped to strength collaboration between local stakeholders and researchers | Data quality & availability No stakeholder participation | Rojas-Rueda D et al, 2011 [37] |
Barcelona | TAPAS tool | Physical activity, air pollution, traffic incidents | Mortality | Active transportation (walking and cycling) and public transport scenarios | First assessment Results helped to strength collaboration between local stakeholders and researchers | Data quality & availability No stakeholder participation | Rojas-Rueda D et al, 2012 [41] |
Barcelona | TAPAS tool | Physical activity, air pollution, traffic incidents | Mortality, morbidity and DALYs | Active transportation (walking and cycling) and public transport scenarios | Provide in deep analysis of transport related impact at local level Results helped stakeholders to understand transport and health pathways | Data quality & availability No stakeholder participation | Rojas-Rueda D et al, 2013 [42] |
Barcelona Brussels Hamburg Lille Lyon Madrid Milan Paris Seville Toulouse Valencia Warsaw | TAPAS tool | Physical activity, air pollution, traffic incidents | Mortality | Bike sharing systems | First multinational assessment Results helped to strength regional advocacy on bike sharing systems | Data quality & availability Lack of harmonized data between countries and cities No stakeholder participation | Otero I et al, 2018 [43] |
Barcelona Basel Copenhagen Paris Prague Warsaw | TAPAS tool | Physical activity, air pollution, traffic incidents | Mortality | Walking and cycling | Policy comparative between multiple cities and countries, helping to understand the implications of similar polices in different context and locations. | Data quality & availability Lack of harmonized data between countries and cities No stakeholder participation | Rojas-Rueda D et al, 2016 [44] |
Morocco | Quantitative Health Impact Assessment | Air pollution, water and sanitation | Mortality | SDGs 3, 6 and 11 implementation | SDG context & stakeholder support | Data quality & availability | Rojas-Rueda D et al, 2018 [45] |
Maputo Cochabamba | Evaluating feasibility, pilot study | NA | NA | NA | Fast urban growing of the cities and low development; Possibilities for policy and intervention assessment; Intersectorial approaches; Establishment of new communication pathways between local authorities. | Low regulations; Low continuity in the policies; Low cooperation between stakeholders and poor long-term engagement; Low understanding of HIA Research Low capacity to collect routinely data; Low comparability between data collected. | Gascon et al. 2016 [46] |
Antwerp Barcelona London Örebro Rome Zurich | Health impact assessment of cycling network expansions in European cities | Transport mode physical activity air pollution (PM2.5) fatal traffic accidents | Mortality | Cycling infrastructure policies | First study evaluating the potential associations between cycling network length, mode share and associated health impacts across European cities Standardized data extraction methods | Detailed data availability Cross-sectional study, no causality can be implied Detailed data availability, assumptions on causal inferences Impacts estimated only for active travelers, societal benefits ignored | Mueller et al, 2018 [48] |
Bradford | UTHOPIA | Transport mode physical activity air pollution (PM2.5) noise (Lden) green space (%GS) Index Multiple Deprivation Ethnicity | Mortality | Local urban and transport planning policies | Holisitic approach in estimating the mortality burden associated with the multiple urban and transport planning related exposures Distribution of mortality burden by SES variables | Assumptions on causal inferences were evidence is lacking Risk of exposure and outcome misclassification Different strengths of evidence for exposures with mortality Quantitative HIA cannot captures intrinsic motivations for behavior change | Mueller et al, 2018 [49] |
Barcelona | Transport-related physical activity (PA), (air pollution (NO2), road traffic noise, green space, urban heat island (UHI) effect | Premature mortality, changes in life expectancy and economic impacts | Local planning (Superblock model) | Robust overall estimation, based on best epidemiological evidence according to the current research. Multiple urban and transport planning related exposures were considered holistically and where uncertainty on causal inferences existed, assumptions were defined with caution and impacts were estimated conservatively. Research conducted by academia in consortium with public health and urban ecology local agencies | Non-fatal impacts such as the expected reduction in chronic disease, improvements in quality of life, social cohesion and mental health have not been quantified. Simultaneous improvement of the suburban commuter network is needed. Gentrification is a possible risk. Undesired relocation of car/motorcycle traffic (to potentially already deprived areas) outside the Superblocks needs to be considered and avoided | Muller et al, 2019 [47] |