ReviewStakeholder participation for environmental management: A literature review
Introduction
Environmental problems are typically complex, uncertain, multi-scale and affect multiple actors and agencies. This demands transparent decision-making that is flexible to changing circumstances, and embraces a diversity of knowledges and values. To achieve this, stakeholder participation is increasingly being sought and embedded into environmental decision-making processes, from local to international scales (e.g. Stringer et al., 2007). Widespread acceptance and promotion of participation has partly been driven by increasing public scepticism about science, increasing knowledge and interest in environmental decisions (Irwin’s (1995) “citizens’ science”) and ongoing policy trends that emphasise sustainable development and partnership working (Younge and Fowkes, 2003, Richards et al., 2004). Participation in environmental decision-making is increasingly becoming regarded as a democratic right (and is enshrined as such in the United Nations Economic Commission for Europe’s 1998 Arhus Convention), and this right is increasingly being used by proliferating environmental interest and pressure groups. In addition to normative arguments such as this, many pragmatic benefits have been claimed for participation; by involving stakeholders, it is argued that the quality and durability of decisions is likely to be greater (e.g. Fischer, 2000, Beierle, 2002, Reed et al., 2008). However, such claims have rarely been tested, and there is growing disillusionment among environmental managers and conservationists who have failed to see these claims realised. Others have sought to address and move beyond these critiques, learning from the mistakes of the participation panacea, to develop a more sensitive, post-participation approach.
This literature review aims to examine evidence for the claims that have been made for and against stakeholder participation and, on this basis, to identify suggestions for best practice participation. This is done in the context of a brief history of participatory approaches to environmental decision-making, and the typologies that have been developed to understand the basis for stakeholder participation. In this article, participation is defined as a process where individuals, groups and organisations choose to take an active role in making decisions that affect them (Wandersman, 1981, Wilcox, 2003, Rowe et al., 2004). This definition focuses on stakeholder participation rather than broader public participation, if stakeholders are defined as those who are affected by or can affect a decision (after Freeman, 1984). This article focuses on stakeholder participation because for purposes of efficiency, most conservationists focus on engaging those who hold a stake (whether directly or indirectly) in the scope of their initiative, rather than attempting to meaningfully engage with the wider public.
Section snippets
Histories and typologies of participation
Approaches to stakeholder participation have progressed through a series of recognisable phases: from awareness raising in the late 1960s (the anti-modernisation critique of the transfer of technology paradigm; see van Tatenhove and Leroy (2003) for a review); incorporating local perspectives in data collection and planning in the 1970s (Pretty, 1995a, Pretty, 1995b); the development of techniques that recognised local knowledge and “put the last first” such as farming systems research and
Benefits of participation: evidence for the claims?
The many claimed benefits of stakeholder participation have to an extent driven its widespread incorporation into national and international policy. At the same time, disillusionment has been growing amongst practitioners, stakeholders and the wider public, who feel let down when these claims are not realised. These claims can be broadly categorised under normative and pragmatic arguments for stakeholder engagement in environmental decision-making.
Normative claims focus on benefits for
Best practice stakeholder participation
When individual practitioners and stakeholders are asked, much disagreement still exists over what constitutes best practice. For example, Webler et al., 2001, Webler and Tuler, 2006 used Q methodology (a form of factor analysis used to study subjective viewpoints among participants) to identify four distinct views of best practice from those who had taken part in ten participatory processes, who differed over how to tackle issues of power and trust, and the role of strong leadership/direction
Conclusion
Although few of the claims that are made for stakeholder participation have been tested, there is evidence that it can enhance the quality of environmental decisions, possibly due to more comprehensive information inputs. However, the quality of decisions made through stakeholder participation is strongly dependant on the nature of the process leading to them. Deficiencies in this process are most commonly blamed for the failures that have led to disillusionment in stakeholder participation.
Acknowledgements
Funded by the Rural Economy and Land Use programme (UK Research Councils with DEFRA and SEERAD) as part of the Sustainable Uplands project (RES-227-25-0001) and EU Framework 6 (Contract No. 037046). Thanks to Nicky Geeson, Jan de Graaff, Joseph Murphy, Jens Newig, Diana Pound, Despina Psarra, Elisabeth Simelton and three anonymous reviewers for comments on an earlier draft of this manuscript.
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