Liveability as determinant of health: Testing a new approach for health impact assessment of major infrastructure
Introduction
Like all species, humans are both a part, and a product of their ecology. For an ever-increasing proportion of society, the city has become the principle ecology (World Bank, 2017), and there is ample evidence that the quality of the built environment significantly affects health. The location and amount of public open space, opportunities for active transport, access to healthy food and other goods, opportunities for recreation, and proximity to centres of employment and education all show causal links to good health (Giles-Corti et al., 2016; Sallis et al., 2016).
Major infrastructures are the physical systems that provide services to the citizens of a state or nation. Infrastructure projects are usually provided by governments; funded through taxes, or by private-public partnerships. They include roads, rail, energy, water and broadband infrastructures. Investment in major infrastructure, particularly in the global south, can have diverse drivers, while the way public interests are treated is varied and complex (Mohan and Tan-Mullins, 2019; Searle and Legacy, 2020). All however, particularly those that are publicly funded, should contribute to equitable improvements in public health, commensurate with their scale (Nuffield Council of Biothics, 2007; Durrant, 2017). Arguably, government investment ‘upstream’ in health (Zola, 1970, cited in McKinlay, 2019) through improvements to the built environment is both an ethical responsibility and a prudent social investment. Investment in the determinants of health that make engaging in healthy behaviours the ‘easy option’ is generally more effective, equitable and yields more sustained benefits than does investing downstream in behaviour change (Watt, 2007).
This paper explores the feasibility of using an evidence-based social determinants of health (SDH) framework, Lowe et al., 2013, Lowe et al., 2015a liveability domains for health impact assessment (HIA) (Harris et al., 2007; EnHealth, 2017). The approach is tested by scoping the impacts of a major infrastructure project, the Upfield Level Crossing Removal (LXR) project in Melbourne, Australia, for later empirical examination. First, the paper introduces HIA protocols, Lowe's eleven liveability domains and the Upfield LXR case study. These are then brought together (Fig. 1), and the framework is tested by scoping the case study's impacts on determinants of health. The paper then describes a formal research program for testing the hypothesised impacts and thus validating the framework. The paper concludes with a discussion of the benefits of the framework for the wider HIA discipline.
The current paper therefore constitutes the first step towards testing Lowe et al., 2013, Lowe et al., 2015a eleven policy domains as a framework for comprehensive health impact assessments in the future, both in Australia and internationally. A forthcoming, comprehensive assessment of the case study will use the unique, liveability framework to ask, ‘Is LXR a prudent investment in public health?’
Section snippets
Health impact assessment
The understanding that health is socially determined has given rise to tools for evaluating proposed policies and projects using a ‘health lens’. Health Impact Assessment (HIA) is one of the predominant procedures and is embedded within other approaches such as Health in All Policies. Dannenberg et al., 2003, p.1506) state that an HIA is “an estimate of the effects of a specified action on the health of a defined population … to improve the quality of public policy decision-making from a health
A liveability framework for assessing determinants of health
In parallel to a growing understanding of the social determinants of health, liveability has arisen as an ideal for which cities should strive. Yet the definition of liveability is contested. The frequently-cited Economist Intelligence Unit's Liveability Index conceptualises international cities' liveability – including those in the global south – as a product of its good transport system, high proportions of public open space, low crime rates, and good educational opportunities (EIU, 2019).
Testing the liveability framework: The Upfield level crossing removal (LXR) project
In 2016, the state government of Victoria, Australia, as part of its ‘Big Build’ program (Victorian Government, 2020b), committed to removing 75 Melbourne metropolitan road/rail level crossings by 2025, “a faster rate of removal than in any other period of Melbourne's history” (Woodcock and Stone, 2016, p.13). Level crossing removal (LXR) involves either ‘undergrounding’ or elevating the railway to create ‘skyrail’. The two most frequently stated rationales for the Melbourne LXRs are to
The liveability domains applied to Upfield LXR
Drawing upon the literature, the following sections use the eleven liveability domains to scope Upfield LXR's impacts on health; short- and long-term, positive and negative. This provides a proof of concept for the liveability framework and a basis for a future detailed empirical examination of the impacts via data collection and analysis. This section is thus followed by proposed methods for gathering evidence in a future HIA assessment phase.
Framework for assessment phase of the HIA
Following on naturally from scoping, the liveability framework provides a useful structure for tackling the complex but essential empirical, i.e. assessment, phase of HIA. For Upfield LXR for example, examination of the eleven domains will involve four broad methods: literature reviews, primary research, secondary research and examination of comparable international case studies. For each domain, the literature review will establish the pathways and mechanisms that make each a determinant of
Discussion and conclusions
HIA aims to ensure consideration of the impacts of major infrastructure projects on health via social and other determinants. Despite this aim, to our knowledge no HIA has yet used an evidence-based and integrated liveability framework as a starting point for the scoping process, particularly not for a large built environment infrastructure project. As applied in this research, Lowe et al's., suite of liveability domains Lowe et al., 2013, Lowe et al., 2015b appears to be a collectively
Declaration of Competing Interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgments
Special thanks to Ms. Miranda Leckey who provided valuable advice during the preparation of this paper and to Dr. John Stone from Melbourne School of Design, The University of Melbourne, for support and advice. We also thank the four anonymous reviewers whose insightful comments contributed to substantial improvements in the manuscript.
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2022, Environmental Impact Assessment ReviewCitation Excerpt :Scholars assert that the ‘knowledge legitimacy’ of the community, and the ‘organisational (the LXRP's) legitimacy’, are equally important inputs to a quality impact assessment (Bond et al., 2018). Unique features of Upfield, that were important to the community, such as trees at Gandolfo Gardens and the serendipitous ‘green wave’ on the bike path (Pucher and Buehler, 2008; Browne and Lowe, 2021) could have been enhanced through genuine consultation that privileged local knowledge unavailable to the ‘expert’ outsider (Brown, 2009). Similarly, the disregard for community concern, particularly about the trees, caused much distress and sadness.
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2022, Environmental Impact Assessment ReviewCitation Excerpt :Theoretically aligning with the notion of ESHS, the ecological model of aging involving individual, familial, and environmental factors has been widely adopted as a backbone theory in the field of environmental gerontology to explain environmental influences on behaviors and public health of the aging population (Liu et al., 2017). This ecological model provides a theoretical foundation for exploring the relationships between the built environment factors and health outcomes among older adults (Browne and Lowe, 2021; Lawton, 1977; Liu et al., 2017; Moore et al., 2018). However, such a comprehensive theoretical model involving multidimensional levels has been barely supported by existing empirical studies.
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2022, Journal of Cleaner ProductionCitation Excerpt :For example, China's urban economy is continuously developing based on rapid urbanization, which makes infrastructures as a carrier bear more economic pressure (Sun et al., 2018). Insufficient economic carrying capacity of urban infrastructures has resulted in unemployment, the gap between the rich and the poor, difficulty in going to school and seeing a doctor, traffic congestion, water pollution, soil pollution, air pollution, low garbage disposal capacity, inadequate public service capacity, surge of public security incidents, poor living environment and other problems (Browne and Lowe, 2021; T. Liu et al., 2020a; Z. Liu et al., 2020b; Wei et al., 2015a). This reduces the attractiveness of cities and affects foreign investment, which has a negative impact on the sustainable development of the economy.
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