New approaches to agriculture are required if we are to reduce the environmental impacts of farming while also feeding more people with a sufficient quantity and diversity of nutritious and safe foods.
This building block explains the concept of sustainable intensification.
Last update: 18 June, 2018
Sustainable intensification (SI): is a recently developed concept that is understood in different ways by its critics and supporters. A common understanding is that it denotes the principle of increasing or maintaining the productivity of agriculture on existing farmland while at the same time, reducing its environmental impacts. Understood in this way, SI designates a goal for the development of agricultural systems but does not, a priori, favour any particular agronomic route to achieve it. It may involve the intensification of different types of agricultural inputs (e.g. of knowledge, biotechnologies, labour, machinery) and apply these to different forms of agriculture (e.g. livestock or arable; agroecological or conventional). Forms of intensification that can be called sustainable intensification must lower environmental impacts and land use, relative to yields. However, for some, to merit the term ‘sustainable’ social, economic, and ethical criteria must also be considered.
Agricultural Intensification: is the process of intensifying the input of agricultural resources (e.g. seeds, labour, fertilisers, pesticides, technologies, knowledge) to increase the level of yield per unit of farmland or livestock. Agricultural intensification is not always clearly nor consistently defined and is often confused with the term intensive agriculture. Unlike intensive agriculture, which could be seen as a specific system of agronomy, agricultural intensification is a general process that can apply, in principle, to any type of agricultural production. Examples of agricultural intensification may range from using new pesticides in intensive agriculture to intensifying the use of indigenous and context specific knowledge in local farming practices. Although agricultural intensification can take many forms, it always involves the intensification of some types of agricultural input with a view to increasing yields.
Intensive arable agriculture (IAA): is often used synonymously with the term industrial agriculture and conventional farming. IA is generally used to denote farming systems that use modern technologies and economies of scale to maximise yields relative to land use and production costs (e.g. costs of labour, technology, seeds, fertilisers, and pesticides). IA is associated with homogeneous landscapes and large fields with low crop-diversity, and high use of chemical fertilisers, agrochemicals, and irrigation. This combination of agricultural technologies became common following the Green Revolution in the mid-20th century. While IA aims to increase agricultural efficiency and so as a side-effect reduces environmental impacts per unit of output, due to its often-large scale, it can result in a concentration of environmental impacts at the local scale.
Ecological intensification (EI): is the principle of using the natural functionalities of an ecosystem to produce greater amounts of food, fibre, and fuel in sustainable ways. Underpinning EI is the idea that ecological functions (e.g. pollination and predator/prey relationships) can be integrated into agricultural practices, ideally leading to ‘agroecosystems’ that are sustained by natural processes and avoid many negative environmental impacts. Ecological intensification is closely related to the concepts of sustainable intensification and climate smart agriculture, but differs in its strong focus on the potential of enhancing ecological processes in food production.
Climate smart agriculture (CSA): often discussed in the context of low-income countries, CSA was first introduced by the FAO in 2010 as an integrated approach geared at reorienting and redesigning agricultural systems to address and build resilience to climate change. CSA involves three interconnected elements: increasing agricultural productivity and incomes; adapting and building resilience to climate change; and the mitigation of greenhouse gas emissions. It aims to identify context specific agricultural strategies supporting these elements and guide coordinated actions among stakeholders (e.g. farmers, researchers, private sector, civil society and policy makers) from the farm to the global level. CSA is criticised for justifying nearly any form of agriculture (thereby ‘greenwashing’ unsustainable practices) and for failing to address enduring inequalities in food production and distribution. CSA is closely related to the concepts of sustainable intensification and ecological intensification but differs from them in its strong focus on planning and implementation for climate change adaptation and mitigation, and less on reducing environmental impacts beyond emissions.
Agroecology (as a practice): agroecology can be defined as a range of agricultural practices that are based on applying ecological concepts and principles to optimize interactions between plants, animals, humans, and the environment. Agroecology also places strong emphasis on the social and ethical aspects of food production. Its advocates tend to have a preference for organic practices (e.g. the avoidance of mineral fertilisers and chemical inputs, and instead prefer the use of biofertilisers, natural pesticides and crop rotation), it also emphasises the need for a ‘multifunctional’ farm system to produce both food and non-food outputs, and for smallholder and indigenous, as opposed to large scale farming. Agroecology has been interpreted in different ways: it also refers to a social movement and field of science.
Food, biofuel and fibre production are major contributors to climate change, resource use, and the destruction of biodiverse ecosystems and the services they provide. It is essential that agriculture’s environmental impacts are reduced, but this cannot be achieved in isolation from the need to ensure food security (see building block on food security) for a growing global population. Billions of people worldwide suffer from various forms of malnutrition (see building block on malnutrition), while the average diet of a growing and urbanising world population is becoming more resource intensive.
Sustainable intensification (SI) has been suggested by some as one contribution to reconciling the need for more environmentally benign agriculture while advancing global food security. It denotes the linked goals of maintaining or increasing the productivity of existing farmland, while reducing the environmental impacts of agriculture. SI will need to be accompanied by other efforts, including those that address inequitable food distribution, unsustainable consumption patterns, and excessive food waste (see Figure 1)1-2.
SI has evolved alongside closely related concepts, including agroecology, climate smart agriculture, and ecological intensification3–5. These concepts try to clarify priorities and guide efforts for the sustainable development of agriculture. Addressing similar topics from slightly different angles, both SI and these other related concepts have been variously debated, endorsed, and rejected by different stakeholders.
SI is a fairly new and still evolving concept. The concept originated in the context of efforts to increase the productivity of smallholder agriculture in African countries during the 1990s6. More recently, SI has been adopted by governments, agribusinesses and international development organisations (including the FAO and the World Bank) and has been used to denote a general guiding principle for the development of agriculture7.
SI was defined in 2009 by the UK’s Royal Society as an aspirational approach to agricultural production wherein “yields are increased without adverse environmental impact and without the cultivation of more land”8. This commonly used definition describes a goal and guideline for the development of agriculture, but leaves open how (i.e. using which farming methods) SI could be achieved.
Different interpretations of sustainable intensification can be found and the concept has been used in very different, sometimes conflicting ways, from an (alleged) vindication of business-as-usual farming practices, to a call to radically redefine current systems of agricultural production7,9. Common criticisms include that sustainable intensification is greenwash, ‘oxymoronic’ or too vague to be useful5,7,10. The looseness of the concept and its perceived association with particular stakeholders or ideologies also means that it has been endorsed by some stakeholders and rejected by others.
Underpinning the concept of sustainable intensification as it is commonly used by academics, and reflected in the Royal Society’s definition, are three important and widely accepted principles for the sustainable development of agriculture as follows3:
Most of the land potentially available for conversion is currently forest, wetland, or grassland. Converting these lands nearly always results in substantial releases of greenhouse gases, threatens a considerable portion of the world’s terrestrial biodiversity, and can disrupt existing ecosystem services (e.g. flood and drought prevention)3,11,12.
A core principle of sustainable intensification is to confine food production to existing farmland, which in the context of a growing global population requires continuous improvements in yield in regions of the world where there is currently a yield gap (see below). In this sense, sustainable intensification is a strategy for land sparing at global and regional levels (see our building block on the land sparing-sharing continuum).
Many farming techniques that were introduced during the Green Revolution and which have now become mainstream, entail high inputs of synthetic chemical fertilisers, pesticides, tillage, and irrigation that have profound environmental impacts, and which can potentially undermine future food production3.
Runoff from fertilisers, for example, can pollute natural habitats and lead to the eutrophication of surface waters12. In addition, pesticides may harm ecosystems and accumulate in food chains, while high levels of water extraction for irrigation can impact on aquatic ecosystems and limit water availability for other purposes (e.g. domestic use)12,13.
Sustainable intensification aspires to intensify the productivity of agricultural land, while reducing harmful resource inputs and any resulting environmental impacts of agriculture to an absolute minimum.
More controversial is SI’s call to increase yields. While it is often argued that global agricultural yields need to increase in order to meet a growing world population’s need for food, critics point out there is currently enough food to feed everyone, and yet people still go hungry. Food insecurity can thus be seen as a failure of socio-economic access to safe and nutritious food, rather than as a simple consequence of insufficient food supply3.
If and to what extent an increase in global food production will be required also depends on the extent to which issues with distribution, demand and waste as well as population growth are addressed3. Rather than reaching predefined global production levels, SI therefore aims to increase the productivity of existing farmland where this is possible: increasing outputs (yields) relative to agricultural inputs (e.g. water, energy, land) and environmental impacts (e.g. greenhouse gas emissions and water pollution)3. Its productivity potential also needs to be secured and enhanced through, for example, a focus on building or restoring good quality soils and natural capital.
In addition, ensuring SI’s sustainability aspect may mean that in some areas yields or yield gains are sacrificed in exchange for better environmental outcomes14. SI may require limiting intensification or even de-intensifying where increasing yields causes unacceptable environmental damages. Some would also argue that in order to become truly ‘sustainable’ in the broadest sense of the word (i.e. a sense that encompasses social, economic and ethical concerns such as smallholder livelihoods or animal welfare), intensification may also need to be limited or reversed in some contexts.
There is disagreement about what types of agricultural practices constitute SI. For instance, it is common for agri-businesses to frame SI as denoting business-as-usual industrial farming, including incremental improvements in environmental impacts resulting from more efficient modes of production. However, many argue that this will be insufficiently impactful to satisfy the three principles outlined above, which broadly describe the parameters of SI, and to align the concept with the twin goals of achieving food security (across scales) within the necessary environmental and social constraints of a sustainable food system (see Figure 2)14.
Both food security and food system sustainability each come with their own complexities. Achieving SI therefore requires that a range of complex topics from debates on food security and food system sustainability are balanced and reconciled as best as possible (see Figure 2)3,14:
Agricultural techniques. A first question to consider is what types of agricultural techniques SI involves. Sustainable intensification does not a priori include or exclude a range of agricultural techniques3. It could, amongst others, incorporate techniques drawn from biotechnology (e.g. genetic modification), precision farming (e.g. robotics and big data to improve the timing and spatial allocation of water and nutrients), agroecology (e.g. intercropping) and organic farming (e.g. closing nutrient loops via the integration of crop and livestock farming)14. To reach the aims of increasing yields and lowering environmental impacts, SI will need to incorporate ideas from different agricultural approaches and apply them in ways that fit different local contexts.
Types of food. What types of food need to be produced to foster food security and lower environmental impacts in local contexts? Food security requires not just the supply of any type of food, but rather that people have access to a sufficient, safe and diverse range of nutritious foods that satisfy a healthy diet (see building block on food security). Different approaches to agriculture may, for example, influence the diversity and affordability of foods available at local markets. At the same time, these foods will need to be produced in ways that minimise environmental impacts: increasing the production of resource intensive foods (e.g. meat and dairy products) or of crops grown via soil-depleting methods may not lead to improved environmental performances and may even undermine future generations’ access to sufficient amounts of safe and nutritionally adequate food.
Yields and/or the environment. How should decisions be made when there are trade-offs between yields and environmental impacts? Under what conditions and in which contexts must yields or yield gains be sacrificed for environmental outcomes? SI could, for example, involve intensification in some areas and deintensification in others. It may be desirable to take some habitats critical for biodiversity as well as lands that are not agriculturally productive completely out of agriculture14. Equally, significant yield increases may not need to come from further intensifying already intensified agriculture, but could particularly result from the sustainable intensification of farmland that is below its current yield potential16. Accordingly, to achieve both its sustainability and intensification aspects, SI will require different actions depending on local contexts and the current statuses of agricultural systems in different regions of the world.
Livelihoods and rural economies. In many countries, rural economies are responsible for a major part of agricultural production4. In some of these contexts, the concern is that some methods of SI may favour large national and international corporations by the techniques and inputs (e.g. seeds, fertilisers, technologies, knowledge) they require. Approaches to sustainable intensification will need to be available to and affordable by smallholder farmers in order to support and enhance their livelihoods and food security17.
Scale levels. The principle of sustainable intensification can be addressed at different scales, ranging from the farm, to the regional and global level. There can be differences between the types of actions that are required to balance and reconcile the goals of food security and food system sustainability at these different levels. This may, for example, influence how trade-offs will be made between global environmental goals, and regional environmental impacts and food security. To manage these trade-offs, SI needs to be embedded within broader governance frameworks that are geared at optimising food security and food system sustainability across different scales in ethical ways.
Animal health and welfare. Sustainable intensification has its origins in crop production, but has also sparked controversy on animal health and welfare when applied to livestock farming3. Some approaches to SI may improve productivity and animal welfare simultaneously (e.g. good veterinary care and more nutritious feeding). In other cases, however, the goal of increasing productivity may be incompatible with improving animal welfare. Which trade-offs between these two goals will still count as being sustainable intensification? The idea of SI will need to consider these conflicting ethical viewpoints: where some will see ‘good’ animal welfare as a non-negotiable precondition to any increase in productivity, others may value productivity and the benefits this brings to humans over animal welfare.
There are currently no clear-cut answers to these major questions and many more relating to SI. However, in the pursuit of SI, and in order to achieve the twin aims of food security and food system sustainability, it will be necessary to continuously engage with them. It is likely that different answers will apply to different contexts and at different scales, resulting in a patchwork of approaches and trade-offs; operating within broader governance frameworks (such as climate and biodiversity conventions and legislation) that set limits and shape decision making on what forms of agricultural intensification are deemed sustainable, in what context.
To learn more about this topic we recommend:
Literature review (open access): Conceptualising Fields of Action for Sustainable Intensification
Literature review (open access): Sustainable Intensification – “Oxymoron” or “third-way”?
FCRN report (open access): Sustainable intensification in agriculture
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2. Smith, P. Delivering food security without increasing pressure on land. Global Food Security 2, 18–23 (2013).
3. Garnett, T. & Godfray, H. C. J. Sustainable intensification in agriculture. Navigating a course through competing food system priorities. (Food Climate Research Network and the Oxford Martin Programme on the Future of Food, University of Oxford, 2012).
4. Campbell, B. M., Thornton, P., Zougmoré, R., van Asten, P. & Lipper, L. Sustainable intensification: What is its role in climate smart agriculture? Current Opinion in Environmental Sustainability 8, 39–43 (2014).
5. Tittonell, P. Ecological intensification of agriculture—sustainable by nature. Current Opinion in Environmental Sustainability 8, 53–61 (2014).
6. Pretty, J. N. The sustainable intensification of agriculture. Natural Resources Forum 21, 247–256 (1997).
7. Mahon, N., Crute, I., Simmons, E. & Islam, M. M. Sustainable intensification – “oxymoron” or “third-way”? A systematic review. Ecological Indicators 74, 73–97 (2017).
8. The Royal Society. Reaping the benefits: science and the sustainable intensification of global agriculture. (The Royal Society, 2009).
9. Levidow, L. European transitions towards a corporate-environmental food regime: Agroecological incorporation or contestation? Journal of Rural Studies 40, 76–89 (2015).
10. Weltin, M. et al. Conceptualising fields of action for sustainable intensification – A systematic literature review and application to regional case studies. Agriculture, Ecosystems & Environment 257, 68–80 (2018).
11. Bellarby, J., Foereid, B. & Hastings, A. Cool Farming: Climate impacts of agriculture and mitigation potential. (Greenpeace, 2008).
12. Tilman, D., Cassman, K. G., Matson, P. A., Naylor, R. & Polasky, S. Agricultural sustainability and intensive production practices. Nature (2002). doi:10.1038/nature01014
13. Burney, J. A., Davis, S. J. & Lobell, D. B. Greenhouse gas mitigation by agricultural intensification. Proceedings of the national Academy of Sciences 107, 12052–12057 (2010).
14. Godfray, H. C. J. & Garnett, T. Food security and sustainable intensification. Phil. Trans. R. Soc. B 369, 20120273 (2014).
15. FCRN. Sustainable Intensification, Food System Sustainability and Food Security. (2018).
16. Garnett, T. et al. Sustainable Intensification in Agriculture: Premises and Policies. Science 341, 33–34 (2013).
17. Tscharntke, T. et al. Global food security, biodiversity conservation and the future of agricultural intensification. Biological Conservation 151, 53–59 (2012).
Fraanje, W., and Lee-Gammage, S. (2018). What is Sustainable Intensification? (Foodsource: building blocks). Food Climate Research Network, University of Oxford.
Walter Fraanje, Food Climate Research Network, University of Oxford
Samuel Lee-Gammage, Food Climate Research Network, University of Oxford
Tara Garnett, FCRN, University of Oxford
Tim Benton, School of Biology at the University of Leeds and Energy Environment and Resources at Chatham House
Niamh Mahon, School of Animal, Rural and Environmental Sciences, Nottingham Trent University
Meike Weltin, Leibniz Centre for Agricultural Landscape Research (ZALF), Müncheberg, Germany
Reviewing does not constitute an endorsement. Final editorial decisions, including any remaining inaccuracies and errors, are the sole responsibility of the Food Climate Research Network.
The Daniel and Nina Carasso Foundation
The Esmée Fairbairn Foundation