ReviewAligning fragmented planning structures through a green infrastructure approach to urban development in the UK and USA
Introduction
The rapid development of green infrastructure (GI) in the UK and USA since the late 1990s provided scope for planners, in both locations, to reframe their approaches to urban planning. Over the subsequent decade the application of GI has diversified to address a range of terrestrial and water based development issues. This has led to variability in the use, and discussion of GI, lowering the level of consistency in its debates, and subsequently, hindering its mainstreaming within centralised (i.e. national) policy narratives. As a consequence, although a cascading of GI principles and actions are evident in its development, the policy structures and delivery mechanisms that support this process lack consistency, limiting to some extent, a consensual understanding of GI, globally and locally.
Evaluations of the development, meanings and use of GI in urban planning have been made since the concept came to prominence through the President's Council on Sustainable Development in 1998 (Mell, 2010), the Conservation Fund and the USDA Forest Service in 1999 (PCSD, 1999, Hellmund and Smith Somers, 2006), and the Environmental Protection Agency (EPA) (Rouse and Bunster-Ossa, 2013). However, due to specific geographical applications, consensus of its meaning (as a concept and of its benefits) has not, to date, been achieved (cf. Wright, 2011, Mell, 2013). In part, this is due to the interaction of normative political and spatial approaches to landscape management, but also reflects the varied nature of urban planning in the UK and USA, illustrating the complexity of situating GI development, when the structures that support planning policy are in a constant state of change.
In North America, and specifically in the USA, this process is focussed predominately on water systems and ecological resource management (Benedict and McMahon, 2006, Weber et al., 2006); whereas, in the UK GI planning has focused on establishing an integrated approach to landscape management addressing social, economic and environmental change (Kambites and Owen, 2006, Thomas and Littlewood, 2010). Although such distinctions suggest that a fragmented interpretation of GI has been developed, over the last five years (2010 onwards), a coalition of GI meaning has become increasingly visible within planning discourses in the UK and USA (Mell, 2013).
One consistent constraint to the development of such a consensus has been the influence of changing planning policy structures. In both the UK and USA prominent advocacy organisations have attempted to integrate GI within policy and delivery structures but with limited success (Allen, 2012, Kambites and Owen, 2006, Lerner and Allen, 2012, Thomas and Littlewood, 2010). As Mell (2010) illustrated a number of prominent environmental advocacy agencies, in both the UK and USA, have engaged with the development of a GI planning agenda; however, there has been a variable, and in some senses, a more ‘passive’ approach from government. ‘Throughout this paper’ are used to describe governmental environmentally focussed organisations, Non-Governmental Organisations (NGOs), and Environmental NGO (ENGOs), which influence policy and delivery strategies. Advocacy agencies are organisations which have effectively (or otherwise) lobbied policy and decision-makers to acknowledge, and latterly, engage with the growing GI evidence base. Delivery agencies are organisations specialising in implementing GI. Local government can also be considered delivery agents if they implement development plans either internally or in collaboration with other agencies. Therefore, although planning policy can be considered multi-directional, the potential pluralism of its focus makes it difficult for advocacy agents to target delivery in line with government mandates. Changes in government policy, co-operation and funding, have also been highlighted as barriers to effective GI implementation (Beatley, 2000).
To address these issues this paper examines the development of GI and its application in the UK and USA. Through an evaluation of each nation's implementation of GI, the paper argues that both nations have experienced changes to the process of planning; shifts which are reflected in how planners address GI. The paper proposes that although its antecedents have established a globalised understanding of what GI is, the implementation of these principles, within individual nations and/or regions, has been increasingly localised. They include: sustainability, multi-functionality, accessibility, connectivity, urban focussed, advocate led policy formation and implementation.
Through a re-interpretation of the diverse conceptual principles of GI, this paper discusses whether a ‘policy-implementation gap’ exists, to illustrate the fluidity of GI policy-application. The development and application of GI in the UK and USA are subsequently used to assess whether it is viable to promote a consensual approach to the pluralistic discussions of GI. Through an examination of the opportunities and constraints placed upon GI development, this paper reflects on how the multi-directional: read pluralistic, nature of planning is being influenced by a constantly changing policy arena. Although the paper makes reference to the evolving GI research agendas in Europe and Asia, these locations are not discussed in the evaluation. They are presented as evidence of the fluidity of the implementation gaps between the conceptual foundations of GI and its delivery. By reflecting on the influence of policy structures and advocacy stakeholders within the praxis of GI, this paper debates whether this ‘gap’ can be addressed.
Section snippets
Review methodology
The following paper does not present, or propose to use, a singular definition of GI, as it recognises plurality to its meanings and uses exists between the UK and USA. In the context of this paper GI can be considered as a concept for strategically planning and managing green and open space as a functional network at different spatial scales and is based on a number of specific but varying principles (see Fig. 1.). This reflects the fluidity of expression, which has become increasingly visible
The rise of green infrastructure as a ‘global’ and ‘localised’ concept
Although we have seen a rapid growth of GI research since the late 1990s, as early as the 1960s Ian McHarg (1969) called for a re-evaluation of how planners address green space: what would now be identified as GI in policy discussions. McHarg proposed that the variability of urban nature could address a range of planning opportunities; in essence illustrating the value of multi-functional GI. He proposed that we rethink ‘nature’ by reintegrating landscape thinking within an urban context.
Planning policy structures in the UK and USA
The dominant planning structures of the UK and USA have been central influences on the development of GI, with the current promotion of economically focussed policy limiting the breadth, and indeed impact, of landscape and environmental planning (Beatley, 2000, DCLG, 2012). Situating GI within national planning frameworks thus highlights the subjectivity applied to its use within locationally specific policy-delivery narratives. Such pluralism has seen GI being adapted through various policy
Global and local barriers to and opportunities for green infrastructure development
A number of barriers and opportunities, some of which are discussed previously, have been identified in both the UK and USA as affecting the development of GI (Mell, 2010). These factors can be broadly described as being a combination of political, economic and environmental influences, with Fig. 3 suggesting that a number of these can be deemed comparable in both locations. The classifications proposed in Fig. 3 were drawn from an extensive review of the academic/practitioner literature and
Establishing consensus for green infrastructure development
Several authors have debated the relevance of creating consensus within GI planning as a mechanism to address the diversity evident in policy, decision-making and implementation (cf. Lennon, 2014). To achieve such a consensual state, an idealised framework for planning which provides a foundation for both global and local uses of GI would need to be developed resembling that proposed by Mell (see Fig. 4; 2010: p. 239). However, a counter argument has been proposed noting that consensus may add
Future mainstreaming options for green infrastructure planning in the UK and USA
The diversity of GI applications has enabled practitioners to apply its principles in varied and innovative ways (TCPA, 2011). Whilst central government in the UK and USA still limit policy support for GI planning, a more regional/sub-regional advocacy approach has witnessed significant uptake (Thomas and Littlewood, 2010). Although continuity can be seen in its application, proposing that investment in GI is progressive, delivery consensus is still varied. A number of investment and
Conclusions
The discussion presented in this paper indicates that a form of consensus is developing to frame GI. Despite the constraints placed upon its conceptual development by the complexities of government in both the UK and USA, broad agreements of GI principles and its deliverable benefits are evident in both locations (Mell, 2010, Mell, 2013). Furthermore, although delivery still fails, in some cases, to show comparability between projects or investments, the wider debates of GI utility are becoming
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