Cah. Agric.
Volume 27, Number 2, Mars-Avril 2018
Les agricultures face au changement climatique. Coordonnateur : Emmanuel Torquebiau
Article Number 26001
Number of page(s) 7
Section Options / Options
Published online 19 March 2018

© E. Torquebiau et al., Published by EDP Sciences 2018

Licence Creative CommonsThis is an Open Access article distributed under the terms of the Creative Commons Attribution License CC-BY-NC (, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

1 Introduction

The Climate-smart agriculture (CSA) concept emerged in 2010 as a response to the imminent threat of climate change. In the original Food and Agriculture Organization (FAO) document (FAO, 2010), the definition of CSA is: “Agriculture that sustainably increases productivity, resilience (adaptation), reduces/removes greenhouse gases (GHG) and enhances achievement of national food security and development goals”. CSA has become known for the so-called “triple win”, i.e., working simultaneously to achieve its three objectives (or pillars): “adaptation, mitigation, and food security”. CSA is also sometimes presented as a mechanism to achieve synergies between the three pillars in a context-specific manner.

CSA aims to contribute to sustainable landscapes and food systems as well as to resilience, ecosystem services, and value chains. It involves a complex set of objectives and multiple transformative transitions for which there are newly identified knowledge gaps related to the performance and conditions of implementing CSA alternatives and measurable outcomes. For some, CSA is not a scientific or technical concept, but rather a “political” concept aiming at better incorporating agriculture in climate negotiations (Fallot, 2016). CSA nevertheless intends to mobilize science to achieve necessary transitions, and requires bridging a diversity of disciplines in agricultural sciences and the environment. Specifically, the use of climate change science data and models by the agricultural research community, such as the Intergovernmental Panel on Climate Change (IPCC) projections, is important (Rosenzweig et al., 2013). A system approach is needed, along with the organization of relevant scientific data and policy that will help to further refine the CSA concept.

The FAO’s original CSA document includes the sub-title: “Policies, Practices and Financing for Food Security, Adaptation and Mitigation”, indicating that CSA lies at the interface between science and policy-making and strives to foster action on the ground and the mobilization of financing. The CSA approach encourages coordinated actions by farmers, researchers, the private sector, civil society and policymakers towards climate-resilient pathways through four main action areas:

  • building evidence;

  • increasing local institutional effectiveness;

  • fostering coherence between climate and agricultural policies;

  • linking climate and agricultural financing (Lipper et al., 2014).

Six years after FAO’s first publication on Climate-smart agriculture, CSA has become a ʻbuzzword’ for many in the agricultural research community as well as among practitioners. There are innumerable websites mentioning CSA. Books and articles focused on CSA are flourishing as well (e.g., Campbell et al., 2014, Lipper et al., 2014, 2017; Harvey et al., 2014; Minang et al., 2015, Torquebiau, 2016, Andrieu et al., 2017). However, there have also been criticisms by some civil society organizations claiming that CSA opens “a new space for promoting agribusiness and industrial agriculture” ( Accessed 13/2/2018) and controversies over the meaning of CSA (Steenwerth et al., 2014). In addition, there are concerns that CSA can be appropriated to support conflicting agendas, such as agroecology or conventional agriculture (Pimbert, 2015).

Has the CSA concept come of age? Are there CSA success stories that match the original CSA definition and achieve the “triple win” (e.g., simultaneous achievement of adaptation, mitigation, and food security)? What does CSA mean today for actual decision-makers such as farmers, companies, and policy-makers at different levels (local, sub-national, national)? How do soil carbon sequestration and the 4 per 1000 Initiative (which has objectives similar to those of CSA) launched at COP 21 integrate into CSA?

To address the above questions and suggest corresponding research topics, the present paper intends to:

  • review achievements and current criticisms of the CSA concept;

  • assess CSA implementation, taking into account particularly the triple-win challenge and synergies or trade-offs between the three CSA objectives;

  • analyze what CSA means for decision-makers;

  • analyze the links between soil carbon sequestration and nitrogen management, and CSA.

2 The conceptual challenge

Since the CSA concept did not arise from the academic community, its underlying concepts were not aligned with existing scientific debates, on e.g., sustainability, food security, resilience, or agroecology. This should not preclude CSA from being analyzed rigorously. The presence of the word “sustainable” in the original CSA definition should indicate that CSA is concerned about the impact of agriculture on future generations, and its environmental, economic, and social implications.

Early texts on CSA by FAO (2010, 2013) and Lipper et al. (2014) showed a progressive shift in meaning from sustainable increase in productivity to food security. However, food security in itself is a complex concept depending on various conditions (access, availability, utilization, stability) which all need to be taken into account (Richardson, 2010). Some authors are consequently using food security indicators such as the Household Food Insecurity Access Scale or Dietary Diversity with indicators of social resilience and CO2 emissions to assess the climate smartness of farming systems (Hammond et al. 2017).

Resilience and resource use efficiency are key guiding principles for CSA, as presented in Lipper et al. (2014). The authors insist that CSA must “emphasize agricultural systems that utilize ecosystem services to support productivity, adaptation, and mitigation”. The term ʻresilience’ is sometimes used interchangeably with ʻadaptation’ in the definition of CSA (Lipper et al., 2017). The ecosystem approach is a dominant aspect of CSA (e.g., niche partitioning, ecological successions, symbiosis), including practices in which those principles play a key role, such as crop diversification, intercropping, rotations, cover crops, agroforestry, biological control of pests and diseases, plant-animal interactions, and the use of agrobiodiversity.

Nevertheless, a detailed analysis of FAO’s reference document on CSA (FAO, 2013) shows that ʻland sparing’ (intensifying in some areas and conserving nature elsewhere; see Grau et al., 2013) is favored, while ʻland sharing’ (combining objectives of production and protection on the same land) is not. This does not make biodiversity and ecosystem services appear as top CSA priorities (Tissier and Grosclaude, 2015). Given that higher cultivation intensity in farmed landscapes has been shown to decrease biodiversity richness and the potential for carbon storage (Renwick et al., 2014), more emphasis could be given to land sharing. A landscape approach to CSA could help to address this weakness, yet this is an under-researched topic (Harvey et al., 2014; Minang et al., 2015).

There is a growing consensus that the “unintended social and environmental consequences” of agriculture need to be addressed (IAASTD, 2009). This consensus has led to greater acceptance of agroecological concepts, which is occurring separately from the CSA debates. Agroecology has been defined differently, ranging from the simple ʻapplication of ecological principles’ to agriculture (Oxford Dictionnaries, 2016) to the ʻintegrative study of the ecology of the entire food system’, encompassing ecological, economic, and social dimensions (FAO, 2015). There are compelling reasons to link agroecology and CSA and to find solutions that address both (Saj et al., 2017). The practices of CSA and agroecology are often one-in-the-same, and can enrich one another.

Agroecology has sometimes been described as being implicitly climate-smart, but is seldom evaluated for its climatic performance. Its potential for carbon storage, as well as adaptation to – or mitigation of – climate change is sometimes mentioned (e.g., Lichtfouse, 2012; Altieri et al., 2015) but ʻclimate-compatibility’ is not among agroecology initial objectives. On the other hand, CSA has not been defined to encompass agroecological principles, but it explicitly does include elements of such principles. CSA is presented in its original definition as an approach covering “agriculture and food systems”. The term ʻfood system’ can be understood as the trajectory ʻfrom field to fork’. This includes production systems, post-harvest interventions, pest, disease and water management, human nutrition, minimizing waste and losses, food transport, and access to markets.

Assessing whether or not CSA can address these requirements along the entire food value chain, while conforming to its original definition in terms of adaptation, mitigation and food security, is not a simple task. Holistic approaches such as life-cycle assessment are useful methodologies. Parallels can be found here with ʻsustainable agricultural intensification’, which is a ʻradical rethinking of food systems not only to reduce environmental impacts but also to enhance animal welfare and human nutrition and support rural economies and sustainable development’ (Garnett et al., 2013; Campbell et al., 2014). The need to develop ʻinclusive food value chains’ in support of CSA was highlighted by the FAO in the founding CSA documents (FAO, 2013). However, innovative research is required to assess CSA under this holistic perspective.

Consequently, there is still a need to carefully rethink the theoretical foundation of CSA. In the thorough review on the CSA global research agenda published by Steenwerth et al. (2014), reference is made to the need for further interdisciplinary and transdisciplinary research to better understand and measure CSA processes that may lead to the transformative changes needed in agriculture. This thinking can help in designing an improved, holistic CSA paradigm.

3 The implementation challenge

Although FAO’s CSA sourcebook (2013) provides many examples, CSA is described in terms of objectives to be reached and not in terms of the means to be employed to reach those objectives. This leaves it open to users to decide on the approach to the types of interventions they consider ʻclimate-smart’. Progressively, the CSA concept has also evolved from achieving the triple win more generally and globally, to achieving synergies between the three CSA objectives as a function of local conditions. Indeed, some practices may be climate-smart in a specific local context, but not in another one, given agroecological conditions, market opportunities, and stakeholders’ priorities. Consequently, CSA practices are not “set in stone” and a broad range of practices is now being recognized.

This context-specific approach takes into account the diversity of agricultural systems and stakeholders’ priorities in order to support CSA implementation and broad adoption (Andrieu et al., 2017). It also explains why for many, CSA is simply a framework to address agriculture under climate change, thus leaving the door open to many interpretations. However, this runs the risk of ignoring one or more of the three pillars with the risk of compromising the overall intentions of CSA.

When the definition of CSA is taken loosely, without the requirements for sustainability and for the three CSA pillars, practices that promote herbicides or energy-or-water-intensive farming – such as in large-scale industrial monocultures or biofuel plantations – have sometimes incorrectly been called ʻclimate-smart.’ Intensive bioenergy crops for instance, have sometimes been described as climate-smart because they contribute to renewable energy production. However, these metrics need to be gauged against other possible land uses (food crops) and in terms of environmental impact (e.g., biochemical inputs, biodiversity, and water). Similarly, drought-tolerant varieties that require high fertilizer inputs may seem well-adapted to climate stress and produce biomass that can contribute to food security, but may not perform in terms of mitigation and resilience to unexpected climatic events.

Operationalizing CSA has often been presented in terms of dealing with synergies or trade-offs among the three pillars, but particularly between adaptation and mitigation. Indeed, mitigation may not be a priority in a given context, particularly where farmers use low levels of production inputs. Practices that may be relevant for their positive effects on adaption or food security may not have a direct effect on mitigation (e.g., drought-tolerant varieties). Consequently, some documents indicate that CSA should aim to reduce emissions “where possible” ( Accessed 13/2/2018). Conversely, mitigation options by small farmers (e.g., options to increase soil organic matter content) may not show co-benefits in terms of adaptive capacity in the short term (Steenwerth et al., 2014).

The question remains whether this is a contradiction with the original CSA definition, or if the CSA concept should be broadened to include options that can at least result in positive outcomes on two pillars. A bias was also introduced in the way mitigation was taken into account by CSA, since it has often been promoted in terms of reducing emissions and not in terms of increasing carbon sequestration through biomass or soil.

Synergies occur when food security, adaptation, and mitigation not only occur simultaneously (i.e., co-benefits) but when there is a positive feedback of either on the others. For instance, if nitrogen-fixing trees are associated with crops to improve soil fertility (adaptation and food security), soil carbon content may increase (mitigation) and the resulting decrease in fertilizer use will lead to a reduction in N2O emissions (mitigation). Similarly, if compost is incorporated into the soil with the objective of increasing soil organic matter (mitigation), better yields and improved livelihoods will result (adaptation).

There are some CSA ʻsuccess stories’ that provide examples of synergies and positive feedbacks among the three pillars. For instance, intermittent irrigation of flooded rice, also known as the ʻSystem of Rice Intensification’ (SRI) has been shown to reduce methane emissions (mitigation), decrease water use (adaptation and resilience), and increase yield, and thus food security (Thakur et al., 2016), although some questions persist about weed control or actual yield benefit. Farmer-managed regeneration of scattered trees on cropland in the Sahel (agroforestry) is another case: it contributes to soil and biomass carbon sequestration, buffers heat stress and erosion, improves soil fertility and finally leads to better food security through commodity and income diversification (Sendzimir et al., 2011). But it needs to be acknowledged that not all practices will result in synergies and often may result in trade-offs, and thus, further research is needed.

Stakeholder-driven analyses of Climate-smart agriculture require a transdisciplinary effort to consistently link state-of-the-art data, climate scenarios, and socio-economic trajectories in crop, livestock, and economic models (Rosenzweig et al., 2013). Crop and livestock model outputs are aggregated as inputs to regional and global economic models to determine regional vulnerabilities, changes in comparative advantage, price effects, and potential climate-smart strategies in the agricultural sector (e.g., Rosegrant et al., 2017). For example, the Agricultural Model Intercomparison and Improvement Project (AgMIP) utilizes intercomparisons of these various types of methods to improve crop, livestock, and economic models and ensemble projections to produce enhanced assessments by in-country crop, livestock, and economic modeling communities (Rosenzweig et al., 2013). These new methods of regional integrated assessments include iterative stakeholder inputs to provide an effective science and evidence base for climate-smart decision-making in farming systems.

4 CSA implications for policy and decision-makers

Contrasting views exist about the development of the CSA concept. Some civil society organizations have described simplifications of the CSA concept as ʻgreen washing’. The triple win has also been described as an ʻillusion’ which can only be resolved with trade-offs through political processes because its three dimensions correspond to negotiating arenas (poverty alleviation, food security, and climate change mitigation) that have different stakes and stakeholders (Caron and Treyer, 2015).

Policymakers in many developing countries, particularly in Africa, have explicitly included CSA in their Nationally Determined Contributions (NDCs) prepared in the context of UNFCCC’s Paris Agreement ( Accessed 13/2/2018) and there are an increasing number of climate change plans and strategies that articulate agriculture and food system adaptation and mitigation at national levels. More effective policies can be designed that take into account complementarity between policy instruments and between implementing institutions. These need to explicitly seek to avoid antagonistic effects such as promoting carbon sequestration and simultaneously subsidizing mineral fertilizers.

Decision-making tools for CSA need to incorporate a complete set of measures that foster change towards the concurrent consideration of food security, adaptation and mitigation in land-use practices and equally importantly, to promote changes in governance and financing (Torquebiau et al., 2016). Furthermore, local adaptation and food security refer to private goods, while mitigation refers to a public (global) good (Steenwerth et al., 2014); thus they are consequently funded by distinct financing schemes.

Many decision support tools for policy makers and local actors have been proposed to take into account the synergies and trade-offs between the CSA pillars (Campbell et al., 2016) but these tools falter due to the lack of scientific evidence on the effectiveness of CSA practices (Rosenstock et al., 2016). Reliable indicators are required to separate CSA from non-CSA activities. For this, the development of consistent CSA metrics, either biophysical, policy-based or finance-related, is needed. Rosenstock et al. (2016) proposed a reference framework, with easy-to-measure parameters, such as proxies for soil carbon sequestration, reduction of GHG emissions, and cost-benefit analyses of the simultaneous fulfillment of CSA’s three pillars. Well-designed metrics will contribute to the ex-post quantification of adaptation or mitigation, and the achievement of robust cross-site comparisons.

The development of environmental and social safeguards for CSA is also a very important issue. Specific indicators are required to ensure that selected CSA technologies and approaches comply with the implicit CSA sustainability requirements, e.g., inclusivity of relevant stakeholders; sensitivity to gender, age, class, or ethnicity; biodiversity protection; role of family farming and traditional knowledge; contribution to rural employment; and property or water rights.

Since climate change plans and strategies are relatively new, there is a lack of documentation of their implementation at the local level. Some case studies show that farmers have a growing perception of climate change and of the need to adapt, but they do not clearly understand the direct consequences to their farm in the short-, medium- and long-terms (Bormann et al., 2012). In developing countries where the level of inputs can be low, mitigation is hardly the entry point to trigger changes. Collective action is therefore necessary to steer governance rules and financing towards the three goals of CSA. Innovative thinking is required in order to reconcile policy and practice along complementary lines.

CSA implementation also faces a better understanding of the capacity of extension services or consultants in each country to help training farmers on climate-smart practices. It is well-known that innovative technologies (e.g., agroforestry) require specific extension support, sometimes not readily available (Chitakira and Torquebiau, 2010). A better understanding of farmers’ views and actions on CSA practices is also required. In the end, it all comes down to whether or not individual farmers are willing to adopt the required changes or have the knowledge and capacity to make those changes (Chatrchyan et al., 2016).

New financing instruments are also needed to support changes at all levels, from local, to national and global. The COP21 Paris Agreement provided a sound basis for further raising the profile of agriculture within the UNFCCC negotiations and developing new financing instruments for climate change and agriculture. The recent COP23 (November 2017) has officially brought agriculture into the negotiations. This will bring greater focus on implementing climate actions in the sector as opposed to negotiations focused on scientific and technical aspects only. Finally, there is an increasing awareness that achievement of CSA globally will require policy interventions at all levels, and including multiple actors (Chatrchyan et al., 2018 forthcoming).

5 Case study: the 4 per 1000 Initiative

At COP21 climate negotiations in Paris, the 4 per 1000 Initiative ‘Soils for Food Security and Climate’ was launched to promote the role of soil organic matter in addressing the triple challenge of food security, adaptation of agriculture to climate change, and mitigation of greenhouse gas emissions (Lal et al., 2015; Minasny et al., 2017; Soussana et al., 2018). The similarity with CSA is striking in terms of objectives, but the 4 per 1000 initiative focuses solely on soil carbon management as a means to achieve its goals. The rationale for the 4per1000 program is that a 0.4% annual growth rate of the carbon stock of all soils of the world would make it possible to offset the present annual increases in atmospheric CO2.

Practices put forward to contribute to soil carbon sequestration include permanent soil cover, agroforestry, crop rotations (especially with legumes), organic fertilizers, conservation agriculture, agroecology, precision agriculture, improved grazing practices and quality of fodder, integrated soil fertility management, and improved water management. The practices encouraged under the 4per1000 concept consider mitigation both in terms of increasing carbon sequestration through biomass or soil and in terms of reducing GHG emissions. CSA can correct some of its weaknesses (and provide answers to criticisms) through a stronger focus on increasing soil organic matter by incorporating the 4 per 1000 principles as a component. This can be achieved not only in terms of soil carbon sequestration practices, but also by encouraging policies and institutional reforms that alert more stakeholders to the need for better soil management. But further evidence is needed to document the actual benefits and long-term metrics of both CSA and 4 per 1000 measures. This in turn could increase farmers’ adoption of sustainable practices and attract more financing for CSA and 4 per 1000 alike. However, it must be clarified that soil carbon sequestration does not happen independently from other sources of nutrients, especially phosphorus and nitrogen.

Indeed, synthetic nitrogen fertilizer continues to be the largest used macro-element on the planet for crop production systems. Over-use of nitrogen fertilizer is among the known causes and is the largest anthropogenic source of the potent GHG, nitrous oxide (N2O) emissions in the biosphere (Denman et al., 2007). In parallel, the nitrogen use efficiency continues to be less than 50% globally (Lassaletta, et al., 2014). Multipronged approaches and research are needed to empower farmers globally to adopt practices to increase the efficient use and application of nitrogen fertilizer. Rather than slow, incremental and evolutionary progress, revolutionary advances are needed in fertilizer management, such as the “Five-R” approach to reduce the ecological footprint (Right Input, at the Right Time, in the Right Amount, at the Right Place, and in the Right Manner) which can be applied to nutrient stewardship and is among the techniques that are scale independent (for large and small scale farming systems). It has been shown to optimize input sources, placement, amount, timing, and manner, while reducing nitrous oxide emissions, and maximize output, efficiency, and profitability in a sustainable manner (Khosla, et al., 2008).

Biological nitrogen fixation through legume plants and symbiotic rhizobia has also a key role to play. Provided there are adequate phosphorus concentrations and sufficient water, symbiotic nitrogen fixation, combined with improved nutrient management, can certainly match CSA requirements in terms of adaptation (particularly in multiple cropping situations), mitigation (accumulated biomass and decrease of N2O emissions) and food security.

6 Conclusions

As a major paradigm breakthrough, CSA raises unexpected questions. In this article, we have shown that CSA is both a technical and a political concept, requiring the bridging of several disciplines, and that achieving the three pillars of CSA concurrently is certainly not an easy task. We have described major implementation challenges of CSA and detailed key implications for policy and decision-makers. We have shown how soil carbon sequestration and CSA can be integrated and encouraged as complementary approaches. These reflections have raised several research questions which need to be addressed for CSA to be adopted. Compared to conventional, monodisciplinary research questions (e.g., breeding a crop for higher yield), CSA research entails a fair amount of uncertainty. Questions remain around how to strike the right balance between the three CSA criteria, how to measure CSA performance, and how to reconcile such a complex paradigm with farmers’ decisions. Not to mention the required negotiation processes between stakeholders and the necessary policy changes that need to take place. The tangled web of climate change mechanisms makes the equation “mitigation + adaptation + food security” a thorny one to solve (Torquebiau et al., 2016).

Agriculture, the human activity probably most dependent on the climate, was initially seen as a victim of climate change. Increasing temperature trends, higher frequency of weather extremes and greater seasonal variability have all been described as representing new threats for agriculture worldwide. Agriculture has then been regarded as one of the culprits responsible for climate change, because of direct greenhouse gases emissions through ruminants, fertilizer manufacturing and application, and on-farm energy use or indirect emissions related to land use change. Agriculture is now beginning to be also viewed as a solution to climate change, because of the role it can play in terms of GHG mitigation. Climate-smart agriculture can help to design land-use systems that make the adaptation-mitigation connectivity a reality at all scales and hence help farmers to become leading actors of climate change solutions.


We thank two anonymous reviewers for useful comments on an earlier version of the manuscript.


  • Altieri MA, Nicholls CI, Henao A, Lana MA. 2015. Agroecology and the design of climate change-resilient farming systems. Agronomy for Sustainable Development 35(3): 869–890. [CrossRef] [Google Scholar]
  • Andrieu N, Sogoba B, Zougmore R, Howland F, Samake O, Bonilla-Findji O, et al. 2017. Prioritizing investments for climate-smart agriculture: Lessons learned from Mali. Agricultural Systems 154: 13–24. [CrossRef] [Google Scholar]
  • Bormann H, Ahlhorn F, Klenke T. 2012. Adaptation of water management to regional climate change in a coastal region – Hydrological change vs community perception and strategies. Journal of Hydrology 454: 64–75. DOI: 10.1016/j.jhydrol.2012.05.063. [CrossRef] [Google Scholar]
  • Campbell BM, Thornton P, Zougmoré R, Van Asten P, Lipper L. 2014. Sustainable intensification: What is its role in climate smart agriculture? Current Opinion in Environmental Sustainability 8: 39–43. [CrossRef] [Google Scholar]
  • Campbell BM, Corner-Dolloff C, Girvetz E, Loboguerrero AM, Ramirez-Villegas J. 2016. Reducing risks to food security from climate change. Global Food Security 11: 34–43. [CrossRef] [Google Scholar]
  • Caron P, Treyer S. 2015. Climate-Smart Agriculture and International Climate Change Negotiation Forums. In: Torquebiau E, ed. Climate change and agriculture worldwide. Dordrecht (Netherlands): Springer, pp. 325–336. [Google Scholar]
  • Chatrchyan AM, Chaopricha NT, Erlebacher RC, Chan J, Tobin D, Allred SB. 2016. Understanding US Farmer Views and Actions on Climate Change. Cornell Institute for Climate Smart Solutions Research and Policy Brief, Issue 1, March 2016. [Google Scholar]
  • Chatrchyan AM, Yin C, Torquebiau E, Nagothu US. 2018. Multi-level policy measures to support sustainable agriculture intensification for smallholders. In: Nagothu US, ed. Agricultural development and sustainable intensification technology and policy challenges in the face of climate change. London: Routledge, 328 p. [Google Scholar]
  • Chitakira M, Torquebiau E. 2010. Barriers and coping mechanisms relating to agroforestry adoption by smallholder farmers in Zimbabwe. Journal of Agricultural Education and Extension 16(2): 147–160. [CrossRef] [Google Scholar]
  • Denman KL, Brasseur G, Chidthaisong A, Ciais P, Cox PM, Dickinson RE, et al. 2007. Couplings between changes in the climate system and biogeochemistry. In: Climate Change 2007: The physical science basis. Contribution of Working Group I to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change. Cambridge, United Kingdom and New York, NY, USA: Cambridge University Press. [Google Scholar]
  • Fallot A. 2016. Témoignage sur la conférence « Climate-smart agriculture 2015 » (Montpellier, 16–18 mars 2015). Natures Sciences Sociétés 24: 151–153. DOI: 10.1051/nss/2016013. [CrossRef] [EDP Sciences] [Google Scholar]
  • FAO. 2010. “Climate-Smart” Agriculture – Policies, Practices and Financing for Food Security, Adaptation and Mitigation. Rome (Italy): FAO. Available from [Google Scholar]
  • FAO. 2013. Climate-smart Agriculture Sourcebook. Rome (Italy): FAO. [Google Scholar]
  • FAO. 2015. Final Report for the International Symposium on Agroecology for Food Security and Nutrition, 18 and 19 September 2014. Rome (Italy): FAO. [Google Scholar]
  • Garnett T, Appleby MC, Balmford A, Bateman, IJ, Benton TG, Bloomer P, et al. 2013. Sustainable intensification in agriculture: premises and policies. Science 341(6141): 33–34. [Google Scholar]
  • Grau R, Kuemmerle T, Macchi L. 2013. Beyond “land sparing versus land sharing”: environmental heterogeneity, globalization and the balance between agricultural production and nature conservation. Current Opinion in Environmental Sustainability 5: 477–483. [CrossRef] [Google Scholar]
  • Hammond J, Fraval S, van Etten J, Suchini JG, Mercado L, Pagella T, et al. 2017. The Rural Household Multi-Indicator Survey (RHoMIS) for rapid characterisation of households to inform climate smart agriculture interventions: Description and applications in East Africa and Central America. Agricultural Systems 151: 225–233. [CrossRef] [Google Scholar]
  • Harvey CA, Chacón M, Donatti CI, Garen E, Hannah L, Andrade A, et al. 2014. Climate-smart landscapes: opportunities and challenges for integrating adaptation and mitigation in tropical agriculture. Conservation Letters 7(2): 77–90. [CrossRef] [Google Scholar]
  • IAASTD. 2009. International Assessment of Agricultural Knowledge, Science and Technology for Development. Agriculture at the Crossroads: The Global Report. Washington DC (USA): Island Press. [Google Scholar]
  • Khosla R, Inman D, Westfall DG, Riech R, Frasier WM, Mzuku M, et al. 2008. A synthesis of multi-disciplinary research in precision agriculture: Site-specific management zones in the semi-arid western Great Plains of the USA. J of Preci Ag 9(1–2): 85–100. [CrossRef] [Google Scholar]
  • Lal R, Negassa W, Lorenz K. 2015. Carbon sequestration in soil. Current Opinion in Environmental Sustainability 15: 79–86. [Google Scholar]
  • Lassaletta L, Billen G, Grizzetti B, Anglade J, Garnier J. 2014. 50 year trends in nitrogen use efficiency of world cropping systems: the relationship between yield and nitrogen input to cropland. Environmental Research Letters 9(10): 105011. [CrossRef] [Google Scholar]
  • Lichtfouse E. 2012. Agroecology and strategies for climate change. NY (USA): Springer. [Google Scholar]
  • Lipper L, Thornton P, Campbell BM, Baedeker T, Braimoh A, Bwalya M, et al. 2014. Climate-smart agriculture for food security. Nature Climate Change 4: 1068–1072. [CrossRef] [Google Scholar]
  • Lipper L, McCarthy N, Zilberman D, Asfaw S, Branca G (ed). 2017. Climate smart agriculture: building resilience to climate change. Natural Resource Management and Policy Series, Vol. 52. Dordrecht (Netherlands): Springer, 629 p. [Google Scholar]
  • Minang P, van Noordwijk M, Freeman OE, Mbow C, de Leeuw J, Catacutan D (eds). 2015. Climate-smart landscapes: Multifunctionality in practice. Nairobi (Kenya): World Agroforestry Centre (ICRAF), 404 p. [Google Scholar]
  • Minasny B, Malone BP, McBratney AB, Angers DA, Arrouays D, Chambers A, et al. 2017. Soil carbon 4 per mille. Geoderma 292: 59–86. [CrossRef] [Google Scholar]
  • Oxford Dictionnaries. 2016. (accessed 5 February 2016). [Google Scholar]
  • Pimbert M. 2015. Agroecology as an alternative vision to conventional development and Climate-Smart Agriculture. Development 58(2–3): 286–298. [CrossRef] [Google Scholar]
  • Renwick AR, Vickery JA, Potts SG, Bolwig S, Nalwanga D, Pomeroy DE, et al. 2014. Achieving production and conservation simultaneously in tropical agricultural landscapes. Agriculture, Ecosystems & Environment 192: 130–134. [CrossRef] [Google Scholar]
  • Richardson RB. 2010. Ecosystem services and food security: economic perspectives on environmental sustainability. Sustainability 2(11): 3520–3548. [Google Scholar]
  • Rosegrant MW, Sulser TB, Mason-D’Croz D, Cenacchi N, Nin-Pratt A, Dunston S, et al. 2017. Quantitative foresight modeling to inform the CGIAR research portfolio. Washington (USA): IFPRI. [Google Scholar]
  • Rosenstock TS, Lamanna C, Chesterman S, Bell P, Arslan A, Richards M, et al. 2016. The scientific basis of climate-smart agriculture: A systematic review protocol. CCAFS Working Paper no. 138. Copenhagen (Denmark): CGIAR Research Program on Climate Change, Agriculture and Food Security (CCAFS). Available at [Google Scholar]
  • Rosenzweig C, Jones JW, Hatfield JL, Ruane AC, Boote KJ, Thorburn P. 2013. The agricultural model intercomparison and improvement project (AgMIP): protocols and pilot studies. Agricultural and Forest Meteorology 170: 166–182. [CrossRef] [Google Scholar]
  • Saj S, Torquebiau E, Hainzelin E, Pagès J, Maraux F. 2017. The way forward: an agroecological perspective for Climate-Smart Agriculture. Agriculture, Ecosystems and Environment 250: 20–24. DOI: 10.1016/j.agee.2017.09.003. [CrossRef] [Google Scholar]
  • Sendzimir J, Reij C, Magnuszewski P. 2011. Rebuilding resilience in the Sahel: regreening in the Maradi and Zinder regions of Niger. Ecology and Society 16(3): 1. [Google Scholar]
  • Soussana JF, Lutfalla S, Ehrhardt F, Rosenstock T, Lamanna C, Havlík P, et al. 2018. Matching policy and science: rationale for the ʻ4 per 1000 – soils for food security and climate’ initiative. Soil & Tillage Research. In press. DOI: 10.1016/j.still.2017.12.002. [Google Scholar]
  • Steenwerth K, Hodson A, Bloom A, Carter M, Cattaneo A, Chartres C, et al. 2014. Climate-smart agriculture global research agenda: scientific basis for action. Agric & Food Secur 3: 1–39. [CrossRef] [Google Scholar]
  • Thakur AK, Uphoff NT, Stoop WA. 2016. Scientific Underpinnings of the System of Rice Intensification (SRI): What is known so far? Advances in Agronomy 135: 147–179. [CrossRef] [Google Scholar]
  • Tissier J, Grosclaude JY. 2015. What about climate-smart agriculture? In: Torquebiau E, ed. Climate change and agriculture worldwide. Dordrecht (Netherlands): Springer, pp. 313–324. [Google Scholar]
  • Torquebiau E (ed). 2016. Climate change and agriculture worldwide. Dordrecht (Netherlands): Springer, 348 p. [Google Scholar]
  • Torquebiau E, Berry D, Caron P, Grosclaude JY. 2016. New research perspectives to address climate challenges facing agriculture worldwide. In: Torquebiau E, ed. Climate change and agriculture worldwide. Netherlands: Springer, pp. 337–348. [CrossRef] [Google Scholar]

Cite this article as: Torquebiau E, Rosenzweig C, Chatrchyan AM, Andrieu N, Khosla R. 2018. Identifying Climate-smart agriculture research needs. Cah. Agric. 27: 26001.

Current usage metrics show cumulative count of Article Views (full-text article views including HTML views, PDF and ePub downloads, according to the available data) and Abstracts Views on Vision4Press platform.

Data correspond to usage on the plateform after 2015. The current usage metrics is available 48-96 hours after online publication and is updated daily on week days.

Initial download of the metrics may take a while.