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Systemic Feedbacks in Global Land Use

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Part of the book series: Human-Environment Interactions ((HUEN,volume 5))

Abstract

Land is a key resource, not only for human societies but also for all organisms—animals, plants and microorganisms—that inhabit terrestrial ecosystems worldwide. Humans use land for at least three purposes: resource supply, waste repository and living space (i.e., the area required for production, consumption, transport, recreation and many other activities). Land use involves the ‘colonization of ecosystems’, that is, purposive interventions into terrestrial ecosystems that aim to support these functions, usually by transforming natural into managed ecosystems (e.g., agro-ecosystems , managed forests, urban systems). Increasingly, land use also aims at other services, such as the conservation of habitats , species or ecosystems or increased carbon sequestration . Maximization of one function, such as biomass supply , often affects other functions, such as carbon sequestration or conservation. Along with the growth of the world population and its per-capita consumption, trade-off s among different functions are becoming more important. A particularly relevant example is the trade-off between food and fuel that has become apparent in the last few years as policies promoting bioenergy on agricultural lands have gained momentum. Although some of these trade-offs can only be mitigated but not completely avoided (e.g., biomass production requires limited resources such as productive area and water), a sociometabolic approach can help identify potential synergies. For example, the use of wastes, by-products and residues (‘cascade utilization ’) may help to increase biomass use efficiency and generate several outputs without resulting in resource competition . This chapter discusses such trade-offs and synergies in global land use with a view toward issues of resource supply (mainly food and energy) as well as various ecological conservation aspects (e.g., biodiversity conservation, carbon sequestration and environmentally less-demanding agricultural technologies).

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Notes

  1. 1.

    In this chapter, we discuss a land surface of approximately 130 million km²; that is, all of the earth’s land outside Greenland and Antarctica.

  2. 2.

    We also analyzed variants of the ‘baseline diet’ by tweaking the production of animal products (a) toward pigs and poultry (+50 %, milk and ruminant meat reduced accordingly) and (b) toward ruminants by reducing pig and poultry products by 50 % and increasing ruminants accordingly. In both cases, the total consumption of animal products was assumed to remain the same as in the baseline.

  3. 3.

    Pets could not be modeled explicitly due to a lack of data. For the year 2000, their feed intake is included in the animal production/consumption data. Implicitly, this means they are scaled up/downward with changes assumed in animal product consumption in the different diet variants.

  4. 4.

    BioBaM distinguishes 11 world regions, seven crop aggregates and two different animal production systems (ruminants, monogastrics). The results can be disaggregated in geographic information system (GIS) grids with a five-minute geographic resolution (ca. 10 km at the equator) based on data by Erb et al. (2007).

  5. 5.

    In all scenarios, urban and infrastructure areas are assumed to grow by +24 % until 2050. Cropland area demand is calculated from food demand according to the variants of yields and feeding efficiencies. The world population in 2050 is assumed to be nine billion.

  6. 6.

    Exceptions include raised bogs, which are able to create long-term carbon sinks because of the exclusion of oxygen in the soil.

References

  • Blanco-Canqui, H., & Lal, R. (2009). Crop residue removal impacts on soil productivity and environmental quality. Critical Reviews in Plant Sciences, 28, 139–163.

    Article  CAS  Google Scholar 

  • Bouwman, A., Van der Hoek, K., Eickhout, B., & Soenario, I. (2005). Exploring changes in world ruminant production systems. Agricultural Systems, 84, 121–153.

    Article  Google Scholar 

  • Braat, L. C., & de Groot, R. (2012). The ecosystem services agenda: bridging the worlds of natural science and economics, conservation and development, and public and private policy. Ecosystem Services, 1, 4–15.

    Article  Google Scholar 

  • Burney, J. A., Davis, S. J., & Lobell, D. B. (2010). Greenhouse gas mitigation by agricultural intensification. Proceedings of the National Academy of Sciences, 107, 12052–12057.

    Article  CAS  Google Scholar 

  • Butsic, V., Radeloff, V. C., Kuemmerle, T., & Pidgeon, A. M. (2012). Analytical solutions to trade-offs between size of protected areas and land-use intensity. Conservation Biology, 26(5):883–893.

    Google Scholar 

  • Coelho, S., Agbenyega, O., Agostini, A., Erb, K.-H., Haberl, H., Hoogwijk, M., et al. (2012). Land and water: Linkages to bioenergy. In: T. Johansson., A. Patwardhan., N. Nakicenonivc, Gomez-Echeverri (Eds.), Global energy assessment. International institute of applied systems analysis (IIASA) (pp. 1459–1525). Cambridge University Press, Cambridge, UK.

    Google Scholar 

  • Ellis, E. C., Klein Goldewijk, K., Siebert, S., Lightman, D., & Ramankutty, N. (2010). Anthropogenic transformation of the biomes, 1700 to 2000. Global Ecology and Biogeography, 19, 589–606.

    Google Scholar 

  • Erb, K.-H., Gaube, V., Krausmann, F., Plutzar, C., Bondeau, A., & Haberl, H. (2007). A comprehensive global 5 min resolution land-use data set for the year 2000 consistent with national census data. Journal of Land Use Science, 2, 191–224.

    Article  Google Scholar 

  • Erb, K.-H., Haberl, H., Krausmann, F., Lauk, C., Plutzar, C., & Steinberger, J. K. (2009). Eating the planet: Feeding and fuelling the world sustainably, fairly and humanely—a scoping study. Social ecology working paper no. 116, Vienna, Potsdam.

    Google Scholar 

  • Erb, K.-H., Mayer, A., Kastner, T., Sallet, K. E., & Haberl, H. (2012). The impact of industrial grain fed livestock production on food security: An extended literature review. Institute of social ecology, working paper social ecology no. 136, Vienna.

    Google Scholar 

  • Essl, F., & Rabitsch, W. (2013). Biodiversität und Klimawandel. Springer, Heidelberg: Auswirkungen und Handlungsoptionen für den Naturschutz in Mitteleuropa.

    Book  Google Scholar 

  • FAO. (2006). World agriculture: Towards 2030/2050—Interim report. Prospects for food, nutrition, agriculture and major commodity groups. Food and Agriculture Organization of the United Nations, Rome.

    Google Scholar 

  • FAO. (2013). The state of food insecurity in the world 2013; the multiple dimensions of food security. Rome, Italy: Food and Agriculture Organisation of the United Nations (FAO).

    Google Scholar 

  • Fischer-Kowalski, M., Haberl, H., Hüttler, W., Payer, H., Schandl, H., Winiwarter, V., et al. (1997). Gesellschaftlicher Stoffwechsel und Kolonisierung von Natur. Amsterdam: Ein Versuch in sozialer Ökologie. Gordon & Breach Fakultas.

    Google Scholar 

  • Godfray, H. C. J., Beddington, J. R., Crute, I. R., Haddad, L., Lawrence, D., Muir, J. F., et al. (2010). Food security: The challenge of feeding 9 billion people. Science, 327, 812–818.

    Article  CAS  Google Scholar 

  • Guzman, G. I., Gonzalez de Molina, M., & Alonso, A. M. (2011). The land cost of agrarian sustainability. An assessment. Land Use Policy, 28, 825–835.

    Article  Google Scholar 

  • Haberl, H., Erb, K.-H., Krausmann, F., Bondeau, A., Lauk, C., Müller, C., et al. (2011). Global bioenergy potentials from agricultural land in 2050: Sensitivity to climate change, diets and yields. Biomass and Bioenergy, 35, 4753–4769.

    Article  Google Scholar 

  • Haberl, H., & Geissler, S. (2000). Cascade utilization of biomass: Strategies for a more efficient use of a scarce resource. Ecological Engineering, 16, 111–121.

    Article  Google Scholar 

  • IAASTD. (2009). Agriculture at a crossroads. International assessment of agricultural knowledge, science and technology for development (IAASTD). Global report. Washington, D.C: Island Press.

    Google Scholar 

  • Krausmann, F., Erb, K.-H., Gingrich, S., Lauk, C., & Haberl, H. (2008). Global patterns of socioeconomic biomass flows in the year 2000: A comprehensive assessment of supply, consumption and constraints. Ecological Economics, 65, 471–487.

    Article  Google Scholar 

  • Lambin, E. F., & Meyfroidt, P. (2011). Global land use change, economic globalization, and the looming land scarcity. Proceedings of the National Academy of Sciences, 108, 3465–3472.

    Article  CAS  Google Scholar 

  • Maeder, P., Fliessbach, A., Dubois, D., Gunst, L., Fried, P., & Niggli, U. (2002). Soil fertility and biodiversity in organic farming. Science, 296, 1694–1697.

    Article  Google Scholar 

  • Millennium Ecosystem Assessment. (2005). Ecosystems and human well-being: Synthesis. Washington, DC: Island Press.

    Google Scholar 

  • Seufert, V., Ramankutty, N., & Foley, J. A. (2012). Comparing the yields of organic and conventional agriculture. Nature, 485, 229–234.

    Article  CAS  Google Scholar 

  • Smith, P., Haberl, H., Popp, A., Erb, K.-H., Lauk, C., Harper, R., et al. (2013). How much land based greenhouse gas mitigation can be achieved without compromising food security and environmental goals? Global Change Biology, 19, 2285–2302.

    Article  Google Scholar 

  • Thornton, P. K. (2010). Livestock production: Recent trends, future prospects. Philosophical Transactions of the Royal Society B: Biological Sciences, 365, 2853–2867.

    Article  Google Scholar 

  • Tilman, D., Balzer, C., Hill, J., & Befort, B. L. (2011). Global food demand and the sustainable intensification of agriculture. Proceedings of the National Academy of Sciences, 108, 20260–20264.

    Article  CAS  Google Scholar 

  • Turner, B. L., Lambin, E. F., & Reenberg, A. (2007). The emergence of land change science for global environmental change and sustainability. Proceedings of the National Academy of Sciences, 104, 20666–20671.

    Article  CAS  Google Scholar 

  • Winiwarter, V., & Gerzabeck, M. H. (2012). The challenge of sustaining soils: Natural and social ramifications of biomass production in a changing world. Interdisciplinary perspectives no. 1, Austrian Academy of Sciences Press, Vienna.

    Google Scholar 

References

  • Haberl, H., Erb, K.-H., Krausmann, F., Gaube, V., Bondeau, A., Plutzar, C., et al. (2007). Quantifying and mapping the human appropriation of net primary production in earth’s terrestrial ecosystems. Proceedings of the National Academy of Sciences, 104, 12942–12947.

    Article  CAS  Google Scholar 

  • Haberl, H., Erb, K.-H., & Krausmann, F. (2014). Human appropriation of net primary production: Patterns, trends, and planetary boundaries. Annual Review of Environment and Resources, 39, 363–391.

    Article  Google Scholar 

  • Imhoff, M. L., Bounoua, L., Ricketts, T., Loucks, C., Harriss, R., & Lawrence, W. T. (2004). Global patterns in human consumption of net primary production. Nature, 429, 870–873.

    Article  CAS  Google Scholar 

  • Körner, C. (2009). Biologische Kohlenstoffsenken: Umsatz und Kapital nicht verwechseln (Biological carbon sinks: Turnover must not be confused with capital). Gaia—Ecological Perspectives for Science and Society, 18, 288–293.

    Google Scholar 

  • Krausmann, F., Erb, K.-H., Gingrich, S., Haberl, H., Bondeau, A., Gaube, V., et al. (2013). Global human appropriation of net primary production doubled in the 20th century. Proceedings of the National Academy of Sciences, 110, 10324–10329.

    Article  CAS  Google Scholar 

  • Vitousek, P. M., Ehrlich, P. R., Ehrlich, A. H., & Matson, P. A. (1986). Human appropriation of the products of photosynthesis. BioScience, 36, 363–373.

    Article  Google Scholar 

  • Wright, D. H. (1990). Human impacts on energy flow through natural ecosystems, and implications for species endangerment. Ambio, 19, 189–194.

    Google Scholar 

Download references

Acknowledgements

Funding by the Austrian Science Fund (FWF) within the project P20812-G11, by the European Research Council within ERC Starting Grant 263522 LUISE and by the EU-FP7 project VOLANTE is gratefully acknowledged. This chapter was written in parts during Helmut Haberl’s research stay at the Integrative Research Institute on Transformation in Human-Environment Systems (IRI THESys) at Humboldt-Universität zu Berlin.

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Correspondence to Helmut Haberl .

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Haberl, H., Erb, KH., Kastner, T., Lauk, C., Mayer, A. (2016). Systemic Feedbacks in Global Land Use. In: Haberl, H., Fischer-Kowalski, M., Krausmann, F., Winiwarter, V. (eds) Social Ecology. Human-Environment Interactions, vol 5. Springer, Cham. https://doi.org/10.1007/978-3-319-33326-7_14

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