Abstract
Between 1348 and 1700, the states of Northern and Central Italy were among the earliest to establish health magistracies in major cities—Venice, Florence and Milan—to coordinate responses to recurring epidemics of bubonic plague. In the fifteenth century, these magistracies had become permanent and had turned their attention to the creation, oversight and maintenance of what we now might call a public health infrastructure (Public Health Infrastructure Resource Centre 2009); the quality of food and medicines, the movement of beggars and prostitutes, activities of doctors and hospitals, sanitary conditions in the poorest neighbourhoods, the quarantining of ships and the keeping of registers of mortality among many others (Cipolla 1992). One of the great achievements of British sanitary reform in the nineteenth century was to extend this tradition of governance of public health to include the built environment. Initially these reforms were focussed on a narrow set of hazards in rapidly expanding cities; local authorities were vested with responsibility for building standards and town planning, the control of noxious trades, water supply, sewage disposal, the management of burials and mortuaries and vermin control. Since then the public health infrastructure has evolved and expanded—shaped by population growth, technological innovation, community expectations, environmental and resource constraints and importantly the national and international experience of regulatory and system failure, and disaster. What have not kept pace with this expansion are the adaptations to the built environment necessary to address contemporary health concerns, particularly the prevention of chronic disease (Corbett 2008). In part, this may be due to the dispersion across government of custody of this infrastructure; public health professionals have less involvement in day-to-day risk management than environmental scientists, traffic engineers, building safety experts and professional urban planners (Perdue et al. 2003). Dams, pipes, sewers, road surfacing and energy infrastructure represent only a part of the vast fixed investment for public health in the built environment. Of greater importance is the institutional capacity to effectively regulate hazards to health and to anticipate and avert system failure; public health laws which are aligned with contemporary public health problems; a workforce skilled and empowered to work across bureaucratic and professional boundaries, and an information infrastructure capable of continuous monitoring of hazards and health and regulatory effectiveness. There is a strong justification for continued regulation of the built environment for public health (Perdue et al. 2003), and for a more explicit role for public health agencies and professionals in defining or redefining public health objectives so that they are both mindful of the need to maintain and improve what we have but are better aligned with the major causes of ill health and disability in the community (Corbett 2005). For example, there is an urgent need for urban planners to be empowered to consider a much broader range of Stephen Corbett is a Public-Health physician and Director of the Centre for Population Health Sydney, West Area Health Service, and Associate Professor at the University of Sydney, School of Population Health and Western Clinical School.
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