GEOG 352 – ENVIRONMENTAL GEOGRAPHY

 

 

Essay Assignment:

 

 

Discuss the claim that a compact city form will contribute to urban sustainability.

 

 

 

 

 

 

Joshua Arbury – 2522603

 

 

Lab Time: Wednesday 10-11am

 

 

 

 

 

 

 

 

 

 

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In recent years city planners, developers and policymakers have increasingly looked towards designing a more ‘compact city’ in order to achieve a more sustainable urban form. There are many perceived benefits of the compact city over ‘urban sprawl’, which include: less car dependency thus lower emissions, reduced energy consumption, better public transport services, increased overall accessibility, the re-use of infrastructure and previously developed land, a rejuvenation of existing urban areas and urban vitality, a higher quality of life, the preservation of green space, and the creation of a milieu for enhanced business and trading activities. (Thomas and Cousins, 1996) As ‘sustainable development’ relies upon the combination of economic, social and environmental elements, it is important for the compact city to show improvements across all three spheres and for most, if not all of the perceived benefits listed above to become a reality. Unfortunately for proponents of the compact city model, in-depth research has shown that simply employing policies to stimulate compact city style development will not necessarily lead to sustainability of the urban environment. In this essay, I will argue that the compact city model is necessary, but not sufficient for sustainability, and that “some aspects of intensification, in some places, have contributed to sustainability, whilst others have clearly not,” (Williams, 2000: 44).

 

            The concern with sustainable development, or sustainability, has grown enormously in the last 15 years. Following the publication of the World Commission on Environment and Development’s (WCED) Our Common Future in 1987, which introduced the idea of sustainable development, there has been a focus around the world to pursue policies seen as ‘sustainable’. Defined by the WCED, sustainable development is: development designed “to ensure that it meets the needs of the present without compromising the ability of future generations to meet their own needs.” (WCED, 1987: 8). It is clear that many, if not all cities throughout the world are functioning in highly unsustainable ways at present. It has been estimated that London requires 50 million acres of land to sustain its population – the food and timber requirements as well as the vegetation necessary to absorb carbon dioxide emissions. This area is roughly 125 times the actual surface, a vivid example of how unsustainable a city can be. (Williams et. al., 2000) Unrestrained economic development throughout the ‘developed world’ has led to unsustainable levels of resource use, and increasingly inequitable lifestyles. The effects of this unsustainable lifestyle are felt not only in the developed world, but are exported to developing countries due to the unfair share of resources used by developed nations. This has led to a growing gap between rich and poor nations, resulting in increasingly unsustainable development. As Williams et. al. (2000: 2) conclude, “it is clear that cities in developed countries are not functioning in a sustainable way. They are using more than their fair share of resources and producing too much pollution.”

 

            The ‘solution’ to the unsustainable nature of cities throughout the world has been frequently referred to as making these cities more ‘compact’, to make better use of the resources currently available. Many planners and policymakers believe that “sustainable communities are places that exhibit a compact urban form.” (Beatley, 1995: 384) However, there is debate about the very definition of a ‘compact city’, and in particular what policies need to be undertaken to achieve urban compaction, let alone whether these particular policies in fact do contribute to sustainability. According to Breheny (2001: 39) “policies of urban compaction involve the promotion of urban regeneration, the revitalisation of town centers, restraint on development in rural areas, higher densities, mixed-use development, promotion of public transport and the concentration of urban development at public transport nodes.” Researchers such as Gordon and Richardson (1997) have renounced many of these policies as being uneconomic, and against the wishes of the general population who have characterized the twentieth century by a rejection of inner city living, and the invention of suburbia. The nature of intensification is also important; while development in mixed-use town centers is usually perceived to have a positive effect, especially if landscaping and urban design improvements are subsequently implemented, infill housing developments in residential suburbs are frequently perceived as being of poor quality and therefore having a detrimental effect on the environment, and sustainability in general.

 

            As sustainability requires a combination of environmental, social and economic improvements it is important to discover whether the claims of the compact city model can be substantiated. Possibly the least explored, but potentially most important aspect of the compact city model is whether or not it contributes to social equity and a higher quality of living. As Elkin et. al. (1991: 203) importantly point out, “sustainable development involves more than just environmental conversation; it embraces the need for equity. Both intra-generational equity providing for the needs of the least advantaged in society, and inter-generational equity, ensuring a fair treatment of future generations need to be considered.” From empirical research conducted by Burton (2000) it appears that there is a positive link between city compactness and social equity, although no definitive answer. Many variables prevent any clear conclusions from being made. In many cases equality rather than equity is enhanced, and therefore the absolute position of the poor does not improve, even though some improvement about their relative position is evident. Moreover, the influence of the compact city on social equity depends upon the form it takes, while cities with a large proportion of high-density housing in the form of terraces and flats combined with a large quantity of locally provided services and facilities had the highest levels of social equity, in other areas such as residential infill housing there is little evidence of any improvements in social equity. Many factors contributed to social equity other than urban design. Socio-economic and ethnic factors are important agents for social equity that often operate completely independently from the city’s ‘compactness’. Therefore “the research provides evidence to support the view that the compact city may support social equity, but only if it is implemented in such a way that maximizes the benefits and ameliorates that potential problems.” (Burton, 2000: 29)

 

            Another related claim of the compact city’s advocates is that urban intensification improves a city’s vibrancy and culture, and leads to a sense of community, local identity and safety. This claim has been strongly challenged by researchers, who have discovered that any findings generally vary between mixed-use centers and residential suburbs – with town centers offering more cultural and entertainment facilities, because of the concentration of retail and employment activities. (Williams, 2000) Simply linking an increase or decrease in urban vibrancy to intensification or decentralization ignores many other factors that may play an even more important role, changes in social behavior or increasing affluence could be seen as playing a more important role in an increase in the number or restaurants, bars and clubs than urban density. In suburban areas, the link between intensification and a sense of community, local identity and safety is largely negative. Intensification has often led to a decrease in the number of home-owning families in the area, replaced by small households, sharers or single-person households. Higher densities has meant more neighbors, as well as neighbors of increasingly diverse socio-economic backgrounds which has led to a loss of local identity or a sense of community. In terms of improving a sense of safety, this appears to have been most successful in town centers, where a higher densities and redevelopment have led to a greater sense of safety due to security cameras, increased policing and the concentration of entertainment facilities in the town center. However, in residential suburbs the sense of safety has declined, as residents felt safer when they knew more of their neighbors, even though increased density claims to improve surveillance due to more people being in public spaces.

 

            In the socio-economic spheres, the influence of compact cities on sustainability has been mixed. The rejuvenation of existing urban structures as well as urban vitality seems to be just as reliant upon independent factors as they are on urban density, while quality of life and social equity are highly dependent on the particular form of intensification undertaken. To generalize, it appears that the compact city model has a more positive socio-economic impact in inner-city areas or town centers, where perceived safety has improved as well as the profitability of business and trading activities (such as entertainment facilities, restaurants, bars and clubs), although once again this may be the result of other factors. In contrast, any intensification in the residential suburbs appears to have had a negative socio-economic impact, as there has been a loss of local identity or any real sense of community as well as a loss of perceived safety.

 

            One of the strongest arguments for the compact city model, in the opinion of its advocates, is the theory that a compact city will reduce the need to travel, and will increase the feasibility of public transport, thus reducing emissions and contributing to environmental sustainability. According to Roger and Burdett (2001: 9) “the more you move away from a town center the less efficient services become. Public transport becomes either more expensive or more scarce (or both), sewers and rubbish collection become inefficient.” They believe that high-density environments can provide the critical mass necessary to make public services work more efficiently. However, the results of empirical testing by a number of researchers (Breheny, 2001 and Williams, 2000 among them) linking higher densities with a reduced number of trips made by cars have proved less than conclusive. Any significant switch to public transport has been found to require significantly higher densities than currently evident in suburbs, while other factors such as gasoline prices have proved to be just as important as urban density in determining the transport mode used by residents. The type of trip undertaken by residents also influences the impact of intensification, while short trips to local employment or shopping may decrease; there is no evidence that urban density will have any impact upon those seeking specialized employment or a different shopping experience and/or leisure pursuit. Growth in car ownership as well as increasingly diffuse life patterns are considerable factors that have led to the inability to reduce travel demands of energy-rich modes of transport, and it seems that changes outside the realm of planning through education or culture change will be required to influence travel patterns at a sustained level. (Williams, 2000)

 

            Possibly the most successful argument for compact cities is that urban intensification represents the most sustainable use of land. The desire to retain rural and agricultural land and to re-use urban land for development indeed does represent a far more sustainable use of land than urban sprawl. The use of ‘brownfield’ sites for development rather than the urban fringe is clearly beneficial as it not only conserves the valuable countryside, but also potentially regenerates the inner-city areas, some of which had become semi-abandoned in the post-industrial era. De Roo (2000: 152) argues that this is the crux of the issue, as “the compact city is most of all a spatial concept with the intention of intensifying the use of urban space ‘as much as possible’, thereby improving the quality of urban life and sparing the countryside.” However, he also argues that the compact city is likely to have a detrimental effect upon the environment in the city, as the result of an ‘environmental clash’ between housing, industry and traffic that can no longer be solved through the traditional methods of placing distance between ‘environmentally intrusive activities’ and ‘environmentally sensitive areas’ through zoning. As a result of its mixed-use and compaction ideologies “the compact city policy makes it difficult to solve environmental conflicts by keeping a sufficient distance between intrusive forces and environmentally sensitive areas, activities and functions.” (de Roo, 2000: 154) The impact of intensification policies on the urban landscape is a highly debatable subject, and is critically important to the overall sustainability of the compact city, as the unsustainable nature of the city might just be shifted from the urban fringe to the central city.

 

            The potential loss of greenery in towns has been identified a sign that compact cities are not in fact contributing to sustainability.  In London, this fear has been justified to some extent, especially in suburban areas that have experienced intensification, as “backland and infill development had meant the loss of trees and shrubs in gardens and public spaces.” (Williams, 2000: 36) In more densely populated areas it has generally been found that more stringent regulation governing the removal of trees and shrubs has led to a reduced impact – to the extent that some inner-city suburbs in London have the same percentage of green-space as those on the urban fringe. (Williams, 2000) The impact of intensification on the built environment is also spatially varied, as in some areas (particularly mixed-use town centers) development has been seen to be done in a tasteful manner and therefore has had a positive effect one the city; while in other areas (typically residential suburbs that have experienced infill housing), “new development has been on such a large scale, or of such poor quality and design that it has had all the opposite effects of disfiguring cities.” (Williams, 2000: 37) Unsurprisingly, the impact of intensification on the built environment is greatly dependent upon how it is managed, and that if landscaping and planting are given priority by developers and planners from the outset, any loss of amenity value is not inevitable.

 

In a similar scenario to the socio-economic impacts of the ‘compact city’ model, any environmental effects, either positive or negative, are varied depending on location as well as other variables unrelated to urban density. It also appears that the best results of intensification can be found in city or town centers rather than the residential suburbs. The method of intensification also has a profound influence on whether sustainability is being achieved or not, and careful planning and design is essential for any form of intensification to ‘work’. The lack of a correlation between urban density and reduced traffic flows is damaging to the ‘compact city’ argument as it can be seen as of critical importance to sustainability that fuel emissions be reduced. In summary, the ‘rush’ by planners and policymakers to adopt ‘compact city’ policies seems to be based solely upon a very narrow conception of sustainability – that of solely environmental sustainability and finding the most sustainable way to use land. For more comprehensive correlations to be made between intensification and sustainability a wider perspective needs to be employed, and problems surrounding socio-economic, and amenity value aspects of sustainability need to be addressed. This is, of course, an incredibly difficult proposition, and therefore means that this debate should continue well into the future.

 

 

 

 

 

LIST OF REFERENCES:

 

Beatley, T. (1995) “Planning and Sustainability: the elements of a new (improved?) Paradigm.” Journal of Planning Literature, 9, pp.383-395.

 

Breheny, M. (2001) “Densities and Sustainable Cities: the UK experience.” in M. Echenique and A. Saint (eds.) Cities for the New Millennium, London. pp. 39-51.

 

Burton, E. (2000) “The Potential of the Compact City for Promoting Social Equity.” in K. Williams, E. Burton and M. Jenks (eds.) Achieving Sustainable Urban Form, London. pp. 19-29.

 

de Roo, G. (2000) “Environmental Conflicts in Compact Cities: complexities, decision making, and policy approaches.” Environment and Planning B: Planning and Design, 27. pp. 151-162

 

Elkin, T., McLaren, D. and Hillman, M. (1991) Reviving the City: towards sustainable urban development, London.

 

Gordon, P. and Richardson, H.W. (1997) “Are Compact Cities a Desirable Planning Goal?” Journal of the American Planning Association, 63. pp. 95-106.

 

Rogers, R. and Burdett, R. “Let’s Cram More into the City.” in M. Echenique and A. Saint (eds.) Cities for the New Millennium, London, pp. 9-15.

 

Thomas, L. and Cousins W. (1996) “The Compact City: a successful, desirable and achievable urban form?” in M. Jenks, E. Burton and K. Williams (eds.) The Compact City: a sustainable urban form? London, pp.53-65.

 

Williams, K., Burton E. and Jenks, M. (2000) Achieving Sustainable Urban Form (Introduction), London.

 

Williams, K. (2000) “Does Intensifying Cities Make Them More Sustainable?” in K. Williams, E. Burton and M. Jenks (eds.) Achieving Sustainable Urban Form, London, pp. 30-45.

 

World Commission on Environment and Development, (1987) Our Common Future, Oxford.