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Global Threats to Human Water Security and River Biodiversity

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Global Threats to Human Water Security and River Biodiversity ARTICLE doi:10.1038/nature09440 Global threats to human water security and river biodiversity C. J. Vo¨ro¨smarty1*, P. B. McIntyre2*{, M. O. Gessner3, D. Dudgeon4, A. Prusevich5, P. Green1, S. Glidden5, S. E. Bunn6, C. A. Sullivan7, C. Reidy Liermann8 & P. M. Davies9 Protecting the world’s freshwater resources requires diagnosing threats over a broad range of scales, from global to local. Here we present the first worldwide synthesis to jointly consider human and biodiversity perspectives on water security using a spatial framework that quantifies multiple stressors and accounts for downstream impacts. We find that nearly 80% of the world’s population is exposed to high levels of threat to water security. Massive investment in water technology enables rich nations to offset high stressor levels without remedying their underlying causes, whereas less wealthy nations remain vulnerable. A similar lack of precautionary investment jeopardizes biodiversity, with habitats associated with 65% of continental discharge classified as moderately to highly threatened. The cumulative threat framework offers a tool for prioritizing policy and management responses to this crisis, and underscores the necessity of limiting threats at their source instead of through costly remediation of symptoms in order to assure global water security for both humans and freshwater biodiversity. Water is widely regarded as the most essential of natural resources, yet pathways, as for pollution, but they also influence water systems in freshwater systems are directly threatened by human activities1–3 and distinct ways. Reservoirs, for example, convey few negative effects on stand to be further affected by anthropogenic climate change4.Water human water supply, but substantially impact on aquatic biodiversity systems are transformed through widespread land cover change, urb- by impeding the movement of organisms, changing flow regimes and anization, industrialization and engineering schemes like reservoirs, altering habitat. Similarly, non-native species threaten biodiversity irrigation and interbasin transfers that maximize human access to but are typically inconsequential to human water security. water1,5. The benefits of water provision to economic productivity2,6 are Here we report the results of a global-scale analysis of threats to fresh often accompanied by impairment to ecosystems and biodiversity, with water that, for the first time, considers human water security and potentially serious but unquantified costs3,7,8. Devising interventions to biodiversity perspectives simultaneously within a spatial accounting reverse these trends, including conventions9 and scientific assessments10 framework. Our focus is on rivers, which serve as the chief source of to protect aquatic biodiversity and ensure the sustainability of water renewable water supply for humans and freshwater ecosystems2,3.We delivery systems11, requires frameworks to diagnose the primary threats use river networks to redistribute the distinctive impacts of stressors on to water security at a range of spatial scales from local to global. human water security and biodiversity along a continuum from head- Water issues feature prominently in assessments of economic waters to ocean, capturing spatial legacy effects ignored by earlier development6, ecosystem services3, and their combination12–14. studies. Our framework incorporates all major classes of anthro- However, worldwide assessments of water resources2 rely heavily on pogenic drivers of stress and enables an assessment of their aggregate fragmented data often expressed as country-level statistics, seriously impact under often divergent value systems for biodiversity and limiting efforts to prioritize their protection and rehabilitation15. human water security. Enhancing the spatial resolution by orders-of- High-resolution spatial analyses have taken understanding of the magnitude over previous studies (using 309 latitude/longitude grids) human impact on the world’s oceans16,17 and the human footprint on allows us to more rigorously test previous assertions on the state of the land18 to a new level, but have yet to be applied to the formal assessment world’s rivers and to identify key sources of threat at sub-national process for freshwater resources2 despite a recognized need19,20. spatial scales that are useful for environmental management. Finally, The success of integrated water management strategies depends on we make the first spatial assessment of the benefits accrued from tech- striking a balance between human resource use and ecosystem pro- nological investments aimed at reducing threats to human water secur- tection2,9,10,21. To test the degree to which this objective has been ity, revealing previously unrecognized, global-scale consequences of advanced globally, and to assess its potential value in the future, local water management practices that are used extensively worldwide. requires systematic accounting. An important first step is to develop a spatial picture of contemporary incident threats to human water Global patterns of incident threat security and biodiversity, where the term ‘incident’ refers to exposure Using a global geospatial framework22, we merged a broad suite of to a diverse array of stressors at a given location. Many stressors individual stressors to produce two cumulative incident threat indices, threaten human water security and biodiversity through similar one for human water security and one for biodiversity. The resulting 1The Environmental CrossRoads Initiative, City University of New York, The City College of New York, New York, New York 10035, USA. 2School of Natural Resources and Environment, University of Michigan, Ann Arbor, Michigan 48109, USA. 3Department of Aquatic Ecology, Eawag: Swiss Federal Institute of Aquatic Science and Technology, and Institute of Integrative Biology (IBZ), ETH Zurich, 8600 Du¨ bendorf, Switzerland and Leibniz Institute of Freshwater Ecology and Inland Fisheries (IGB), 16775 Stechlin, Germany. 4Division of Ecology and Biodiversity, School of Biological Sciences, The University of Hong Kong, Hong Kong SAR, China. 5Water Systems Analysis Group, University of New Hampshire, Durham, New Hampshire 03824, USA. 6Australian Rivers Institute, Griffith University, Nathan, Queensland 4111, Australia. 7School of Environmental Science and Management, Southern Cross University, New South Wales 2480, Australia. 8School of Aquatic and Fishery Sciences, University of Washington, Seattle, Washington 98195, USA. 9Centre of Excellence in Natural Resource Management, The University of Western Australia, Albany 6330, Australia. {Present address: Center for Limnology, University of Wisconsin, Madison, Wisconsin 53706, USA. *These authors contributed equally to this work. 30 SEPTEMBER 2010 | VOL 467 | NATURE | 555 ©2010 Macmillan Publishers Limited. All rights reserved RESEARCH ARTICLE Incident human water security threat 0.2 0.6 1 0 0.4 0.8 No appreciable flow Incident biodiversity threat 0.2 0.6 1 0 0.4 0.8 No appreciable flow Figure 1 | Global geography of incident threat to human water security and generally moderate (mean | r | 5 0.34; n 5 253 comparisons). Regional maps biodiversity. The maps demonstrate pandemic impacts on both human water exemplify main classes of human water security threat (see main text and security and biodiversity and are highly coherent, although not identical Supplementary Fig. 4). Spatial patterns proved robust in a variety of sensitivity (biodiversity threat 5 0.964 3 human water security threat 1 0.018; r 5 0.97, tests (Supplementary Methods and Supplementary Discussion). Threat indices P , 0.001). Spatial correlations among input drivers (stressors) varied, but were are relative and normalized over discharging landmass. maps reflect the central role of hydrology in spatially configuring Spatial differentiation of incident threat also arises from the inter- environmental impacts, with local stressor loads routed downstream action of multiple factors. China’s arid western provinces would be through digital river networks23 and adjusted for new sources and expected to show high threat due to minimal dilution potential, but dilution (Supplementary Methods and Supplementary Fig. 1). sparse population and limited economic activity combine to keep Similar to an approach used for marine systems16,17, multiple stressors indices low. In contrast, heavily populated and developed eastern were combined using relative weights to derive cumulative threat China shows substantially higher threat, despite greater rainfall and indices. Stressors were expressed as 23 geospatial drivers organized dilution capacity, especially within the Yangtze basin. Other large under four themes (catchment disturbance, pollution, water resource rivers are incapable of fully attenuating the impacts of concentrated development and biotic factors). Expert assessment of stressor impacts development. Over 30 of the 47 largest rivers, which collectively dis- on human water security and biodiversity produced two distinct charge half of global runoff to the oceans, show at least moderate weighting sets, which in turn yielded separate maps of incident threat threat levels (.0.5) at river mouth, with eight rivers (for human water reflecting each perspective. security) and fourteen (for biodiversity) showing very high threat We find that nearly 80% (4.8 billion) of the world’s population (for (.0.75). 2000) lives in areas where either incident human water security or A strikingly small fraction of
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