This paper argues strongly in favour of a re-examination of the term ‘sustainability’ in
international development research, policy and practice. It demonstrates that the term is understood pluralistically, being both environmental and economic. Within economic interpretations, this paper identifies three clear understandings of ‘sustainability’, which effect programme design and, ultimately, their impact on poverty significantly. The paper argues that the ramifications of this definition go far beyond semantics and have a significant impact on the development outcomes realised by programmes that incorporate the term. Having evaluated these conceptions, the paper argues for sustainability in development as being interventions that alter the causes of poverty so that the process through which change occurs is improved in an adaptive and permanent way, a permanent increase in adaptability. Evidence is drawn from a review of the literature and policy documentation.
Please reference the copyrighted version of this article Taylor, B., 2014, Who wants to give forever: Giving meaning to sustainability in development, Journal of International Development 26.
Introduction
Sustainability is a concept that has increasingly influenced development policy in the last two decades and yet the concept remains ill-defined. The term is highly contentious, yet plurality in its definition is not well understood by those who employ it (Kidd, 1992). Understanding is either too narrow considering only the environmental impact of development or, as in much development practice, too loose, considering anything that continues to exist beyond the life of a programme.
This paper takes what some might argue to be a partisan standpoint of considering only the perspective of the poor people whose lives development aims to improve. Grounded in world systems theory it takes the perspective that sustainability need not reproduce a snapshot of the present in the future rather it must leave, in aggregate, equivalent opportunities for the population (York et al., 2010). Also drawing on dependency theory, the reconfigured conception of sustainability needs to consider how development programmes have altered the systems that underpin poverty rather than how the symptoms of that poverty have been alleviated in the short term (Catterson and Lindahl, 1999; Fowler, 2000; Easterly, 2008). After a development programme has ended, what’s left behind?
The importance of sustainability under this conception has been recognised by practitioners and policy makers far more so than in academic literature. The recent inclusion of systemic change objectives in development policy, including in ‘making markets work for the poor’ (M4P) approaches, signifies a recognition of this understanding, incorporating economic considerations into programme objectives, including in new areas such as health and education (Carpenter, 2003; Best et al., 2005; Burra and Mahadevan, 2005; Miehlbradt et al., 2005; Porteous, 2005; Elliot et al., 2008). The Swiss Agency for Development and Cooperation (SDC) & Development for International Development (DfID) operational guide for the M4P approach defines sustainability in exactly these terms (DfID and SDC, 2008). However, there persists a looseness in the broader understanding of what is sustainable, rather than simply sustained – articulated by Anand and Sen’s danger of underspecification (2000; 2037). If something is built in a development programme, it will remain built once the programme has ended but is this truly sustainable without a consideration of the means through which new building might occur?
This paper aims to explore different concepts of sustainability in order to arrive at an understanding which better represents the long-term interests of poor people. The paper is structured as follows. The first section is a broad overview of some of the important definitions in considering sustainability in development so as to narrow the scope of the paper. The scope is further narrowed in the following section of the paper which argues in favour of the reprioritisation of sustainability objectives in favour of the poor people whose lives development programmes aim to improve. It does so via engagement with the currently more prominent environmental conceptions of sustainability.
Having narrowed the scope of the paper to economic conceptions of sustainability, then, the paper proceeds to disaggregate these further. Here, an examination is conducted of different approaches to development programming and how sustainable their impacts might be.
Firstly, the conception of sustainability as affordability is identified whereby donors see aid as an on-going commitment and a budgetary matter, rather than a question of how change can be delivered.
Secondly, the conception of sustainability as asset transfer is outlined and can be understood as programmes which approach aid as the direct delivery of assets to poor people, whether these are physical assets such as equipment or infrastructure, or intangible assets such as skills development.
Finally, sustainability as a permanent increase in adaptability conceives of a fundamental altering of the system in which poor people live and work. This view of sustainability necessitates an approach to development which ensures local ownership of the change that occurs and the ability to respond to changes in external factors.
The final section of the paper then draws together the preceding sections, examining how these various interpretations of sustainability in development have impacted on development programming and, ultimately, on the lives of poor people. This is used to outline the importance of sustainability in development programming and thus the fundamental consideration of how it is defined.
Key Definitions
It is important first to clarify the broader concept of sustainability and, in doing so, define the terms of this paper.
The roots of the term “sustainability” are so deeply embedded in fundamentally different concepts, each of which has valid claims to validity, that a search for a single definition seems futile. The existence of multiple meaning is tolerable if each analyst describes clearly what he means by sustainability (Kidd, 1992; 2).
The broadest, simplest and perhaps most universally acceptable definition of sustainability is given by Charles Kidd who states that “the wisdom of current policies and of proposed actions should be assessed in terms of their full long-range effects” (Kidd, 1992; 3). This allocates no time preference or specification of the nature of what is to be sustained.
It is necessary to clarify how it is understood for the purposes of the paper in the context of economic development. For some (Solow, 1974, for example) sustainability is about intergenerational equity and ‘nondeclining’ of welfare, income, consumption, capital stocks etc. This would appear, however, to be targeting sustainability of the status quo. Development is a dynamic process. Sustainability in development should target an increase in aggregate measures of living standards incorporating a marked increase in these measures for those at the lower end of any given scale. International development as a public sector, an academic discipline or a policy area, sees this objective being achieved through poverty reduction.
It should also be noted here that a separate paper could be written (and indeed many have, see Moss et al. (2006) for a review) on the sustainability of aid itself, with respect to the objectives of aid, the appropriate levels to bring about change and the incentives it creates for change to happen. Such papers suggest that there is a level beyond which aid itself perpetuates poverty by preventing the formation of the robust local institutions which, most agree, are fundamental to its reduction. These conclusions exclude contributions towards international public goods such as peacekeeping, trading blocs and research into diseases.
Systemic change approaches to development go further, taking the long-term view that aid itself is unsustainable and is useful in the short-medium term only to facilitate the construction of robust national systems of provision (Moyo, 2009; Rogerson, 2011). This paper, however, focuses on the sustainability of the change which current approaches to aid delivery aim to bring about.
More fundamental to the discussion that follows, however, is an understanding of the equally contested term ‘development’. While it is accepted that there are a number of potential understandings of development, this paper is based around the ‘development sector’ wherein development incorporates any outside intervention that aims to improve the lives of poor people. This includes any programme funded by official development assistance (ODA) or charitable donations which includes such objectives. It is accepted too that this definition is far from incontestable, with the subjectivity of the ‘improvement’ aspect of the definition, but it is beyond the scope of this paper to engage fully with this debate (see (Dwyer, 1977; Hirschman, 1988; Chambers, 1990) amongst others for a fuller discussion).
For clarity, then, this paper aims to examine how various understandings of ‘sustainability’ and ‘sustainable development’ are realised in the development programmes of donors (national governments, bi-lateral and multi-lateral agencies and NGOs).
Sustainability for Whom? Conservation and Sustainability
A second point of clarification is necessary before the paper can address sustainability more directly. It is fair to say that sustainability in development is a discourse dominated by environmental concerns (Lele, 1991; Åhman, 2013). Search for the terms “sustainable development” or “sustainability in development” in any journal aggregation database and over 90% of the most cited articles are related directly to conservation, ecology or the environment.
Environmental, ecological and conservational definitions of sustainability (of which there are many) are predicated on the ‘do no harm’ mantra that has long been prevalent in philanthropic and humanitarian work (Uvin, 2002; Brown et al., 2008). While their origins lie much earlier, a key piece of literature in this area came with the Brundtland Report (Brundtland, 1987) which had a significant influence in unifying environmental and development goals, recognising environmental limits to growth. The report defined sustainable development as “development that meets the needs of the present without compromising the ability of future generations to meet their own needs” (ibid.; Chapter 2).
This conception of ‘sustainable development’ identified in the Brundtland report is represented as “the Theory” in Figure 1.
Adams goes on to argue, contrary to the argument contained herein and argued elsewhere (Koning, 2001; Colantonio, 2009; Åhman, 2013), that environmental concerns have been marginalised in the years since the Brundtland Report and there is a need for a reprioritisation of environmental concerns in development practice.
A key criticism of the argument contained in the Brundtland report and subsequently articulated by Adams is that it appears to exist in a geo-political vacuum. Is this inter-temporal resource equilibrium taken at a global or a local scale? If a development programme results in a developing country being able to access their own non-renewable resources more readily, and consequently improve the living standards of poor people but at the same time results in greater carbon emissions, is the responsibility on the recipient country, the donor country, or the global population as a whole to mitigate this additional contribution to carbon emissions? The answers to these questions depend fundamentally on which of two diametrically opposed theories of growth and development one subscribes to; a world-systems perspective or neo-classical economics (Hornborg, 2003). Can economic growth lead to solutions to environmental problems or does this conception of sustainability, and the development policies that employ it, simply displace responsibility for ecological problems from those principally responsible for their creation to those that can least afford to address them? As articulated by Anand and Sen “a universalist approach cannot ignore the deprived people today in trying to prevent deprivation in the future” (2000; 2030).
The spirit of this argument was undoubtedly intended to mean that development practices should not consume or alter environmental conditions in such as way as to prevent future generations from meeting current standards of living. Interestingly, however, the wording of the definition – regarding “compromising the ability of future generations to meet their own needs” – inadvertently invokes theories of dependency and external funding which are grounded in the different economic conceptions of sustainability examined in this paper.
Anand and Sen (ibid.) argue for a recognition of the imperatives of securing the conditions of the current generation in parallel with the consideration of conditions that future generations will inherit.
Not working toward guaranteeing the basic capabilities to the future generations would be scandalous, but in the same way, not working toward bringing those elementary capabilities within the reach of the deprived in the present generation would also be outrageous. Given the implicit biases in many policy debates, there is a real need for jealously guarding that universalist perspective (2030).
This is not to say that environmental concerns are irrelevant to poor people today, even in the short term. Indeed, as convincingly argued by Dercon (2012), in accordance with the above, growth and the environment are fundamentally interlinked but environmental considerations should be made in development programmes only to the extent that they affect poor people:
...poverty reduction is likely to offer the poor most resilience to the increasing risks of climate change, and they should not be asked to pay the price for greening the planet (17)
Poor people are, in many cases, the most vulnerable to change in environmental conditions, given the proportion that are involved in agriculture. However, it is important to see environmental aspects of sustainability in this light; how they affect poor people. Development is not a laboratory through which Northern donors can experiment with new models of environmentally sustainable routes to growth, displaying how they would achieve development if they were starting from a similar position. Whatever the domestic political considerations, poverty reduction has to be the target of development programmes. The prioritisation of environmental conceptions of sustainability necessarily compromises the development imperatives of the present. The imposition on projects and programmes of stipulations which are viewed by Northern norms as environmentally progressive (as opposed to those which attempt to mitigate the negative consequences of growth on environmental degradation and subsequent growth at the local level) at the expense of those which offer the greatest opportunities for pro-poor growth is hypocritical and negligent towards the poverty reduction objectives explicitly pursued by donors (see DfID’s PEPE or USAID’s LEAD programme as examples). Donors require programmes to seek out investments which reduce carbon emissions or utilise recycled materials while at the same time exploring for more fossil fuels and producing waste at hundreds of times the rate of the countries in which these ‘environmentally sound’ programmes are conducted.
This paper aims to recapture sustainability objectives for the benefit of the current generation through concentrating on the relatively undeveloped concepts of the sustainability of different economic conceptions of the term. While the importance of how local environmental conditions impact on the lives of poor women and men in the short to medium term is recognised, the paper concentrates on economic considerations as it is these that have been ignored in current discussions of sustainability in development programming.
Sustained Vs. Sustainable: Economic Conceptions of Sustainability
Having argued for the necessity of poverty being the guiding principle of development programming, this paper now goes on to make its primary contribution in differentiating between economic perspectives of sustainability in development.
Despite the argument outlined above on the dominance of environmental concerns within sustainability discourse in development, economic sustainability is a concern of many involved in development programming, albeit as one of an ever growing number of considerations. Within this, however, understandings of sustainability vary greatly.
The need to better understand what is meant by the economic sustainability of development interventions is made clear in one of the rare articles that tackle the issue. Kremer and Miguel (2007), in a paper entitled, The Illusion of Sustainability examine approaches to deworming for their ‘effectiveness’ and, having demonstrated that free distribution of deworming drugs resulted in fewer infections than other approaches including financial contributions by recipients, education programmes and individual mobilisation, the authors conclude that:
More generally, it is probably an illusion to think that a onetime infusion of external assistance will lead to the indefinitely sustainable voluntary provision of most local public goods (Kremer and Miguel, 2007; 1011)
There are numerous problems with the study and the conclusions extracted from it. Firstly, the construction of sustainability that the paper aims to dismiss is a simple one of direct donor input triggering lasting change. They do not address sustainability as the legacy from a development programme of a process through which change occurs, as explored in remainder of this paper. Externally delivered and paid-for training programmes do not have at their core a logic which envisages a permanent change in the way the system functions to realise the greatest poverty impact.
The timeframe for the transmission of information was also short and, in being constructed in this way, many of the positive externalities which develop over time as the result of an intervention may have been missed. Further, the study fails to consider the broader system within which these goods and services are provided, which could have significant impacts on sustainability, considering as they do, just a single outcome variable. For example, in the training interventions the paper addresses, no consideration is made of who delivers the training, the impacts on incomes and the externalities and possible creations or distortions of interrelated markets.
The study’s principle conclusion is that:
“[T]here may simply be no alternative to ongoing subsidies financed by tax revenue raised either from local or national governments, or international donors”.
If one perceives of sustainability as a permanent increase in adaptability, however, then, despite the author’s insistence that this demonstrates the ‘illusion of sustainability’, this is a situation which represents the ultimate goal of a development programme with objectives of sustainability.
This is symptomatic of how a failure to clearly define sustainability can lead to inaccurate conclusions being drawn, hence, three different interpretations of development are examined here i) sustainability as affordability; ii) sustainability as asset transfer, and; iii) sustainability as a permanent increase in adaptability.
As clichéd as it may be, the hackneyed example of ‘giving a man a fish’ will be utilised owing to people’s familiarity with the concept, which will allow for better communication of the subtleties of the definitional differences. The stylised example will be utilised to show how perceptions of sustainability can affect developmental outcomes substantially.
Sustainability as Affordability
This first definition of sustainability is the simplest; that which is affordable is sustainable. Many donor programmes use the language of sustainability to assess the relative merits of programmes by their financial cost i.e. the sustainability of donor finance to the project, given finite resources. Evidently, in such assessments, cheaper is equivalent to better. More developed conceptions of this type begin to examine returns on investment i.e. the impact on poverty relative to the financial input from the donor, often referred to as ‘value for money’, as an example of the new public management system that has begun to dominate the public sectors in many major donor countries in the last decade (Pollock et al., 2002; Stoker, 2006; Nisar, 2007; Eyben, 2012). This conception implicitly assumes a finite number of people living in poverty and a consistent supply of donor finance.
The fundamental principles of this approach do not necessarily envisage a future without aid. As countries develop economically, levels of aid may shift and some countries may be introduced as recipients while others stop receiving aid. Proponents of this approach would not necessarily see giving a man a fish as being unsustainable, provided that there was a reliable source of fish that the donor’s current level of financial support could provide.
Sustainability as Asset Transfer
This second conception of the economic sustainability of development programmes aims to prioritise programmes where assets that have been transferred continue to exist once donor support ceased. Assets, here, refers to both physical assets, such as vehicles, buildings or infrastructure, and intangible assets, such as knowledge or skills transfer through capacity building initiatives.
In contrast to the previous conception, it is not possible for the donation of food or money to people to be considered sustainable. While sustainability as affordability does not necessarily mean the direct delivery of goods and services, they could be included under its definition.
The range of activities that might be engaged in through the asset transfer conception of sustainability vary greatly in both their longevity and utility. Some, for example, would see the donation of a tractor as sustainable; once the initial investment has been made, no further donor input will be required and the tractor continues to exist. Whether the recipients have the knowledge or skills to maintain it or the fuel to power it are, of course, additional considerations.
At the other end of the scale a market analysis may identify the key constraint on the growth of an industry as being the absence of trained horticulturalists, for example. The donor may therefore contract a team of consultants travel to the country in question to train a range of horticulturalists. Once funding ceased and the consultants have left the country, the horticulturalists would remain trained and should help the industry to grow. Proponents of this approach would therefore see the intervention as sustainable.
Some of the flaws of this approach can be seen in this extract from a review of Swedish bi-lateral aid to Tanzania.
Donors, including Sweden, favoured the support of investments and building up organisations and structures, rather than support for operations and maintenance. Thus from the recipient organisation side, the investment phase was “free” while the operation and maintenance phase was costly. From the recipient side it made more sense to let a road, power plant, a school deteriorate than to maintain the existing one with domestic resources (Lindahi and Catterson, 2005; 146)
Firstly, the fact that an activity is ‘free’ to the recipient can, in some circumstances, distort local markets and lead to an undervaluing of the good or service provided. Secondly, perverse incentives are created that actually detract from the sustainability of previous development interventions. With donors more willing to fund capital costs than recurring costs, there is no incentive for national governments to maintain a previous investment.
The paradigm of ‘sustainable rural livelihoods’ is conceptually far closer to incorporating elements of resilience and adaptability beyond simple asset transfer (Chambers and Conway, 1992). However, when applied practically the sustainable rural livelihoods approach is characteristic of the conception of sustainability as asset transfer. Sustainability is taken as a snapshot of the asset profile of an individual or household, without a consideration of the broader system within which that individual or household and their assets exist. Put more simply, no consideration is given to the relationship between current assets and their future value.
The sustainability of a livelihood can be linked with its net assets. Of these, tangible assets are easier to identify and estimate. A useful and useable indicator of vulnerability and security, may be the net position of a household, defined as the value of its realisable tangible assets less liabilities such as debts (Chambers and Conway, ibid ; 20)
The absence of a consideration of how assets might be sustained, let alone the means through which further assets might be produced demonstrates a key failing in this conception of sustainability.
To return to the fish example, those who see sustainable development as the continuation of interventions beyond donor input would not view ‘giving a man a fish’ as sustainable. Giving a man fishing equipment, however, or training in more effective fishing methods or the provision of some kind of storage facility to account for fluctuations in the number of fish caught (insulation from asymmetric shocks), would be viewed as sustainable.
Sustainability as a Permanent Increase in Adaptability
This final conception of sustainability takes a more overarching view of change and the role of ‘development’ within it. Fundamental to understanding sustainability in these terms is the concept of a system. Inequality is created and maintained through a system, or rather a series of interconnected systems. For a change to be considered sustainable under this conception of sustainability not only does the change have to persist beyond the period of outside engagement but the system through which that change was produced must also alter so that the overall system has the capacity to adapt to continue to produce positive developmental impacts for the benefit of poor people.
In reference to the capacity of donor interventions to generate community level institutions, Kremer and Miguel (2007; 1009) recognise the limits of donor interventions in creating the correct incentives for these institutions to continue in their absence. This is one of the principle differences between understanding sustainability as a permanent increase in adaptability and other conceptions of economic sustainability, questioning why a change would persist in the absence of outside intervention and what the incentives are for this to happen.
To return once again to the fish analogy, this conception of sustainability would not view giving a man a fish or giving a man the means to catch his own fish as sustainable – if the fishing rod were to break, how would the man replace it? Is there the infrastructure in place to provide a reliable supply of replacement parts and inputs, such as fishing line?
While the systemic constraints of every sector in every place differ, it might be the case that government import duties are too high to allow the import of affordable manufactured equipment for supply to poor people. In this case a development programme might engage with government or preferably with local trade organisations such as chambers of commerce who would in turn engage with government, in order to bring about policy change. It might be the case that there is a lack of micro-credit facilities to allow poor people to buy the equipment which may constitute significant initial expenditure but which may be repaid through the additional income of selling surplus fish caught using the new equipment. Where these low levels of capital are not a key constraint, supply might be an issue, where manufacturers and retailers focus on urban areas, limiting poor people’s access to the market. In such cases the role of a development programme may be conducting research or working with a manufacturer to demonstrate the potential of low-income markets, potentially reconfiguring their offer to cater better to poorer people. These are just a small number of myriad ways that this particular development issue might be addressed in different contexts but in each case, the change brought about by the intervention proposed is one that will continue and adapt in the absence of external involvement.
There are those that contend that no solution is sustainable in situations of extreme poverty and, indeed, no proponents of a systemic understanding of sustainability would claim that a permanent increase in adaptability will result from every intervention. One would not attempt to teach a drowning man to swim let alone alter the state incentives for schools to offer swimming lessons as a public good to minimise the future need for emergency services. However, often, systemic change principles are more applicable than one might immediately assume.
Once this clause is highlighted there is a tendency for every donor, NGO, or programme to argue that their particular issue in their particular context constitutes the case of the drowning man, which can have a pernicious effect on the outcomes for sustainability. Once ‘relief’ and ‘development’ are dichotomised in such a way, the potential for more sustainability in relief is removed.
The US-based NGO Mercy Corps, whose remit is to work exclusively in crisis or conflict situations, recognised the unhelpful nature of this divide and have begun to work in less direct ways through partners in the private and public sector, where possible, to increase the sustainability of the change which they affect (Mercy Corps, 2013). This concept is documented by Hitchins et al. (2004) who characterise this not as a dichotomy but as a “spectrum of economic weakness” with a “viability void” on one side, where relief is more appropriate, to an enabling environment on the other, where there are greater opportunities for sustainable innovations.
Sustainability under this conception of the term commonly involves both public and private sector actors. In many cases, it is a question of the capacity of institutions, local, national or transnational, to perform functions adequately, and the incentives they have to do so. Many functions cannot be performed adequately by the private sector actors but it is a question of which level of institution has the capacity, remit, or responsibility to intervene. Indeed, in the case of deworming drugs discussed by Kremer and Miguel (2007), if the local or state government can provide sufficient positive externalities through the free provision of deworming drugs in the form of a healthy workforce whose additional tax revenues pay for the treatment then this is in fact the very definition of a sustainable solution. This is undoubtedly an oversimplification of a complex issue and it is far more likely that political decisions at a local and national level have to be taken as to what spending priorities are, even if there is a positive cost to the provision of the treatment once all externalities have been considered. From a donor perspective, however, development as a concept cannot be the same as charity. The purpose of development is not to replace social welfare but to leverage investments made to improve the ability of poor people to meet their own needs and, therefore, reduce the need for social welfare.
Interestingly, this interpretation of sustainability has considerable implications for the perspective of sustainability as affordability. Based on an evaluation of Swedish aid to Tanzania, Lindahi and Catterson conclude that:
...the available financial resources for aid were greater than what could be disbursed in a prudent manner in worthwhile projects. Under such circumstances there were hardly any incentives for the desk officer or the project manager to use resources efficiently. Likewise, the recipient organisation had no incentive to argue for prudent use of resources, such as an early phase-out of Swedish assistance, as this would mean use of scarce government funds instead of free donor funds (145)
Conceiving of sustainability in this way invokes thinking around the industry of aid or development as a business. However one conceives of sustainability there are few incentives for any of the actors involved at the levels of policy, design, implementation, evaluation or research around aid to bring about sustainable change, as is documented extensively elsewhere (Svensson, 2000; Paul, 2006; Van Brabant, 2010; Williamson, 2010; Font et al., 2012). Rent-seeking behaviours are evident across the aid industry and while there is a clear recognition of the importance of ‘sustainability’ the ill-defined nature of the concept allows those with incentives to do so to perpetuate this behaviour. By conceiving of sustainability as a permanent increase in adaptability the incentive structure is changed, provided the principle of sustainability being desirable remains intact. Programmes assessed by these criteria must be designed so as to deliver this change and those that are successful in doing so will be rewarded accordingly.
Ultimately, the perception of sustainability as a permanent increase in adaptability is the only approach that can lead to long term growth, independent of outside involvement. The global financial crisis has led to public sector cuts which have seen many country’s cut aid budgets; an economy, and the livelihoods of the poor people within it, cannot be dependent on the external whims of a foreign government, making the perception of sustainability as affordability a precarious and vulnerable position. For both the perception of sustainability as adaptability and, to a lesser extent, the environmental perspectives on sustainability, the reality is that the world is a complex and dynamic place. Climate, markets and governments amongst a plethora of other dimensions change, and a one-off involvement that does not leave behind the capacity to adapt to these changes is doomed to failure in the long term.
From an environmental perspective, multiple studies have shown that the capacity to adapt to climatic changes in terms of impact on growth, amongst other things, is far lower amongst less developed countries (Dell et al., 2008; Dell et al., 2009; Noy, 2009; Raddatz, 2009). The perception of sustainability as a permanent increase in adaptability is the only way in which development can contribute to the building of complex adaptive systems and conceiving of sustainability in other ways has the potential to negatively impact on poor people as documented in the concluding section.
Consequences of Interpretations and Concluding Remarks
The issues raised by this co-optation of the term ‘sustainability’ by multiple development academics, policy-makers, and practitioners, each with their own distinct set of priorities, has had consequences that reach far beyond semantics. Sustainability is now almost universal in the terms of reference for development programmes from a wide range of donors (see various USAID, DfID, UN, IFAD and AUSaid programmes for examples). However, as outlined above, interpretations of the term vary between donors, between programmes, and amongst personnel within donors.
A programme whose primary objective is poverty alleviation, as it is either directly or indirectly with the vast majority of programmes, is now likely to be tasked with sustainability (often phrased as ‘green growth’ in a contemporary setting under environmental conceptions of sustainability) as a secondary or parallel objective. While programmes, and their designers, utilising market systems development frameworks might interpret this as the likelihood of benefits persisting beyond the period of donor intervention, other departments or individuals within the donor organisation or evaluator might interpret this as a requirement that interventions are climate neutral, or have a secure source of donor funding.
Poor people in recipient countries are often negatively impacted by these different interpretations of sustainability. As included in the earlier extract, where the incentives are in favour of building new infrastructure rather than maintaining the existing infrastructure, access becomes unreliable and displacement of people from homes and land is increased. Moreover, where temporary solutions are introduced to address a problem, markets are distorted and poor people lose the opportunity to develop sustainable solutions to improve their lives. Very few people in the world are entirely destitute. Giving every man a fish denies the fisherman who catches an extra fish the chance to trade with the farmer who has a higher maize yield one season. Take this to a national level and markets are not created which otherwise would have been. Markets may be ‘thin’ but they exist and the distortion that some interpretations of sustainability necessitate can have negative consequences for poor people.
From an environmental perspective consider, as an example, a programme, the design of which is geared towards increasing the use of fertiliser by poor farmers in order to increase yields and subsequently increase incomes. They might work through a local producer of fertiliser to create a product geared more appropriately to poor consumers with little access to credit. Despite achieving these goals successfully and helping to raise the incomes of hundreds of thousands of people, the programme might be deemed a failure for having increased the use of chemical fertiliser rather than organic fertiliser. Similarly, a programme which intervenes in a system in a number of ways so as to grow a particular export market from a poor country and improve the position of poor people within that system, might be criticised, by those who interpret sustainability from an environmental perspective, for the increase carbon emissions that exports are creating.
Sustainability in development, then, must be re-evaluated, so that the long-term interests of poor people are prioritised. This entails an appraisal of the most effective way to ensure that changes made to poor people’s capacity to address their needs is carried out by donors, rather than employing conceptions that serve domestic political, individual or firm-level goals. Conceiving of sustainability as a permanent increase adaptability is the only way to ensure that development programmes’ objectives are aligned to the achievement of lasting pro-poor change.
References
ADAMS, W. M. The future of sustainability: Re-thinking environment and development in the twenty-first century. In: IUCN, ed. Report of the IUCN renowned thinkers meeting, 29-31 January 2006.
ÅHMAN, H. 2013. Social sustainability–society at the intersection of development and maintenance. Local Environment, 1-14.
ANAND, S. & SEN, A. 2000. Human development and economic sustainability. World development, 28, 2029-2049.
BEST, R., FERRIS, S. & SCHIAVONE, A. Beyond Agriculture: Making markets work for the poor Theme 1: Building linkages and enhancing trust between small-scale rural producers, buyers in growing markets and suppliers of critical inputs. 2005. NRI/ITDG conference. Chatham, UK.
BROWN, D., SEYMOUR, F. & PESKETT, L. 2008. How do we achieve REDD co-benefits and avoid doing harm. Moving ahead with REDD: issues, options and implications, 107-118.
BRUNDTLAND, G. H. 1987. Our common future, Oxford University Press Oxford.
BURRA, S. & MAHADEVAN, D. 2005. Making Markets Work for the Poor: The Small Investors' Fund. Economic and Political Weekly, 40, 3245-3249.
CARPENTER, G. 2003. Making markets work for clean water. Water Science & Technology, 47, 97-102.
CATTERSON, J. & LINDAHL, C. 1999. The sustainability enigma: aid dependency and the phasing out of projects: the case of Swedish aid. In: EXPERT GROUP ON DEVELOPMENT ISSUES (ed.).
CHAMBERS, R. 1990. Rural development: putting the last first, CTA.
CHAMBERS, R. & CONWAY, G. 1992. Sustainable rural livelihoods: practical concepts for the 21st century. IDS Discussion Paper. Brighton: Institute of Development Studies.
COLANTONIO, A. 2009. Social sustainability: linking research to policy and practice.
DELL, M., JONES, B. F. & OLKEN, B. A. 2008. Climate change and economic growth: Evidence from the last half century. NBER Working Paper Series. National Bureau of Economic Research.
DELL, M., JONES, B. F. & OLKEN, B. A. 2009. Temperature and income: reconciling new cross-sectional and panel estimates. National Bureau of Economic Research.
DERCON, S. 2012. Is green growth good for the poor? In: WORLD BANK (ed.) Policy Research Working Paper. Washington: World Bank.
DFID & SDC 2008. The Operational Guide for the Making Markets Work for the Poor (M4P) Approach. In: SDC & DFID (ed.).
DWYER, D. J. 1977. Economic development: Development for whom? Geography, 325-334.
EASTERLY, W. 2008. Reinventing foreign aid, Boston, The MIT Press.
ELLIOT, D., GIBSON, A. & HITCHINS, R. 2008. Making markets work for the poor: rationale and practice. Enterprise Development and Microfinance, 19, 101-119.
EYBEN, R. 2012. Relationships for aid, London, Routledge.
FONT, X., GOODWIN, H. & WALTON, R. 2012. Donor funded tourism projects: factors for success. In: TOURISM, I. C. F. R. (ed.) ICRT Occasional Paper. ICRT.
FOWLER, A. 2000. NGDOs as a moment in history: beyond aid to social entrepreneurship or civic innovation? Third world quarterly, 21, 637-654.
HIRSCHMAN, A. O. 1988. The strategy of economic development, Westview Press.
HITCHINS, R., ELLIOTT, D. & GIBSON, A. 2004. Making business service markets work for the rural poor–a review of experience. Small Enterprise Development, 16, 10-23.
HORNBORG, A. 2003. Cornucopia or zero-sum game? The epistemology of sustainability. Journal of world-systems research, 9, 205-16.
KIDD, C. V. 1992. The evolution of sustainability. Journal of Agricultural and Environmental Ethics, 5, 1-26.
KONING, J. Social sustainability in a globalizing world: context, theory and methodology explored. More on MOST, 2001 The Hague,. National UNESCO Commission.
KREMER, M. & MIGUEL, E. 2007. The illusion of sustainability. The Quarterly Journal of Economics, 122, 1007-1065.
LELE, S. M. 1991. SUSTAINABLE DEVELOPMENT - A CRITICAL-REVIEW. World Development, 19, 607-621.
LINDAHI, C. & CATTERSON, J. 2005. What Causes Aid Dependency? Evaluating Thirty Years of Swedish Bilateral Aid to Tanzania1. Evaluating Development Effectiveness, 7, 133.
MERCY CORPS. 2013. Private Sector Engagement [Online]. Available: http://www.mercycorps.org.uk/research-resources/private-sector-engagement [Accessed 07/08/2015]
MIEHLBRADT, A. O., MCVAY, M. & TANBURN, J. 2005. From BDS to making markets work for the poor: The 2005 Reader, International labour organization (ILO). International training centre.
MOSS, T., PETTERSSON, G. & VAN DE WALLE, N. 2006. An aid-institutions paradox? A review essay on aid dependency and state building in sub-Saharan Africa. Center for Global Development working paper, 11-05.
MOYO, D. 2009. Dead aid: Why aid is not working and how there is a better way for Africa, New York, Macmillan.
NISAR, T. M. 2007. Value for money drivers in public private partnership schemes. International Journal of Public Sector Management, 20, 147-156.
NOY, I. 2009. The macroeconomic consequences of disasters. Journal of Development Economics, 88, 221-231.
PAUL, E. 2006. A survey of the theoretical economic literature on foreign aid. Asian‐Pacific Economic Literature, 20, 1-17.
POLLOCK, A. M., SHAOUL, J. & VICKERS, N. 2002. Private finance and “value for money” in NHS hospitals: a policy in search of a rationale? BMJ: British Medical Journal, 324, 1205.
PORTEOUS, D. 2005. The access frontier as an approach and tool in making markets work for the poor. In: DFID (ed.) Newsletter.
RADDATZ, C. 2009. The wrath of God: macroeconomic costs of natural disasters. In: WORLD BANK (ed.) Policy Research Working Paper. Washington.
ROGERSON, A. 2011. What if development aid were truly “catalytic”? Background Note. London: ODI.
SOLOW, R. M. 1974. The economics of resources or the resources of economics. The American Economic Review, 64, 1-14.
STOKER, G. 2006. Public Value Management A New Narrative for Networked Governance? The American review of public administration, 36, 41-57.
SVENSSON, J. 2000. Foreign aid and rent-seeking. Journal of International Economics, 51, 437-461.
UVIN, P. 2002. The development/peacebuilding nexus: a typology and history of changing paradigms. Journal of Peacebuilding & Development, 1, 5-24.
VAN BRABANT, K. Managing aid agency security in an evolving world: The larger challenge. November. EISF Article Series. London, UK: European Interagency Security Forum, 2010.
WILLIAMSON, C. R. 2010. Exploring the failure of foreign aid: The role of incentives and information. The review of Austrian economics, 23, 17-33.
YORK, R., ROSA, E. A. & DIETZ, T. 2010. Ecological modernization theory: theoretical and empirical challenges. In: REDCLIFT, M. & WOODGATE, G. (eds.) The International Handbook of Environmental Sociology. New York: Edward Elgar.
Comments