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      The Role of Latin America’s Land and Water Resources for Global Food Security: Environmental Trade-Offs of Future Food Production Pathways

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          Abstract

          One of humanity’s major challenges of the 21st century will be meeting future food demands on an increasingly resource constrained-planet. Global food production will have to rise by 70 percent between 2000 and 2050 to meet effective demand which poses major challenges to food production systems. Doing so without compromising environmental integrity is an even greater challenge. This study looks at the interdependencies between land and water resources, agricultural production and environmental outcomes in Latin America and the Caribbean (LAC), an area of growing importance in international agricultural markets. Special emphasis is given to the role of LAC’s agriculture for (a) global food security and (b) environmental sustainability. We use the International Model for Policy Analysis of Agricultural Commodities and Trade (IMPACT)—a global dynamic partial equilibrium model of the agricultural sector—to run different future production scenarios, and agricultural trade regimes out to 2050, and assess changes in related environmental indicators. Results indicate that further trade liberalization is crucial for improving food security globally, but that it would also lead to more environmental pressures in some regions across Latin America. Contrasting land expansion versus more intensified agriculture shows that productivity improvements are generally superior to agricultural land expansion, from an economic and environmental point of view. Finally, our analysis shows that there are trade-offs between environmental and food security goals for all agricultural development paths.

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          Reconciling food production and biodiversity conservation: land sharing and land sparing compared.

          The question of how to meet rising food demand at the least cost to biodiversity requires the evaluation of two contrasting alternatives: land sharing, which integrates both objectives on the same land; and land sparing, in which high-yield farming is combined with protecting natural habitats from conversion to agriculture. To test these alternatives, we compared crop yields and densities of bird and tree species across gradients of agricultural intensity in southwest Ghana and northern India. More species were negatively affected by agriculture than benefited from it, particularly among species with small global ranges. For both taxa in both countries, land sparing is a more promising strategy for minimizing negative impacts of food production, at both current and anticipated future levels of production.
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            International trade drives biodiversity threats in developing nations.

            Human activities are causing Earth's sixth major extinction event-an accelerating decline of the world's stocks of biological diversity at rates 100 to 1,000 times pre-human levels. Historically, low-impact intrusion into species habitats arose from local demands for food, fuel and living space. However, in today's increasingly globalized economy, international trade chains accelerate habitat degradation far removed from the place of consumption. Although adverse effects of economic prosperity and economic inequality have been confirmed, the importance of international trade as a driver of threats to species is poorly understood. Here we show that a significant number of species are threatened as a result of international trade along complex routes, and that, in particular, consumers in developed countries cause threats to species through their demand of commodities that are ultimately produced in developing countries. We linked 25,000 Animalia species threat records from the International Union for Conservation of Nature Red List to more than 15,000 commodities produced in 187 countries and evaluated more than 5 billion supply chains in terms of their biodiversity impacts. Excluding invasive species, we found that 30% of global species threats are due to international trade. In many developed countries, the consumption of imported coffee, tea, sugar, textiles, fish and other manufactured items causes a biodiversity footprint that is larger abroad than at home. Our results emphasize the importance of examining biodiversity loss as a global systemic phenomenon, instead of looking at the degrading or polluting producers in isolation. We anticipate that our findings will facilitate better regulation, sustainable supply-chain certification and consumer product labelling.
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              Exploring global changes in nitrogen and phosphorus cycles in agriculture induced by livestock production over the 1900-2050 period.

              Crop-livestock production systems are the largest cause of human alteration of the global nitrogen (N) and phosphorus (P) cycles. Our comprehensive spatially explicit inventory of N and P budgets in livestock and crop production systems shows that in the beginning of the 20th century, nutrient budgets were either balanced or surpluses were small; between 1900 and 1950, global soil N surplus almost doubled to 36 trillion grams (Tg) · y(-1) and P surplus increased by a factor of 8 to 2 Tg · y(-1). Between 1950 and 2000, the global surplus increased to 138 Tg · y(-1) of N and 11 Tg · y(-1) of P. Most surplus N is an environmental loss; surplus P is lost by runoff or accumulates as residual soil P. The International Assessment of Agricultural Knowledge, Science, and Technology for Development scenario portrays a world with a further increasing global crop (+82% for 2000-2050) and livestock production (+115%); despite rapidly increasing recovery in crop (+35% N recovery and +6% P recovery) and livestock (+35% N and P recovery) production, global nutrient surpluses continue to increase (+23% N and +54% P), and in this period, surpluses also increase in Africa (+49% N and +236% P) and Latin America (+75% N and +120% P). Alternative management of livestock production systems shows that combinations of intensification, better integration of animal manure in crop production, and matching N and P supply to livestock requirements can effectively reduce nutrient flows. A shift in human diets, with poultry or pork replacing beef, can reduce nutrient flows in countries with intensive ruminant production.
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                Author and article information

                Contributors
                Role: Academic Editor
                Journal
                PLoS One
                PLoS ONE
                plos
                plosone
                PLoS ONE
                Public Library of Science (San Francisco, CA USA )
                1932-6203
                24 January 2015
                2015
                : 10
                : 1
                : e0116733
                Affiliations
                [1 ]Research Centre for the Management of Agricultural and Environmental Risks (CEIGRAM), Department of Agricultural Economics and Social Sciences, Universidad Politécnica de Madrid, Madrid, Spain
                [2 ]Water Observatory, Botin Foundation, Madrid, Spain
                [3 ]Environment and Production Technology Division, International Food Policy Research Institute (IFPRI), Washington, District of Columbia, United States of America
                [4 ]Center for the Environment, Harvard University, Cambridge, Massachusetts, United States of America
                Potsdam Institute for Climate Impact Research, GERMANY
                Author notes

                Competing Interests: The authors have declared that no competing interests exist.

                Conceived and designed the experiments: IF CR BW HX NDM. Performed the experiments: IF BW HX GP. Analyzed the data: IF BW HX CR AG. Contributed reagents/materials/analysis tools: IF BW HX GP NDM CR AG. Wrote the paper: IF BW HX. Scenario construction: IF CR AG. IMPACT model runs and validation: GP IF. Contributed to the discussion: IF BW HX NDM CR AG. Data collection: IF BW HX NDM.

                Article
                PONE-D-14-31149
                10.1371/journal.pone.0116733
                4305321
                25617621
                4c10e2f9-6830-484d-ba42-3b80a61ee3ea
                Copyright @ 2015

                This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited

                History
                : 11 July 2014
                : 12 December 2014
                Page count
                Figures: 8, Tables: 1, Pages: 24
                Funding
                Funding provided by Fundación Botin—CEIGRAM, Universidad Politécnica de Madrid (grant numbers: P12 0220c-003 and P13 0220c-008; URLs: www.ceigram.upm.es and www.fundacionbotin.org): IF BW AG, CGIAR Research Program on Water, Land and Ecosystems: HX GP CR and NDM received no specific funding for this work. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
                Categories
                Research Article
                Custom metadata
                All relevant data and model equations concerning IMPACT baseline model runs can be obtained from http://www.ifpri.org/book-751/ourwork/program/impact-model. The following data has been deposited to http://thedata.harvard.edu/dvn/dv/IFPRI: baseline crop and livestock yield, crop area harvested and livestock number growth rates; changes in fertilizer application (2050), cultivated land and pasture area (year 2000–2050); basin efficiencies by FPU (2000, 2010, 2050); trade parameters PSE, CSE, MI. The following data obtained from http://www.earthstat.org: Base year fertilizer application rates (year 2000), Yields and area of seven mayor crops for yield gap analysis (year circa 2000), Attainable yield estimates of seven mayor crops for yield gap analysis (year 2000). 5 arc minute geographical dataset on aboveground carbon stocks by main land use types can be obtained from: http://cdiac.ornl.gov/; 5 arc minute resolution global soil organic carbon map in the top 1 m can be obtained from: http://eusoils.jrc.ec.europa.eu/esdb_archive/octop/Global.html. 1 km resolution bird species presence can be obtained from: http://sedac.ciesin.columbia.edu/data/set/species-v1-americas-bird-presence; 300 meter resolution 2009 Global Land Cover and Land Use Map can be obtained from: http://due.esrin.esa.int/globcover/.

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