Recent energy security strategies, investment opportunities and energy policies have led to an escalation in biofuel consumption at the expenses of food crops and pastureland. To evaluate the important impacts of biofuels on food security, the food-energy nexus needs to be investigated in the context of its linkages with the overall human appropriation of land and water resources. Here we provide a global assessment of biofuel crop production, reconstruct global patterns of biofuel crop/oil trade and determine the associated displacement of water and land use. We find that bioethanol is mostly produced with domestic crops while 36% of biodiesel consumption relies on international trade, mainly from Southeast Asia. Altogether, biofuels rely on about 2-3% of the global water and land used for agriculture, which could feed about 30% of the malnourished population. We evaluate the food-energy tradeoff and the impact an increased reliance on biofuel would have on the number of people the planet can feed.
The synthesis of biofuels from plant biomass (mostly crops) offers the opportunity to rely on energy from geologically recent carbon as an alternative to fossil fuel1. The two main types of biofuels used for transportation are bioethanol and biodiesel. The former is made from sugar and starchy crops (Fig. 1A) and can be blended with gasoline, while the latter is produced using organic fats and vegetable oils (Fig. 1B) and can be blended with petrol diesel1.
In recent years, rising interest in biofuel production has resulted both from the increase in oil prices and new U.S. and E.U. energy policies mandating a certain degree of reliance on renewable energy as a strategy to curb greenhouse gas (GHG) emissions from the transport sector2,3,4. Biofuels may contribute to the enhancement of energy security in countries lacking direct access to fossil fuel deposits, the reduction of greenhouse gas (GHG) emissions, and a more profitable use of crops than in the food market where the same agricultural products would often be less valued.
The production of biofuel crops, however, can also have negative impacts on the environment, particularly through land use change and deforestation5,6,7,8,9,10. Moreover, biofuels require water and land resources11,12 that could otherwise be used for the production of food13,14 and ecosystem goods and services. Therefore, the competing needs for land and water resources by food and biofuel production are at the forefront of the energy-food debate15,16, which is fueled by recent food crises and associated spikes in food prices17,13,4. As a result, a number of outstanding questions on the energy-food nexus have arisen, including the number of people who could be fed by the crops used for biofuels; the extent to which these crops, if used for food consumption in the producing countries, could alleviate malnutrition; and whether bioenergy production entails an important displacement of land use18 through its reliance on the trade of feedstock or vegetable oil.
Between 2000 and 2008 the consumption of alcohol for non-food uses (“other uses”, the FAO data sets)19 (i.e., bioethanol) more than doubled in the USA and underwent a five-fold increase in Brazil, concurrently with the global increase in bioethanol consumption reported by OECD/FAO20. Overall, in 2013 about 86 million tons of biofuels were consumed globally, including 65 million tons of bioethanol and 21 of biodiesel. We estimate that in 2013 1.91 × 106 TJ/y of bioethanol and 0.82 × 106 TJ/y of biodiesel energy were produced worldwide (Table 1), claiming an area of about 41.3 million ha, which accounts for about 4% of the global arable area, consistent with findings by14. Biofuel production consumed 216 billion m3 of water, which corresponds to about 3% of the global water consumption for food production21. Our results also show that, while the water footprint of biodiesel and bioethanol energy are overall comparable, the land footprint of biodiesel is on average more than 100% greater than that of bioethanol (Table 2). These values, however, vary substantially, depending on the crop and geographic location.
Our findings show that bioethanol is produced mostly with sugarcane and maize followed by wheat, sugarbeet and sorghum (Fig. S1A). Because of its higher ethanol yield, maize accounts for 67% of the global bioethanol supply (Fig. S1B). However, while sugarcane is by far the highest contributor to bioethanol production (in terms of crop biomass), it is not the greatest water consumer because bioethanol produced from maize and wheat has a greater water footprint11,12 (Fig. S1C). Thus the different bioethanol crops used by producing countries explain their different use of resources (water, land, and food equivalent) (Fig. 2). The impact of bioethanol production is also evaluated in terms of the number of people who could be fed by bioethanol crops (Fig. 2D). We find that about 200 million people could be fed by the agricultural resources used to meet the bioethanol demand in the countries listed in Table 1.
Biodiesel is produced in equal proportions with rapeseed, soybean and palm oil (Fig. S2A). These oils have comparable biodiesel yields, but different extraction rate (i.e., crop oil yield) resulting in the consumption of a double amount of soybean compared to rapeseed (Fig. S2B). The proportion of water consumed by each of these vegetable oils, however, is not the same: biodiesel produced with palm oil is the most water demanding11,12 (Fig. 3). Most of the global consumption of biodiesel takes place in OECD + EU27 countries (listed in the caption of Table S1).
The greatest biodiesel consumers are USA and Brazil, followed by France, Germany, and Italy (Fig. 3A). These countries (USA, France, Germany and Italy) rely mostly on rape-mustard seed and soybean oil (and, in smaller amounts, palm oil), as do most of the other OECD + EU27 countries. Different oil consumption patterns are found in Brazil, which strongly relies on soybean oil. Countries that rely more on soybean seed oil use (either domestically or internationally) more land per unit energy consumed (Table 2; Fig. 3B). Because oil palm is a very high-yield crop, soybean oil and rape-mustard seed oil consumption are the main contributors to the land footprint of biodiesel energy (Table 2; Fig. 3B). An analysis based on per capita calorie requirements and the caloric content of biodiesel crops shows that about 70 million people could be fed by the food calories of the vegetable oils used for biodiesel production in the top 29 consumer countries that account for 97% of the global biodiesel consumption (Table 1; Fig. 3D).
The amounts of feedstock determined with the approach used in this study are in agreement with those reported by other sources. For example ANP22 reports the use of 2,041 × 103 m3 of soybean oil for biodiesel consumption in Brazil, while the data sources and methods used in this paper lead to an estimate of 2,480 × 103 m3. In the case of Europe, USDA-GAIN23 reports for rape-seed oil a consumption of 5,770 × 103 m3, which favorably compares with our estimate of 6,097 × 103 m3, while for soybean oil USDA-GAIN reports 850 × 103 m3, in overall agreement with our estimate 1060 × 103 m3. Likewise, USDA-GAIN reports a combined estimate for palm oil and used cooking oil of 2,920 × 103 m3, while our analyses show a value of 3,425 × 103 m3. There is an overall agreement among these sources within a 10–20% tolerance.
On average, biodiesel requires about the same amount of water resources but more land than bioethanol (Table 2). The direct impact of biodiesel on food security is similar to that of bioethanol, if evaluated in terms of number of people who could be fed per unit of biofuel energy (Table 2). However, because the global production of biodiesel is overall smaller than that of bioethanol, the impact of bioethanol on the number of people who could be fed is greater (Figs 2D and 3D).
Dependence on international trade
The natural resources used for biofuel production are partly available domestically in the country where the biofuel is consumed and partly (virtually) imported from other countries that produce and export feedstock for bioenergy. Globally, 97% of the water footprint and 96% of the land footprint of bioethanol production are internal. For the external portion of these footprints the associated global patterns of trade are dominated by Japan’s imports from the U.S.A. and Australia and trade partnerships internal to South America (Fig. 4).
In the case of biodiesel we were able to trace imports only for the aggregate of OECD/EU27 countries rather than for each country individually (see Supplementary Information). For this group of countries, 59% of the water footprint and 80% of the land footprint of biodiesel were internal. Thus, while most of land used to produce bioethanol is internal to the countries where it is consumed, in the case of biodiesel there is a stronger reliance on trade. However, even though bioethanol imports are still just a fraction of the global production, the energy flows associated with biodiesel trade are only about five times those for bioethanol because of the overall greater worldwide consumption of bioethanol (Fig. 4). The major energy flows related to biodiesel are from Malaysia, Indonesia and Papua New Guinea because of palm oil trade. There are also other important flows from South America (soybean and rape-mustard seed oil) and Canada, (rape-mustard seed oil) (Fig. 4). The European Union is the biggest importer (Fig. 4). Most of the virtual water trade (75%) associated with the biodiesel market is contributed by palm oil, while the virtual water trade of mustard and rapeseed oil tends to occur within the OECD + EU27 country group and cannot be resolved by our analysis (see Supplementary Materials).
The environmental impacts of European palm oil imports from Malaysia and Indonesia (Fig. 4 and S3) have been highlighted by a number of recent studies. Such impacts include high deforestation rates and large carbon emissions in Malaysia and Indonesia due to oil palm plantations8,5 as well as losses of habitat and threats to biodiversity24. In response, the European Union has taken some action to limit these unwanted effects on the environment25. For instance, biofuels produced from feedstocks grown on land with “high biodiversity value” (e.g., primary forests, peatlands, wetlands, certain woodlands and grassland) are not accepted under E.U. renewable energy mandates. The direct and indirect effects of biofuel production on these ecosystems, however, remain difficult to verify26.
The Water-Food-Energy Nexus
First generation bioethanol (i.e., produced from food crops) is still the major contributor to the global biofuel supply. The production of second and third generation biofuels from cellulosic plant tissues or algae is overall negligible (but is expected to be substantial in the coming 10–20 years27,28), despite their lower water and land footprints, and their lack of competition with food production.
In addition to the environmental impacts, biofuel production has important societal implications that can be better understood by examining the energy-food-water nexus of biofuels. Crops used to produce 1 TJ of biofuel would be sufficient to feed 110 and 90 people in the case of bioethanol and biodiesel, respectively. Interestingly, bioethanol production uses as feedstock major staple crops (e.g., maize and wheat) that could be directly used as food. In the case of biodiesel the competition with food is partly mitigated by the growing reliance of the biofuel industry on recycled cooking oil (up to 88% in the case of the U.K.29). At the global scale, we find that about 280 million people (i.e., more than one fourth of the malnourished population in the world30) could be fed with the crop calories used for biofuels in 2013. We stress, however, that this is not the number of people that would likely see an improvement in their access to food, should biofuel use be reduced to zero. Clearly, there are important economic and policy drivers underlying the current trends in biofuel consumption that are not accounted for in our 1:1 replacement of biofuel with food crops. Regardless, these numbers highlight the important contrast between biofuel production (which provides only 4 percent of energy needed by the transport sector and 0.2% of the global energy use in all sectors31), and food security (which could be strongly enhanced by biofuel crops). This fact calls for revisions to current climate change mitigation policies based on biofuels, as more recently recommended by the E.U.25. On April 2015 the European Parliament approved a reform of the Renewable Energy Directive (RED), which includes a 7 percent cap on food crop based biofuels for the transport sector.
The water-food-energy nexus of biofuel consumption can be further analyzed by evaluating the tradeoff between the maximum number of people the planet could feed, and a partial conversion of the societal metabolism from fossil fuel reliance to renewable energy32,33,34. With the industrial revolution, human societies switched from a metabolism based only on solar energy (i.e., photosynthesis) to an increasing reliance on fossil fuels (i.e., solar energy from a geological past)33. Thanks to this reliance on fossil resources, humans have been able to increase the agricultural production and greatly enhance their access to energy and food35. Biofuels offer a mechanism through which society could reduce its reliance on fossil fuels. Our study as well as recent analyses of global food security14,36, however, have shown that the global agricultural land could not be sufficient to meet the current human demand for food and energy. How many people can be supported by the food and bioenergy the planet can produce?Assuming a 10% reliance on biofuels (b = 0.10) (E.U., 2009) and using the bioenergy footprint values determined by this study, we find (see Methods) that the area A can meet the food and energy requirements of 6.7 billion people with the current average global food and energy demand. However, patterns of economic development show shifts toward higher energy consumption rates and more calorie demanding diets (e.g., more meat) as societies become more affluent37. To evaluate the impact of these increasing trends in food and energy demand, we recalculate the population size that could be sustained (100% food and 10% transport energy) by the same agricultural area, A, using average consumption rates characteristic of the E.U. (see Methods); in these conditions the population size would be P = 4.8 billion people, which would decrease to P = 4.4 billion people with b = 0.20 and P = 2.5 billion people with 100% reliance on biofuels for transport energy (b = 1).
Despite their being based only on average yields and consumption rates, these calculations allow us to relate population size to its food and energy demand, and dependency on fossil fuels. These results highlight how the societal reliance on fossil fuels cannot be reverted by first generation bioethanol without undermining the food security of human societies. It should be stressed that the competition between food and biofuels is expected to become even more intense in the near future, with the world’s population predicted to reach 9 billion by 2050.
The potential development of second and third generation biofuels is an important step in the direction of mitigating the food-biofuel competition through new technologies relying on agricultural waste.
We use biofuel consumption data, inferred from the FAOSTAT database38, to determine the amounts and types of crops used for bioethanol and biodiesel production in each country or country group, while the total values of bioethanol and biodiesel production and consumption are taken from other sources (Table S1). Because the FAOSTAT database does not provide estimates of error or uncertainty, the degree of uncertainty around the estimates presented in this paper remains unknown. Our study reconstructs patterns of biofuel consumption and trade using FAO data38 and other reports (i.e. Eurostat database39, US Energy International Administration40, USDA-Foreign agricultural service-Global Agricultural Information Network,41 Epure42, UK Department for Transport29, French Environment and Energy Management Agency (ADEME)43, Swedish Energy Agency44, Italian Ministry of Economic Development45, Agência Nacional do Petróleo, Gás Natural e Biocombustíveis – ANP46), without assuming a percentage of biofuel blending with diesel or gasoline. It accounts for the effect of trade on the water and land footprint of biofuels and determines the internal and external portion of these footprints. Finally, it evaluates the extent to which biofuels can be used to reduce our societal reliance on fossil fuels, while maintaining levels of food production that are sufficient to meet the needs of the global population. For more details, see the Supplementary Materials.
How to cite this article: Rulli, M. C. et al. The water-land-food nexus of first-generation biofuels. Sci. Rep. 6, 22521; doi: 10.1038/srep22521 (2016).
Mosdale, D. M. In Biofuels: Biotechnology, Chemistry and Sustainable Development (ed. Mosdale, D. M. ), (CRC Press, Taylor and Francis, 2008).
U.S.A. Congress, Energy Independence and Security Act of 2007 (EISA). Pub L No. 110–140 (2007).
European Union, Directive 2009/28/EC of the European Parliament and of the Council of 23 April 2009 on the promotion of the use of energy from renewable sources and amending and subsequently repealing Directives 2001/77/EC and 2003/30/EC (2009).
Sorda, G., Banse, M. & Kemfert, C., An overview of biofuel policies across the world, Energ Policy. 38, 6977–6988, 10.1016/j.enpol.2010.06.066 (2010).
Fargione, J., Hill, J., Tilman, D., Polasky, S. & Hawthorne, P. Land clearing and the biofuel carbon debt. Science. 319, 1235–1238, 10.1126/science.1152747 (2008).
Fitzherbert, E. B. et al. How will oil palm expansion affect biodiversity? Trends Ecol Evol. 23, 538–545, 10.1016/j.tree.2008.06.012 (2008).
Lima, M., Skutsch, M. & de Medeiros Costa, G. Deforestation and the social impacts of soy for biodiesel: perspectives of farmers in the south Brazilian Amazon. Ecol Soc. 16(4): 04, 10.5751/ES-04366-160404 (2011).
Carlson, K. M. et al. Committed carbon emissions, deforestation, and community land conversion from oil palm plantation expansion in West Kalimantan, Indonesia. Proc Natl Acad Sci USA 109, 7559–7564, 10.1073/pnas.1200452109 (2012).
Achten, M. J. W. & Verchot, L. V. Implications of biodiesel-induced land-use changes for CO2emissions: case studies in tropical America, Africa, and Southeast Asia. Ecol and Soc. 16(4): 14, 10.5751/ES-04403-160414 (2011).
Havlk, P. et al. Global land-use implications of first and second generation biofuel targets. Energ Policy. 39, 5690–5702, 10.1016/j.enpol.2010.03.030 (2011).
Gerbens-Leenes, P. W., Hoekstra, A. Y. & van der Meer, Th.H. The water footprint of bioenergy. Proc Natl Acad Sci USA 106(25), 10219–10223, 10.1073/pnas.0812619106 (2009).
Gerbens-Leenes, P. W., van Lienden, A. R., Hoekstra A. Y. & van den Meer, T. H. Biofuel scenarios in a water perspective: the global blue and green water footprint of road transport in 2030. Global Environ Chang. 22(3), 764–775, 10.1016/j.gloenvcha.2012.04.001 (2012).
FAO-OECD, Food and Agriculture Organization/Organization for Economic Co-operation and Development: Price Volatility in Food and Agricultural Markets: Policy Responses. (Food and Agriculture Organization of the United Nations, 2011).
Cassidy, E. S., West, P. C., Gerber, J. S. & Foley, J. A. Redefining agricultural yields: from tonnes to people nourished per hectare. Environ Res Lett. 8, 034015, 10.1088/1748-9326/8/3/034015 (2013).
Smith P. et al. Competition for land. Phil Trans R Soc B: Biol Sci 365, 2941–2957, 10.1098/rstb.2010.0127 (2010).
Lambin, E. F. & Meyfroidt, P. Global land use change, economic globalization, and the looming land scarcity. Proc. Natl Acad. Sci. USA 108, 3465–3472, 10.1073/pnas.1100480108 (2011).
Brown, L. R. In Full Planet, Empty Plates (W.W. Norton & Company 2012).
Meyfroidt, P. et al. Globalization of land use: distant drivers of land change and geographic displacement of land use. Curr Opin Environ Sustain 5, 1–7, 10.1016/j.cosust.2013.04.003 (2013).
Food and Agriculture Organization of the United Nations (FAO) in Food Balance Sheets, A Handbook. (Food and Agriculture Organization of the United Nations 2001).
OECD/ Food and Agriculture Organization of the United Nations in OECD- FAO Agricultural Outlook 2013-2022, (OECD publishing 2013).
Carr, J. A., D’Odorico, P., Laio, F. & Ridolfi, L. Recent history and geography of virtual water trade, PLoS One 8, e55825, 10.1371/journal.pone.0055825 (2013).
Agência Nacional do Petróleo, Gás Natural e Biocombustíveis – ANP, Statistic on biofuel, Available at http://www.anp.gov.br/ (Date of access: 10/07/2015).
Flach, B. et al. in Biofuels annual-UE28 2015, USDA Foreign agricultural service GAIN Report Number NL5028. Available at http://gain.fas.usda.gov/Recent%20GAIN%20Publications/Biofuels%20Annual_The%20Hague_EU-28_7-15-2015.pdf (Date of access: 20/07/2015).
United Nations Environment Programme, Towards sustainable production and use of resources: Assessing Biofuels, UNEP, Division of Technology Industry and Economics, Paris (2009).
European Union, Proposal for a directive of the European Parliament and of the council amending Directive 98/70/EC relating to the quality of petrol and diesel fuels and amending Directive 2009/28/EC on the promotion of the use of energy from renewable sources, European Commission, Bruxelles (2012).
Hermele, K. In The Appropriation of Ecological Space. Agrofuels, unequal exchange and environmental load displacements, pp. 158, (ed. Rutledge 2014).
OECD/ Food and Agriculture Organization of the United Nations in OECD- FAO Agricultural Outlook 2014-2023, (OECD publishing 2014).
Gerbens-Leenes, P. W., Xu, L., de Vries, G. J. & Hoekstra A. Y. The blue water footprint and land use of biofuels from algae, Water Resour Res, 50, 8549–8563, 10.1002/2014WR015710 (2014).
UK department for Transport, in RTFO 2012–2014 year four report (ed. UK: Department for Transport 2014).
FAO, IFAD & WFP, In The State of Food Insecurity in the World 2014. Strengthening the enabling environment for food security and nutrition. (ed. FAO 2014).
International Energy Agency, IEA database, Available at http://www.iea.org/statistics/statisticssearch/ (Date of access: 03/03/2015).
Giampietro, M. & Mayumi, K. Multiple-scale integrated assessment of societal metabolism: Introducing the approach, Popul Environ 22(2), 109–153, 10.1023/A:1026691623300 (2000).
Scheidel, A. & Sorman, A. H. Energy transitions and the global land rush: Ultimate drivers and persistent consequences. Global Environ Chang 22, 588–595, 10.1016/j.gloenvcha.2011.12.005 (2012).
Rosegrant, M. W. & Msangi, S. Consensus and Contention in the Food-Versus-Fuel Debate. Annu Rev Env Resour 39, 271–294, 10.1146/annurev-environ-031813-132233 (2014).
Erisman, J. W., Sutton, M. A., Galloway, J., Klimont, Z. & Winiwarter, W., How a century of ammonia synthesis changed the world, Nat Geosci 1, 636–639, 10.1038/ngeo325 (2008).
Davis, K. F., D’Odorico, P. & Rulli, M. C. Moderating diets to feed the future. Earth’s Future 2, 10, 559–565, 10.1002/2014EF000254 (2014).
Tilman, D., Balzer, C., Hill, J. & Befort, B. L. Global food demand and the sustainable intensification of agriculture. Proc Natl Acad Sci USA 108, 20260–20264, 10.1073/pnas.1116437108 (2011).
Food and Agriculture Organization of the United Nations. Faostat Database (2009) Available at http://faostat3.fao.org/faostat-gateway/go/to/download/FB/*/E (Date of Access: 22/01/2014).
Eurostat database, http://ec.europa.eu/eurostat/en/data/database (Date of access: 10/07/2015).
US Energy International Administration (EIA) database, Available at http://www.eia.gov/ (Date of access: 15/07/2015).
USDA-Foreign agricultural service-Global Agricultural Information Network Available at http://gain.fas.usda.gov/Pages/Default.aspx (Date of access: 15/07/2015).
EPURE statistics [Available at http://www.epure.org/resources/statistics (Date of access: 15/07/2015)].
Charles, C., Keller, M. & Moerenhout, T. Biofuels-At what cost?A review of costs and benefits of France’s biofuel policies. Research Report (2013) International Institute for Sustainable Development -Global Subsidies Initiative. Available at https://www.iisd.org/gsi/sites/default/.../bf_costeffectiveness_france.pdf (Date of access: 15/07/2015).
Swedish Energy Agency, Sustainable biofuel and bioliquids Technical Report (2013) Available at https://energimyndigheten.a-w2m.se/FolderContents.mvc/DownloadResourceId=3037 (Date of access: 15/07/2015).
Italian Ministry of Economic Development, statistics on biofuel, Available at http://www.sviluppoeconomico.gov.it/index.php/it/ (Date of access: 03/03/2015)].
Agência Nacional do Petróleo, Gás Natural e Biocombustíveis – ANP, Statistic on biofuel, Available at http://www.anp.gov.br/(Dateofaccess:03/03/2015) (Date of access: 03/03/2015).
PD was funded by the National Socio-Environmental Synthesis Center, NSF DBI-1052875.
The authors declare no competing financial interests.
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Rulli, M., Bellomi, D., Cazzoli, A. et al. The water-land-food nexus of first-generation biofuels. Sci Rep 6, 22521 (2016). https://doi.org/10.1038/srep22521
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