Transition Management is an alternative model of Environmental Governance which seeks to guide the gradual, continuous process of transformation of socio-political landscapes, socio-technical practices and “the structural character of society” from one equilibrium to another. [1][2] In its application, transition management seeks to steer the outcome of change to lessen inherent uncertainty, produce desirable social outcomes and enhance resilience during the transformation of socio-technical systsms (ibid).This is primarily achieved by engaging a wide range of stakeholders over the multiple levels to create shared visions and goals which are then tested for practicality through the use of experimentation, learning and adaptation at the niche level. The model is often discussed in reference to Sustainable Development and the possible use of the model as a method for change.

Key principles to transition management as a form of governance:[3]

  • seeks to widen participation by taking a multi-actor approach in order to encompass societal values and beliefs
  • takes a long term perspective (between 1-3 generations) creating a basket of visions in which short term objectives can be identified
  • focused on learning at the niche level, experiments are used to identify how successful a particular pathway could be and uses the concept of “Learn by doing, doing by learning”[4]
  • a systems thinking approach which identifies that problems will span multiple domains, levels and actors.

History

edit

There have been numerous societal transitions in the past, studied examples include the transition from horse drawn carriage to motorised cars and the change from physical telegraphy to the electric telephone.[5] There are a number of theories that muse over how transition management evolved into being. One school of thought identifies the sociological aspect of transition as deeply rooted within population dynamics and the evolution of society from high birth rate/high death rate to low birth rate/low death rate. [6] Other theorists consider that transition management has its basis within systems theory and the co-evolution of social and technical factors within the system[7]. Most agree that the shift in the political landscape, from a centralised government to a more liberal, market-based structure has allowed new forms of bottom-up governance styles to rise to prominence and a break from dominant approaches. [8]The most notable use of Transition Management can be established through its development into a practical tool by the Dutch Government to manage the radical transformation of their energy systems in the early 2000s.[9]


Broad Definition

edit

Transition Management is a new approach for tackling the complex issue of Sustainable Development. Sustainable Development in itself is a dynamic, multi-dimensional, multi-actor and multi-level problem that is in a constant state of flux[10]. Critics consider that the current Political System is insufficiently equppied to deal with the complexity of the issue and that incremental changes will not address the fundamental system failures that underpin the issue. As an alternative to traditional politics, Transition Management will seek to steer development in a more sustainable direction by identifying and fundamentally restructuring the unsustainable systems that underpin our society. The goal of transition management is geared towards enabling, facilitating and guiding the social, technical and political transformations required by embedded societal systems to bring about sustainability[11]. The need for such a model of governance has arisen through the persistence of problems which have developed to span multi-actors, multi-levels and multi-domains. The inherent complexity of society [12] (from the difference of perspectives, norms and values) added to the intricacy of modern day issues requires a new form of governance. Therefore Transition Management recognises the need to address this problem on the multiple levels and dimensions in which it manifests. The approach seeks to widen participation by encouraging bottom-up approaches that are supported in a top-down manner. The synergy gained from utilising Transition Management to provide a novel approach to the complex issue of Sustainable Development could be essential if progress is to be made on the issue.

Unlike traditional forms of regulation that use Command and Control techniques, Transition Management does not seek to control the uncertainties of change but steer, indirectly influence and redirect the choices of actors towards sustainability [13] In the long-term, transition management will seek to completely transform the system through the process of “creative destruction”[14] , much of the literature considers that only the radical rebuilding of our society's systems will be able to transcend the stable lock-in to unsustainable systems which has been systematically reinforced by aspects of the landscape and regime levels. [15] [16]


Levels Within Socio-technical Systems

edit

Most literature recognises that there are three separate levels that Transition Management must work within; Landscape, Regime and Niche: [17]. [18]

  • Landscape (Macro) refers to the overall socio-technical setting that encompasses both the intangible aspects of social values, political beliefs and world views and the tangible facets of the built environment including institutions and the functions of the marketplace such as prices, costs, trade patterns and incomes.
  • Regime (Meso) refers to the dominant practices, rules and technologies that provide stability and reinforcement to the prevailing socio-technical systems.
  • Niche (Mirco) is the level or 'area' at which the space is provided for radical innovation and experimentation. This level is less subject to market and regulation influences and can facilitate the interactions between actors that support product innovation.

File:Wikiuploadfoxon.png


Actors

edit

Each level has its own set of actors that interact in different ways, broadly they can be defined into the following categories:

  • Government which creates top-down pressure from regulation, and the use of market incentives, while also encouraging the 'collective learning process' by supporting innovation financially and providing access to information provided by advisory boards [19] [20]
  • Market Based Actors, who interact both vertically through the supply chain and horizontally with other industry leaders to share best practice and create innovative ideas.

Power and Relationships

edit

Power within the transition process is distributed rather than being top-down in nature; every actor plays a part in shaping the transition. This distributed power enables the process of mutual adaptation towards collective goals and the emergence of self-organised socio-technical ‘trajectories’[21]. However, power is not necessarily evenly distributed; relationships and the power of actors within any system are always mixed which gives rise to different forms of interaction and transition. Transition Management seeks to exploit this opportunity by involving a wide selection of participants within the process. There are also a number of other important reasons for widening the participation of actors within governance. Firstly, most actors will have different preferences, a small group of actors, even if representative, will fail to identify one vision that will be accepted by everybody. By engaging all actors a plurality of visions that share common factors can be established and provide the basis for the next step. Furthermore the use of widened participation is likely to attract stronger support and therefore less resistance to the transition. [22] In order to fully transform the landscape level, the underpinning socio-political values and beliefs will also need to be radically rewritten, without the full involvement of society, this may be suceptible to failure. Finally it has also been considered that the heterogeneity of society allows for collective learning which spurs the development of innovations through exploration at the niche level.[23]

Transition Management: A Multi Level Framework

edit

Kemp et al[24] put forward a framework for identifying the different type of activities of which transition management attempts to align. These activities are broadly divided into, strategic, tactical and operational and each activity has its own actors, agendas and strategies which co-evolve.

Strategic activities encompass the process of vision development; the collective action of goal and norm setting through discussion and the formulation of long term goals. Strategic activities will lead to changes in the ‘culture’ of the societal system at the landscape level. The focus of this activity is long term in scale (30years/Generations)[25]and directed towards transition at the landscape level and the system as a whole.

Tactical activities relate to the interaction between actors that steers development of both institutions in the landscape level and socio-technical structures (practices, regulations, technology) at the regime level. Tactical activities focus on interpreting the visions created by strategic activities into the regime level and into the various networks, organisations and institutions involved [26]. Tactical activities will also seek to identify the barriers that may be encountered (such as regulation, economic conditions) when interpreting these visions into the regime level.[27]At this stage, actors that have the ability to make changes are recruited to translate the transition vision into their own agendas.

Finally the operational activites constitute the process of learning by doing through experimentation and implementation at the niche level. It has a much short time span of 0-5years and is focused on the radical innovation that will transform “societal, technological, institutional, and behavioural practices” that will in turn filter up and transform structures, culture and routines in the regime and landscape levels (Ibid).

A further activity can be considered which establishes the process of assessment and evaluation of societal change. One can observe that reflexive activities can be both embedded within policy and regulation but also as a function of society and the evaluation of policies through the media and internet (ibid).

Transition Management in Practice

edit

There are number of key aspects that differentiate Transition Management from other forms of governance, these differences are most apparent due to the model’s prescriptive nature. With the concept still being quite fresh and only a handful of case studies to draw from the methodology is still under debate. However most literature (See References - Loorbach, Kemp, Meadowcroft, Foxon) constitutes the following methodology:

A problem becomes apparent to actors throughout the levels and domains; the first step involves defining the key parameters of the problem then characteristing the existing regime and landscape pressures. Differences in interpretation, perceived pressures, opinions and preference ensues the construction of a plurality of visions and solutions for consideration. A ‘basket of objectives’ is created which express the shared visions and goals of the actors. [28]The visions outlined are long term in nature most commonly spanning at least one generation if not more and are used to inform short term objectives. [29] These visions can be expressed in a number of ways; more common forms include the use of pathways, scenarios and blueprints. As an example, if the problem of the unsustainable nature of our oil-dependent nation is presented, visions that may be put forward that constitute a carbon-neutral future include; the hydrogen economy, the all-electric society and the transition to global energy infrastructure to facilitate the maximisation of renewable energy.[30] [31] Although each vision will require different socio-technical changes they will all seek to broadly ensure the same goals are met, for example a low or no carbon economy and a secure and reliable supply.

Once the pathways have been created short term 'interim' objectives can be formed through Backcasting (as illustrated by the purple lines in the diagram) and actors within the niche level have the opportunity to form innovative solutions to the problem that may contribute to one of more of the pathways. Transition Management will seek to identify those niches that will likely destablise the regime level and contribute the most to its transformation.[32] Once identified these niche opportunities can be supported by regime changes such as new policy implementation that provide new funding opportunities. In addition to deliberative steering of such choices, pressure can also filter down from the landscape level in the form of market forces which may also steer transition. Experiments within the niche level form a series of 'development rounds' which provide information to decision makers regarding the viability of different options. [33] The information provided by the development rounds is evaluated and if the options are considered to be viable the solution is rolled out primarily on a small scale. Evaluative information can also be used to inform the overall vision created (as illustrated in red in the diagram). Eventually the development of options snowball down a particular pathway and a full system transition takes place. Not all development and transition time-scales are consistent within and between the different levels, actors and domains; some change much more quickly than others. In particular, the landscape level is much slower to change than the regime or niche levels; this has lead to the concept being labelled as chaotic and non-linear in nature.[34]

File:Existing vs TM transitions.png

Tansition Management in the UK

edit

Although being less apparent than the Dutch energy transformation, it appears that there is an increasing pressure for theorists to establish frameworks to guide a similar transition within the UK. The UK energy sector is an example of a socio-technical subsystem that exhibits strong lock-in, socially, politically and technically. [35] The technical domain exhibits a strongly centralised infrastructure facilitated by a distribution network, socially speaking the UK energy system is heavily relied upon to provide welfare and enable economic activity. A number of landscape and regime pressures have emerged which impact on the system, primarily related to security of supply and the issue of climate change. The system has also come under pressure from the landscape level in the form of volatile market prices and the impact of the credit crunch. Meanwhile, development at the niche level has continued to build significant levels of alternative technologies and system possibilities through innovation such as offshore wind, wave and tidal power. At the regime level, the institutions such as the European Investment Bank are beginning to provide funding to facilitate the resources required to advance such niche technology. Furthermore policies such as that of the Renewables Obligation channels funding from the energy industry to support the niche space and development. As per the method, a number of visions are currently being explored, including smart infrastructure, renewable energy alternatives and the viability of hydrogen. The UK Government uses the Renewable Obligation to 'steer' innovators towards particular solutions. More Renewable Obligation Certificates are awarded to those technologies that are pre-demonstration such as tidal and wave power, while developed technologies such as onshore wind receive less..[36]

Although there are a number of indicators that suggest the Transition Management model of Governance is beginning to emerge within the sector, including in-depth literature outlining the methodology and possible pathways, the UK Government’s current pathway (embodied in the UK Low Carbon Transition Plan) does not appear to embody the radical transformation required by Transition Management. Instead of seeking radical socio-technical transformation, the plan seeks to incrementally improve the system by seeking behavioral changes such as energy efficiency and technical changes by enhancing the contribution of renewables.[37] Without radical infrastructure change the UK risks locking-out a number of promising possible alternatives and may significantly increase the cost of transformation in the future when the need for fundamental systems change becomes more apparent as the current system becomes more insufficient. [38]



  1. ^ Foxton, T (September 2008). [www.lowcarbonpathways.org.uk/lowcarbon/.../Sust_Transitions_Conf_paper_Foxon.pdf "Transition pathways for a low carbon energy system in the UK: assessing the compatibility of large-scale and small-scale options"] (PDF). 7th BIEE Academic Conference, St Johns College. {{cite journal}}: Check |url= value (help); Unknown parameter |coauthors= ignored (|author= suggested) (help)CS1 maint: date and year (link)
  2. ^ Meadowcroft, James (2009). "What about the politics? Sustainable development, transition management, and long term energy transitions". Policy Science. 42 (4): 323–340. doi:10.1007/s11077-009-9097-z.
  3. ^ Loorbach, Derk (2007). Transition Management: New mode of governance for sustainable development. Utrecht, Netherlands: International Books.
  4. ^ Loorbach, Derk (2007). Transition Management: New mode of governance for sustainable development. Utrecht, Netherlands: International Books.
  5. ^ Elzen, B (2004). System innovation and the transition to sustainability: theory, evidence and policy. Edward Elgar Publishing.
  6. ^ Davis, K (1945). "The world demographic transition cited by Rotmans et al 2001 "More Evolution than Revolution: Transition Management in Public Policy"". Annals of the American Academy of Political and Social Science. 237 (4): 1–11. doi:10.1177/000271624523700102.
  7. ^ Shove, E (2007). "Caution! Transitions ahead: politics, practice and sustainable transition management". Environment and Planning. 39 (4): 763–770. doi:10.1068/a39310. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  8. ^ Loorbach, Derk (2010). "Transition Management for Sustainable Development: A perscriptive, complexity-based governance model". Governance: An International Journal of Policy, Administration, and Institutions. 23 (1): 161–183. doi:10.1111/j.1468-0491.2009.01471.x.
  9. ^ Meadowcroft, James (2009). "What about the politics? Sustainable development, transition management, and long term energy transitions". Policy Science. 42 (4): 323–340. doi:10.1007/s11077-009-9097-z.
  10. ^ Kemp, R (2007). "Transition management as a model for managing processes of co-evolution towards sustainable development". The International Journal of Sustainable Development and World Ecology. 14 (1): 78–91. doi:10.1080/13504500709469709. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  11. ^ Kemp, R (2003). "Governance for sustainability through transition management" (PDF). IHDP-conference. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  12. ^ Loorbach, Derk (2007). Transition Management: New mode of governance for sustainable development. Utrecht, Netherlands: International Books.
  13. ^ Loorbach, Derk (2007). Transition Management: New mode of governance for Sustainable Development. Utrecht, Netherlands: International Books.
  14. ^ Schumpter, J (1934). The Theory of Economic Development. Harvard University Press.
  15. ^ Meadowcroft, James (2009). "What about the politics? Sustainable development, transition management, and long term energy transitions". Policy Science. 42 (4): 323–340. doi:10.1007/s11077-009-9097-z.
  16. ^ Verbong, G (2010). "Exploring sustainability transitions in the electricity sector with socio-technical pathways". Technological Forecasting and Social Change. 77 (8): 1214–1221. doi:10.1016/j.techfore.2010.04.008. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  17. ^ Kemp, R (2003). "Governance for sustainability through transition management" (PDF). IHDP-conference. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  18. ^ Foxon, J (2009). "Transition pathways for a UK low carbon energy system: exploring different governance patterns" (PDF). Paper for 1st European Conference on Sustainability Transitions: "Dynamics and Governance of Transitions to Sustainability", Amsterdam. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  19. ^ Foxon, J (2009). "Transition pathways for a UK low carbon energy system: exploring different governance patterns" (PDF). Paper for 1st European Conference on Sustainability Transitions: "Dynamics and Governance of Transitions to Sustainability", Amsterdam. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  20. ^ Rotmans, J (2001). "More evolution than revolution: transition management in public policy". Foresight. 3 (1): 15–31. doi:10.1108/14636680110803003. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  21. ^ Kemp, R (2005). "Governance for sustainable development: moving from theory to practice" (PDF). International Journal of Sustainable Development. 8 (1): 12. doi:10.1504/IJSD.2005.007372. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  22. ^ Rotmans, J (2001). "More evolution than revolution: transition management in public policy". Foresight. 3 (1): 15–31. doi:10.1108/14636680110803003. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  23. ^ Foxon, J (2009). "Transition pathways for a UK low carbon energy system: exploring different governance patterns" (PDF). Paper for 1st European Conference on Sustainability Transitions: "Dynamics and Governance of Transitions to Sustainability", Amsterdam. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  24. ^ Kemp, R (2007). "Transition management as a model for managing processes of co-evolution towards sustainable development". The International Journal of Sustainable Development and World Ecology. 14 (1): 78–91. doi:10.1080/13504500709469709. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  25. ^ Loorbach, Derk (2010). "Transition Management for Sustainable Development: A perscriptive, complexity-based governance model". Governance: An International Journal of Policy, Administration, and Institutions. 23 (1): 161–183. doi:10.1111/j.1468-0491.2009.01471.x.
  26. ^ Kemp, R (2007). "Transition management as a model for managing processes of co-evolution towards sustainable development". The International Journal of Sustainable Development and World Ecology. 14 (1): 78–91. doi:10.1080/13504500709469709. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  27. ^ Loorbach, Derk (2010). "Transition Management for Sustainable Development: A perscriptive, complexity-based governance model". Governance: An International Journal of Policy, Administration, and Institutions. 23 (1): 161–183. doi:10.1111/j.1468-0491.2009.01471.x.
  28. ^ Kemp, R (2007). "Transition management as a model for managing processes of co-evolution towards sustainable development". The International Journal of Sustainable Development and World Ecology. 14 (1): 78–91. doi:10.1080/13504500709469709. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  29. ^ Rotmans, J (2001). "More evolution than revolution: transition management in public policy". Foresight. 3 (1): 15–31. doi:10.1108/14636680110803003. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  30. ^ Meadowcroft, James (2009). "What about the politics? Sustainable development, transition management, and long term energy transitions". Policy Science. 42 (4): 323–340. doi:10.1007/s11077-009-9097-z.
  31. ^ Verbong, G (2010). "Exploring sustainability transitions in the electricity sector with socio-technical pathways". Technological Forecasting and Social Change. 77 (8): 1214–1221. doi:10.1016/j.techfore.2010.04.008. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  32. ^ Foxon, J (2009). "Transition pathways for a UK low carbon energy system: exploring different governance patterns" (PDF). Paper for 1st European Conference on Sustainability Transitions: "Dynamics and Governance of Transitions to Sustainability", Amsterdam. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  33. ^ Rotmans, J (2001). "More evolution than revolution: transition management in public policy". Foresight. 3 (1): 15–31. doi:10.1108/14636680110803003. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  34. ^ Foxon, J (2009). "Transition pathways for a UK low carbon energy system: exploring different governance patterns" (PDF). Paper for 1st European Conference on Sustainability Transitions: "Dynamics and Governance of Transitions to Sustainability", Amsterdam. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  35. ^ Rotmans, J (2001). "More evolution than revolution: transition management in public policy". Foresight. 3 (1): 15–31. doi:10.1108/14636680110803003. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)
  36. ^ DECC. "Renewables Obligation".
  37. ^ DECC. "The UK Low Carbon Transition Plan".
  38. ^ Rotmans, J (2001). "More evolution than revolution: transition management in public policy". Foresight. 3 (1): 15–31. doi:10.1108/14636680110803003. {{cite journal}}: Unknown parameter |coauthors= ignored (|author= suggested) (help)


Tropical deforestation as a global concern rose to prominence in the 1980s and can be somewhat attributed to a fight for action by environmentalists and northern countries over the need to protect tropical woodland[1] [2] . Prior to this, a number of other economic and regulatory mechanisms such as financial aid, policy frameworks and trade conventions were established in the fight against deforestation. These include the International Tropical Timber Agreement (1983), the Convention of International Trade on Endangered Species (1975) and the Global Environment Facility (1991). Despite the increased level of concern on the run up to the 1992 Earth Summit held in Rio de Janeiro, tensions between the North and the global South over access to finance and technology for the preservation of forests protracted negotiations[3] . Although many Northern countries had hoped for a legally binding convention the resulting Statement of Forest Principles represents the “mean position of the lowest common denominator”[4] and is voluntary. Disappointed with the outcome of the Earth Summit, NGOs such as WWF-International began to turn their attention to industry for a more meaningful governance orientated resolution to the problem of deforestation[5] .

In the lead up to the Earth Summit, social groups, NGOs and industries were also beginning to consult on the issue of deforestation. In America the consultation process that eventually lead to the establishment of the FSC was initiated in 1990 by representatives of the timber industry, social groups and environmental organizations and ended in the confirmation of support for the development of a voluntary worldwide certification and accreditation governance system that would cover all forest types [6] . In the UK, NGO WWF began to facilitate action through the establishment of the 1995 Group, recruiting organisations that had been spurred on by instances of direct action and boycotting over the sale of tropical wood to form an NGO-Business partnership[7] . Through stakeholder involvement it became apparent that a standard setting body would be required to verify the source of wood products and define sustainable forest management. After 18 months of consultation in ten different countries the Forest Stewardship Council was finally established in 1993[8] .

The failure of Governments to reach any notable form of consensus in the form of an internationally reaching and legally binding agreement although causing disillusionment also created an opportunity for change through the involvement of civil society and business actors to form “soft law"[9] . As such the establishment of the Forest Stewardship Council as the response to this disillusionment also represents a global shift from Government to Governance and its creation is a primary example of the use of market and economic factors to create movement on a global environmental issue[10] . The evolving historical context in which the FSC was formed is theorized to reflect a much broader scepticism towards state power and as a consequence a shift away from traditional state-centric forms of regulation. This said, although the FSC transcends national boundaries, the state continues to play a part in the regulatory landscape of the domestic forest and as such the FSC must develop appropriate domestic rules to reflect this[11] .


References

edit
  1. ^ Humphreys, David (1996). Forest Politics: the Evolution of International Cooperation. London: Earthscan.
  2. ^ Kirton, John J., and M. J. Trebilcock. (2004). Hard Choices, Soft Law: Voluntary Standards in Global Trade, Environment, and Social Governance. Aldershot: Ashgate Publishing.{{cite book}}: CS1 maint: multiple names: authors list (link)
  3. ^ Humphreys, David (2008). "The Politics of 'Avoided Deforestation': Historical Context and Contemporary Issues". International Forestry Review. 10 (3): 433–442. doi:10.1505/ifor.10.3.433.
  4. ^ Humphreys, David (2008). "The Politics of 'Avoided Deforestation': Historical Context and Contemporary Issues". International Forestry Review. 10 (3): 433–442. doi:10.1505/ifor.10.3.433.
  5. ^ Murphy, D.F. and Bendell, J (2001). The Earthscan reader in Business and Sustainable Development. London: Earthscan.{{cite book}}: CS1 maint: multiple names: authors list (link)
  6. ^ FSC. "History of FSC". FSC. Retrieved 8 April 2011.
  7. ^ Murphy, D.F. and Bendell, J (2001). The Earthscan reader in Business and Sustainable Development. London: Earthscan.{{cite book}}: CS1 maint: multiple names: authors list (link)
  8. ^ FSC. "History of FSC". FSC. Retrieved 8 April 2011.
  9. ^ Kirton, John J., and M. J. Trebilcock (2004). Hard Choices, Soft Law: Voluntary Standards in Global Trade, Environment, and Social Governance. Aldershot: Ashgate Publishing.{{cite book}}: CS1 maint: multiple names: authors list (link)
  10. ^ Tollefson, Chris, Gale, Fred and Haley, David (2008). Setting the Standard: Certification, Governance, and the Forest Stewardship Council. Vancouver: UBC.{{cite book}}: CS1 maint: multiple names: authors list (link)
  11. ^ Kirton, John J., and Trebilcock, M.J. (2004). Hard Choices, Soft Law: Voluntary Standards in Global Trade, Environment, and Social Governance. Aldershot: Ashgate Publishing.{{cite book}}: CS1 maint: multiple names: authors list (link)