Implications

This review shows that the role of livestock in agricultural sustainability in Sub-Saharan Africa (SSA) is complex and conflicting. In view of the marked diversity in biophysical and socio-economic contexts of smallholder crop-livestock farmers in SSA, the concept of sustainable agriculture has to be adapted to varied local values and constraints. Livestock deliver a range of ‘goods’ in the dominant smallholder mixed crop and livestock systems in Africa, therefore the over-emphasis on the environment is simplistic and should be moderated by the enormous importance of livestock in generating food security for some of the more vulnerable people in the world.

Sustainable agriculture: definition of concept and need

The concept of sustainability is increasingly recognized as a desirable, if not essential, outcome in many areas of agricultural research. However, researchers often struggle to define it when challenged to do so. Indeed, Pretty et al. (Reference Pretty, Toulmin and Williams2011) draw attention to more than 100 different ways of defining sustainability and it can be concluded from this pot pourri that there is no one definition to fit all possible scenarios. The umbrella definition of sustainable development, going back to 1978, is perhaps that of the World Commission on Environment and Development (also known as the Brundtland Commission), namely ‘development that meets the needs of the present without compromising the ability of future generations to meet their own needs’. Whilst there are many subtleties that are not captured by this definition, it does serve to emphasize the essential element of considering the implications of current practice for future generations as well as our own.

The concept of sustainable agriculture essentially follows the key principles inherent in sustainable development. Rudel et al. (Reference Rudel, Kwon, Paul, Boval, Rao, Burbano, McGroddy, Lerner, White, Cuchillo, Luna and Peters2016) defined sustainable agriculture as producing enough food for consumers and enough income for farmers while maintaining agro-ecosystem services. National Research Council (NRC) (2010) in its publication ‘Toward Sustainable Agricultural Systems in the 21st Century’ defined sustainable agriculture as agriculture that satisfies human food, feed and fibre needs; enhances environmental quality and the resource base; sustains economic viability and enhances the quality of life for farmers, farm workers and society as a whole. From these various definitions, the common elements of sustainable agriculture include food production for both present and future needs, persistence of the systems (i.e. capacity to continue to produce desired outputs over long periods), resilience (ability to absorb shocks and stresses, and deliver the desired outputs) and environmental friendliness. (Schiere et al., Reference Schiere, Ibrahim and van Keulen2002; Pretty et al., Reference Pretty, Toulmin and Williams2011). Nonetheless, the concept of agricultural sustainability inherently lacks specificity. Approaches to overcoming this difficulty usually centre around the definition of indicators and metrics (Smith et al., Reference Smith, Snapp, Chikowo, Thorne, Bekunda and Glover2017) that the evidence suggests are likely to be reliably associated with ultimately sustainable outcomes.

In view of marked diversity in biophysical and socio-economic contexts of smallholder crop-livestock farmers in SSA, the concept of sustainable agriculture has to be adapted to varied local values and constraints. This implies that agricultural practices that can be regarded as sustainable in one region may not be sustainable in another. In this paper, we will adopt as a working definition of sustainable agriculture, ‘agriculture that is sufficiently productive to meet food needs in both short and long-terms, and that is economically viable, environmentally friendly and socially acceptable’ (Schiere et al., Reference Schiere, Ibrahim and van Keulen2002; NRC, 2010).

The role of livestock in sustainable agriculture in Sub-Saharan Africa

In SSA, sustainable agricultural practices have focused on intensification practices which aim to increase the efficiency (output : input ratio) of production systems. Intensification of farming systems will depend on factors such as farmers’ agro-ecological potential, economic conditions, market situation, policy environment, institutional capacity and available technological options (Gunton et al., Reference Gunton, Firbank, Inman and Winter2016). Tactics for intensification include increasing use of inputs, introduction of new inputs to the system, and or use of existing inputs in a new way (Pretty et al., Reference Pretty, Toulmin and Williams2011) provided that these changes result in a disproportionate increase in associated outputs. Some common intensification practices in mixed crop and livestock systems include application of inorganic fertilizer, use of improved seed, conservation agriculture and small-scale mechanization alongside animal-related interventions such as animal traction, animal manure use, improved breeds and improved feeding practices (Table 2). Generally, capital-intensive intensification options are not widely adopted in SSA due to the obvious constraint of lack of financial resources (Vall et al., Reference Vall, Marre-Cast and Kamgang2017).

Table 2 Benefits and constraints of some intensification practices in smallholder mixed crop-livestock systems in sub-Saharan Africa

Application of animal manure to cropped land is widely practiced in SSA and there is widespread evidence of beneficial effects on grain yield and soil fertility (Vall et al., Reference Vall, Marre-Cast and Kamgang2017). Application of animal manure is normally pivotal in mixed crop-livestock systems. In African Drylands, often only manured crop fields are in positive nutrient balance as shown by results of a study of livestock-mediated nutrient transfers from south-western Niger (Hiernaux and Ayantunde, Reference Hiernaux and Ayantunde2004;Table 3). The main constraints to manure application is always inadequate quantity due to low animal numbers and a shortage of labour for distributing the manure.

Table 3 Dry matter, nitrogen and phosphorus balance of different land use types in Fakara, south-western Niger in 1998

Adapted from Hiernaux and Ayantunde (Reference Hiernaux and Ayantunde2004). Only manured field had a positive nutrient balance but only 10% of the crop field in the study site is manured.

Associated with peri-urban dairy production in many African countries is the use of improved dairy cows (Anderson, Reference Anderson2003; Paul et al., Reference Paul, Frelat, Birnholz, Ebong, Gahigi, Groot, Herrero, Kagabo, Notenbaert, Vanlauwe and van Wijk2018) which produce more milk than local breeds provided they are well fed. For example in Rwanda, the government provided crossbred cow to poor farmers under the ‘one cow per poor family’ programme which aims to improve food and nutrition security, and reducing poverty (Paul et al., Reference Paul, Frelat, Birnholz, Ebong, Gahigi, Groot, Herrero, Kagabo, Notenbaert, Vanlauwe and van Wijk2018). The crossbred cows produced 2 to 4 l/cow per day compared with 2 l/cow per day for the local breed (Paul et al., Reference Paul, Frelat, Birnholz, Ebong, Gahigi, Groot, Herrero, Kagabo, Notenbaert, Vanlauwe and van Wijk2018). Although crossbreds make a big difference to yield potential, there are relatively few examples of economically sustainable practices that allow that potential to be realised. The main constraint to more widespread use of improved livestock breeds is lack of artificial insemination, high feed requirements of the improved breeds, reduced disease resistance and lack of necessary animal husbandry skills.

Use of animals (bull, oxen, horse and donkey) for traction is also a common practice in mixed crop and livestock systems in SSA (Savadogo et al., Reference Savadogo, Reardon and Pietola1998; Sheahan and Barrett, Reference Sheahan and Barrett2017). Animal traction is widely practiced to plough crop field and for weeding in many farming systems in SSA, particularly for cash crops such as cotton in West African Sahel. Lack of bulls, particularly in West Africa, and high feed requirements are often the constraints to use of animal traction in mixed crop and livestock systems.

Food security is an urgent and immediate challenge in SSA due to a rapidly growing population coupled with lagging agricultural growth (The Montpellier Panel, 2013). Addressing this challenge requires sustainable agricultural practices and choices to significantly increase yields on existing agricultural land. Livestock have an important role to play in enhancing food security and particularly nutritional security. Although there is increasing consumption of animal source food in the human diet in many countries in SSA (such as Burkina Faso, Ghana, Ethiopia, Kenya; Food and Agriculture Organization of the United Nations (FAO), 2011), the diet is still largely dominated by the intake of basic cereal-based staple foods which are usually deficient in protein and micro-nutrients necessary for healthy human development (Reynolds et al., Reference Reynolds, Wulster-Radcliffe, Aaron and Davis2015). The consumption of animal products is closely related to per capita income with the urban population consuming higher amounts of animal protein due to their growing financial means. Consumption of animal protein is particularly important for children under 5 years and women of reproductive age. The importance of consumption of animal source food for cognitive development of children is well documented (Fan and Brzeska, Reference Fan and Brzeska2016). For example, a nutritional study in Gourma in the Northern part of Mali showed that the children of mobile pastoralists were better nourished based on weight-height, weight-age and height-age measures than children of sedentary farmers (Pederson and Benjaminsen, Reference Pedersen and Benjaminsen2008). This difference was largely attributed to consumption of milk and milk products by the pastoralist children underscoring the important role that livestock play in human nutrition. Households that keep livestock are more likely to consume animal-source food because of their proximity to these nutrient-rich foods (Reynolds et al., Reference Reynolds, Wulster-Radcliffe, Aaron and Davis2015). Increased consumption of animal-source food by rural households reduces stunting in children and improves the health of household members, particularly children and vulnerable women (Pedersen and Benjaminsen, Reference Pedersen and Benjaminsen2008). One pathway to improve the consumption of animal protein is through improvements in livestock production. Agricultural production practices that lead to increased grain and livestock productivity will likely impact positively on food security as observed by the respondents in a survey in two provinces in Burkina Faso regarding the impact of intensification practices on household food security (Figure 1).

Figure 1 Perceived impact of intensification practices on household food security in Burkina Faso (n=400 households interviewed in Seno and Yatenga provinces).

Household survey data show that another key food security role of livestock is in generating income, so that food can be bought throughout the year. Families that keep few livestock are the most vulnerable to food shortages based on evidence from surveys in mixed crop-livestock systems in four countries in West Africa (Figure 2). In Figure 3 (after Ritzema et al., Reference Ritzema, Frelat, Douxchamps, Silvestri, Rufino, Herrero, Giller, López-Ridaura, Teufel, Birthe and Wijk2017), at contrasting sites in Burkina Faso, Ethiopia and Kenya, the relative importance of on- and off-farm activities for food security is quantified, illustrating that both consumption and sales of livestock products are essential for food security. In the agro-pastoral region in Borana, southern Ethiopia, direct consumption of livestock products plays a dominant role in livelihoods, while in the other sites, sales of livestock products are important for cash generation. These results also show that the most food secure households are also typically the households with most livestock and therefore the highest importance of livestock products in their livelihood compared with the other food security groups.

Figure 2 Vulnerability of different families to food shortage (normalized ranks 0 to 1) in West Africa (data from survey of 550 households in Burkina Faso, Mali, Niger and Nigeria). Poor in livestock means those with no cattle and less than 5 sheep and goat. Those that lack cultivable land are those who lack access to land often immigrants.

Figure 3 Relative contribution of six livelihood sources to food security. Results reported by household food security groupings and by site, Yatenga, Burkina Faso (BF); Borana, Ethiopia (ET); Nyando and Wote, Kenya (KE). Column widths denote the relative household membership within each food security category at each site (after Ritzema et al., Reference Ritzema, Frelat, Douxchamps, Silvestri, Rufino, Herrero, Giller, López-Ridaura, Teufel, Birthe and Wijk2017). FAI is Food Availability Index while Household FAI groupings are expressed in MJ/male adult equivalent (MAE)/day.

Drivers of sustainable agriculture in Sub-Saharan Africa and some constraints

Population growth, climate change and natural resource availability (land and water) are the main drivers of sustainable intensification in SSA (Pretty et al., Reference Pretty, Toulmin and Williams2011). There is a need to produce more food on less land to meet the growing food demand of the population, but this must be done in a way that does not undermine environmental integrity. The average annual population growth rate of 2.7% in SSA has led to the challenge of feeding more people which necessitates an increase in agricultural production (The Montpellier Panel, 2013).

Climate change and variability has compelled farmers to diversify species composition of their herds (Zougmoré et al., Reference Zougmoré, Partey, Ouédraogo, Omitoyin, Thomas, Ayantunde, Ericksen, Said and Jalloh2016; Vall et al., Reference Vall, Marre-Cast and Kamgang2017). For example, repeated occurrence of droughts in the Sahel has led many pastoralists, who were once solely dependent on livestock for their livelihoods, to adopt agro-pastoralism (i.e. rearing livestock and growing crops; Zougmoré et al., Reference Zougmoré, Partey, Ouédraogo, Omitoyin, Thomas, Ayantunde, Ericksen, Said and Jalloh2016). In response to climate change, many crop farmers have also diversified in the past two decades into rearing livestock due to repeated crop failure associated with droughts (Zougmoré et al., Reference Zougmoré, Partey, Ouédraogo, Omitoyin, Thomas, Ayantunde, Ericksen, Said and Jalloh2016). Investment in irrigation has been advocated as a potential ‘game changer’ in improving agricultural productivity in view of the present very low irrigated area (4% of the cultivated land) in Africa (The Montpellier Panel, 2013).

Some barriers to sustainable intensification in SSA include lack of policy support to smallholder farmers (Garnett et al., Reference Garnett, Appleby, Balmford, Bateman, Benton, Bloomer, Burlingame, Dawkins, Dolan, Fraser, Herrero, Hoffmann, Smith, Thornton, Toulmin, Vermeulen and Godfray2013), a dysfunctional institutional environment (Hounkonnou et al., Reference Hounkonnou, Kossou, Kuyper, Leeuwis, Nederlof, Röling, Sakyi-Dawson, Traoré and van Huis2012), market failures, lack of appropriate productivity-enhancing agricultural technologies and low adoption where they are available, lack of access to credit, low use of external inputs and poverty leading to short-termism among farmers. The policy (local, national and regional) and institutional environment (customary and modern) are key to sustainable agriculture in SSA. At continent level, the policy initiative of the African Governments to increase agricultural productivity known as the Comprehensive Africa Agriculture Development Programme has set a target of six per cent annual agricultural productivity growth rate. To achieve this target it has been recommended that 10% of the annual budget of each country should be spent on the agriculture sector at the Maputo Declaration (New Partnership for Africa’s Development, 2003). This increased policy attention to agricultural growth is a welcome spur to agricultural intensification in Africa although the implementation may be lagging behind. Institutional issues that can impact on agricultural sustainability in SSA include natural resource governance, knowledge institutions (agricultural research and local institutions) and stakeholders’ organizations, particularly farmers’ networks/associations. Other factors such as insecurity and civil war, insecure land tenure and water rights, weak agricultural extension systems, and underfunding of national agricultural research systems further aggravate the difficulties facing agricultural production in SSA (Douxchamps et al., Reference Douxchamps, Ayantunde and Barron2014).

Market development and the associated growing demand for agricultural products (food, e.g. grains, meat and milk; and processed food products) is another important factor determining agricultural sustainability (Garnett et al., Reference Garnett, Appleby, Balmford, Bateman, Benton, Bloomer, Burlingame, Dawkins, Dolan, Fraser, Herrero, Hoffmann, Smith, Thornton, Toulmin, Vermeulen and Godfray2013). This entails both more food and value addition. The barrier to sustainable agriculture of low use of external inputs could be attributed to extensive farming systems and the associated subsistence orientation of crop and livestock farmers. Besides, low use of external inputs could be due to poor financial resources among farmers, lack of access to external inputs and the high price of the inputs where available confounded by high production risk, as agriculture is largely rainfed in SSA, and high market risk. One opportunity to reduce the latter risk is the rapidly increasing availability of mobile phone technology. Increased use of mobile phones has facilitated real-time access to market information particularly prices of agricultural products (grains and live animals) which is influencing the decision of many rural farmers on when and where to sell their produce (Sheahan and Barrett, Reference Sheahan and Barrett2017).

Livestock-related intensification practices in Sub-Saharan Africa: pathways to sustainable agriculture

Intensification of agricultural production has been widely advocated as the key pathway to sustainable agriculture in Africa. There is great potential for intensification of crop and livestock production in view of the current low productivity and high productivity gap (Gunton et al., Reference Gunton, Firbank, Inman and Winter2016). For intensification to be sustainable, Pretty et al. (Reference Pretty, Toulmin and Williams2011) suggested a number of criteria including efficient and prudent use of inputs, minimizing greenhouse gas (GHG) emissions or environmental costs, increasing the flow of environmental services and strengthening resilience. A well-known conceptual example of livestock intensification is the so-called livestock ladder (Udo et al., Reference Udo, Aklilu, Phong, Bosma, Budisatria, Patil, Samdup and Bebe2011), which describes a theoretical system that poor smallholders can use to step up from keeping small-stock to acquiring larger animals. Continued re-investment in the agricultural system is needed in the lowest parts of ladder, plus the availability of fodder to feed the growing stock. According to these authors, the economic benefits derived from livestock intensification depends on the rung of the ladder where the farmers are located. Thus, the smallest economic benefits will come from village poultry, followed by small ruminants, pigs and local cattle while the largest economic benefit will come from dairy cattle.

The livestock ladder gives a conceptual model of change in livestock holdings over time, but in practice the resource-constrained smallholder crop and livestock farmers in SSA can directly potentially increase their livestock production (produce more per given land area and per unit livestock) through adoption of appropriate technological, social and institutional innovations, and through improvement of farmers’ knowledge and capacity, and better market access (Pretty et al., Reference Pretty, Toulmin and Williams2011). For example, Amole et al. (Reference Amole, Zijlstra, Descheemaeker, Ayantunde and Duncan2017) have shown through a simulation model of West Africa Dwarf goats production that with improved feeding management such as grazing with supplementation or cut-and-carry feeding systems, the pre-weaning growth rate of kids can be doubled and the pre-weaning mortality can be reduced from about 26% in the traditional free-range feeding system to between 5% and 12% in improved feeding systems. Similar results of increased animal productivity have been reported with improved feeding systems in smallholder dairy production in East Africa (Bebe et al., Reference Bebe, Udo and Thorpe2002). In Ethiopia, yield gap analyses of attainable milk yield by cows showed that replacing indigenous zebu with crossbred cattle could lead to doubling of milk yields, even on traditional diets, and to a profitable smallholder dairy enterprise (Mayberry et al., Reference Mayberry, Ash, Prestwidge, Godde, Henderson, Duncan, Blummel, Reddy and Herrero2017). This demonstrates that there is great potential for livestock productivity and economic gains through more intensive livestock production.

The growing demand for livestock products particularly in urban areas also provides opportunity for the intensification of livestock production. Consumption of livestock products has been increasing over the years in all regions in SSA and these trends are expected to continue in the foreseeable future. For example, in West Africa, the current annual growth rates in livestock commodity consumption (2.7% for mutton, 4% for poultry, 2.9% for milk and 3.3% for beef; FAO, 2011) are much higher than for cereals (about 2%). The growing demand for consumption of animal source food has been driven partly by rapidly growing cities, potentially opening up avenues to bridge nutritional gaps, as well as providing incomes and livelihoods for the population, including for target groups such as the poor, women and youth. In addition, the growing demand has also been driven by the improved regional economic performance in the last few decades, moving from the negative GDP growth rates observed in the early 1980s to annual growth rates that have remained positive since then. Though there will be continued growth in per-capita demand for livestock products in West Africa and other regions in Africa from 2000 to 2030, the absolute increase in annual per-capita consumption (in kg/person) during this period is still low compared with regions in Asia (FAO, 2011).

Another opportunity for sustainable agriculture in SSA is the increasing integration of crop and livestock production, though the level of integration may vary depending on the agro-ecological potential, socio-economic endowment, production objectives, natural resource base and local institutions. Better integration of crop and livestock production could improve the efficiency of nutrient cycling in farming systems and whole farm productivity (NRC, 2010; Vall et al., Reference Vall, Marre-Cast and Kamgang2017). Integration of crop and livestock production provides opportunity for value addition to crop residues by the livestock through conversion of ‘waste’ products which cannot be consumed by humans (crop residues) into nutrient-rich foods. The contribution of crop residues to livestock diets will continue to increase in African farming systems depending on the agro-ecological zone in view of the declining grazing areas due to expansion of arable production, particularly in Africa drylands (Dongmo et al., Reference Dongmo, Vall, Dugué, Njoya and Lossouarn2012) For example, results from evaluation of feed resources in three countries in West Africa showed the increasing contribution of crop residues to livestock diets as we move from sub-humid zone (<10%) to semi-arid zone (about 50%; Figure 4). Similar trends are seen in a recent study in Ethiopia which assessed historical changes in feed sourcing across the pastoral to highland gradient and pointed to increasing importance of crop residues in livestock diets (Figure 5).

Figure 4 Contribution of crop residues to household livestock (cattle, sheep and goat) diet across agro-ecological zones in West Africa.

Figure 5 Historical changes in feed sourcing across the pastoral to highland gradient in Ethiopia, 30–40 years ago compared with present (2011) (adapted from Mekasha et al., Reference Mekasha, Gerard, Tesfaye, Nigatu and Duncan2014).

Better manure management also provides the opportunity to reduce GHG emissions in addition to contributing to efficient nutrient cycling in the mixed crop and livestock systems. Practices such as mulching or using cereal straws as beddings where animals are corralled have resulted in better capture of faecal and urinary nitrogen thereby reducing ammonia volatilization, which can be up 60% of excreted faeces and urine (Hiernaux and Ayantunde, Reference Hiernaux and Ayantunde2004). Besides, the association of mulching and corralling of ruminants improves soil chemical properties which can lead to increase in grain yield and crop residue biomass.

In addition to intensification, livelihood diversification is an important pathway to sustainable agriculture in Africa. This can be defined as the process by which rural families construct a diverse portfolio of activities and social support capabilities in order to survive and to improve their standards of living (Ellis, Reference Ellis1998). According to Ellis, diversification may occur both as a deliberate strategy by the household or be triggered by crises such as climatic shocks. Diversification may concern on-farm or off-farm activities. Off-farm activities such as small commerce, seasonal migration, etc., provide additional sources of revenue for rural households which may be invested in agricultural production. Livestock play an important role in diversification strategies, because of their diverse role in smallholder livelihoods: livestock produce food that can be directly consumed, while livestock products are also sold to generate essential cash for expenses. The livestock herd can also function as a flexible reserve for the farm household. For example, the repeated occurrence of droughts in the West African Sahel has led to significant shifts in herd composition from cattle to small ruminants (Zougmoré et al., Reference Zougmoré, Partey, Ouédraogo, Omitoyin, Thomas, Ayantunde, Ericksen, Said and Jalloh2016). Diversification of agricultural production systems is often associated with increased resilience of livelihoods and livestock can play a key role in the ability of smallholder households to deal with shocks (e.g. the ‘banking’ function of livestock in case of severe droughts) when major food crops fail. Both intensification and livelihood diversification pathways to sustainable agriculture are complementary. For example, money from seasonal migration by members of the agro-pastoral households is often invested in acquiring livestock and inputs for crop farming.

Environmental consequences of livestock in sustainable agriculture

In the previous sections we have stressed the ‘goods’ of livestock for sustainable intensification and increased recycling of organic matter and nutrients: soil fertility amendment through concentration of organic matter (either through grazing of crop residues or common grasslands), including enhanced nutrient cycling; the essential role of livestock in supplying traction and thereby the timely planting of crops at the start of the growing season; and adding value to crop residues leading to increased system productivity. In this section we will concentrate on the environmental consequences of livestock in sustainable agriculture in SSA.

Livestock have received much negative publicity in recent years for their impact on the environment (Steinfeld et al., Reference Steinfeld, Gerber, Wassenaar, Castel, Rosales and Haan2006) and their role in disease transmission (Jones et al., Reference Jones, Patel, Levy, Storeygard, Balk, Gittleman and Daszak2008). Much of this negative messaging is influenced by livestock production practices and food consumption patterns in the Global North. Industrial production practices have serious environmental externalities including GHG emissions and pollution of air and water. Much of the feed used in such systems could be more efficiently used if directly consumed by humans (Wilkinson, Reference Wilkinson2011). Furthermore, levels of animal source food consumption in the Global North are much higher than in the Global South and this brings a range of health issues. Livestock production in SSA is a different story. In SSA, livestock are an integral component of mixed system agriculture as indicated above. They play key roles in the livelihoods of much of the rural population. None-the-less environmental consequences of livestock production on the continent cannot be ignored.

Trade-offs associated with livestock’s roles in sustainable agriculture

Limited information is available about how far intensification can be taken without too many internal and external detrimental effects. System internal trade-offs look at how limited resources (e.g. land, labour, crop residues, cash) can be allocated across crop and livestock production (and off-farm activities), and thereby provide information on how far current systems can intensify. The crop residue for fodder v. for soil amendment debate has been quite intensive given the push for conservation agriculture (e.g. Giller et al., Reference Giller, Corbeels, Nyamangara, Triomphe, Affholder, Scopel and Tittonell2009; Valbuena et al., Reference Valbuena, Erenstein, Homann-Kee Tui, Abdoulaye, Claessens, Duncan, Gérard, Rufino, Teufel, van Rooyen and van Wijk2012). For example, work by Rusinamhodzi et al. (Reference Rusinamhodzi, Corbeels, Zingore, Nyamangara and Giller2013) showed that the crop residue fodder v. soil amendment trade-off is not strong, and that in central Zimbabwe about 25% to 50% of the crop residues can be returned to the soil without having negative effects on cattle productivity. This would be enough to ensure good soil cover, and limit soil erosion. However, despite the need for these trade-off analyses (e.g. Klapwijk et al., Reference Klapwijk, van Wijk, Rosenstock, van Asten, Thornton and Giller2014) few other studies are available that explore these internal, resource constraint-driven, trade-offs. Externally, performance indicator-driven trade-off analyses are even less available beyond studies that show that trade-offs exist between production intensification and for example GHG emissions. Typically, in the low input systems of many low-income countries there is a large scope to improve emission intensities (i.e. the GHG emission per unit of livestock product produced) while intensifying production, but it is unclear in many systems up to what level production can be increased while still reducing emission intensity. In absolute emission terms investment in increasing the productivity of the existing cattle herd is attractive, as the animals are already there and emissions already take place. Improved feeding of these cattle will increase absolute amount of emissions (e.g. Herrero et al., Reference Herrero, Havlik, Valin, Notenbaert, Rufino, Thornton, Blummel, Weiss, Grace and Obersteiner2013) but not at the same levels that it would take to achieve similar levels of improved total production through expansion of a low productivity herd. Work by Amole et al. (Reference Amole, Zijlstra, Descheemaeker, Ayantunde and Duncan2017) and Rufino et al. (Reference Rufino, Herrero, van Wijk, Hemerik, De Ridder and Giller2009) has shown that large production increases can be achieved by relatively small changes in livestock diets. Also the low productivity of the grasslands in many agro-pastoral regions (e.g. Rufino et al., Reference Rufino, Dury, Tittonell, van Wijk, Herrero, Zingore, Mapfumo and Giller2011) gives ample opportunity to increase livestock production (e.g. through agroforestry, incorporation of legumes or other better regulation of the access to land use to avoid overgrazing). Given the fact that demand for livestock products will rise sharply over the coming decades, this information is essential to determine where investments in livestock products can be both efficient without further major negative environmental effects.