IUCN Red List of Ecosystems Team, Commission on Ecosystem Management (CEM)
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Fact Sheet on Health and Biodiversity
Living in harmony with nature Health and Biodiversity We rely on biodiversity to stay healthy. Biodiversity sustains our food supply, is a source of medicines, and supports the provision of clean air and fresh water while also contributing to economic development, cultural and spiritual enrichment. It is now also widely recognized that biodiversity is affected by climate change, with negative consequences for human well-being, but biodiversity, through the ecosystem services it supports, also makes an important contribution to both climate change mitigation and adaptation. As all people require freedom from illness as well as social, emotional, physical, spiritual and cultural well-being, we cannot have healthy societies without biodiversity. Changes to biodiversity can have severe and unpredictable effects on the health of all living things, including people. Clearing new land, for example, can bring people into closer contact with wildlife that may transmit their diseases to humans and also promote the spread of disease from humans to animals. It may also reduce populations of predators that hold disease-carrying organisms in check. In addition, clearing of land may bring about the loss of plants and other organisms useful in medical research or that may contain substances used as medicines. People in developing countries face particularly heavy health burdens from a loss of biodiversity, with impacts on food supply and quality, medicines, and cultural and religious values. It has been estimated that approximately 80% of the world’s population from developing countries rely mainly on traditional medicines derived from plants and that 25% of prescriptions dispensed in United States pharmacies contained plant extracts or active ingredients derived from plants. -
Assessing Ecosystem Health D.J
REVIEWS Assessing ecosystem health D.J. Rapport, R. Costanza and A.J. McMichael here is now abundant evi- Evaluating ecosystem health in relation to health in terms of ‘system organiz- dence that many human- the ecological, economic and human ation, resilience and vigor, as well dominated ecosystems, in- health spheres requires integrating human as the absence of signs of ecosys- Tcluding various biophysical values with biophysical processes, an tem distress24. The definition also systems at regional and global lev- integration that has been explicitly includes the presence of essential els, have become highly stressed avoided by conventional science. The field functions and key attributes that and dysfunctional1. The ‘services’ is advancing with the articulation of the sustain life systems (Box 1). provided by these ecosystems are linkages between human activity, regional A healthy ecosystem is defined extremely important to human wel- and global environmental change, as being ‘stable and sustainable’; fare2–5. As stressed ecosystems reduction in ecological services and the maintaining its organization and have become highly degraded1,6–9, consequences for human health, autonomy over time and its re- they have also become incapable economic opportunity and human silience to stress24. Assessment of of supplying services to the same communities. Increasing our these properties in large-scale sys- level as in the past5,10. The ca- understanding of these interactions will tems through specific indicators pacity of the environment to sus- involve more active collaboration between of resilience, organization and tain economic activity4,10 and hu- the ecological, social and health vigor has been attempted for the man health11–15 is, therefore, being sciences. -
Unifying Research on Social–Ecological Resilience and Collapse Graeme S
TREE 2271 No. of Pages 19 Review Unifying Research on Social–Ecological Resilience and Collapse Graeme S. Cumming1,* and Garry D. Peterson2 Ecosystems influence human societies, leading people to manage ecosystems Trends for human benefit. Poor environmental management can lead to reduced As social–ecological systems enter a ecological resilience and social–ecological collapse. We review research on period of rapid global change, science resilience and collapse across different systems and propose a unifying social– must predict and explain ‘unthinkable’ – ecological framework based on (i) a clear definition of system identity; (ii) the social, ecological, and social ecologi- cal collapses. use of quantitative thresholds to define collapse; (iii) relating collapse pro- cesses to system structure; and (iv) explicit comparison of alternative hypoth- Existing theories of collapse are weakly fi integrated with resilience theory and eses and models of collapse. Analysis of 17 representative cases identi ed 14 ideas about vulnerability and mechanisms, in five classes, that explain social–ecological collapse. System sustainability. structure influences the kind of collapse a system may experience. Mechanistic Mechanisms of collapse are poorly theories of collapse that unite structure and process can make fundamental understood and often heavily con- contributions to solving global environmental problems. tested. Progress in understanding col- lapse requires greater clarity on system identity and alternative causes of Sustainability Science and Collapse collapse. Ecology and human use of ecosystems meet in sustainability science, which seeks to understand the structure and function of social–ecological systems and to build a sustainable Archaeological theories have focused and equitable future [1]. Sustainability science has been built on three main streams of on a limited range of reasons for sys- tem collapse. -
For-75: an Ecosystem Approach to Natural Resources Management
FOR-75 An Ecosystems Approach to Natural Resources Management Thomas G. Barnes, Extension Wildlife Specialist ur nation—and especially Kentucky—has an The glade cress Oabundance of renewable natural resources, including timber, wildlife, and water. These re- sources have allowed us to build a strong nation and economy, creating one of the highest stan- dards of living in the world. As our nation grew and prospered during the past 200 years, we ex- tracted those natural resources through agricul- ture, forestry, mining, urban or industrial expansion, and other developments. Ultimately, we affected the amount of wild lands that native plants and animals need for survival. In the past, natural resources agencies have ral- The glade cress grows in Jefferson and Bullitt counties lied public support for declining wildlife popula- and nowhere else in the world. tions. In the 1930s, Congress passed the Federal Aid to Wildlife Resto- Table 1. Selected Ecosystem Declines in the ration Act, also called including the bald eagle, brown pelican, peregrine United States the Pittman-Robertson falcon, and American alligator, have recovered % Decline (loss) or Act, and state wildlife from the brink of extinction. However, numerous Ecosystem or Community Degradation agencies received fund- other species and unique habitats are declining, Pacific Northwest Old Growth Forest 90 ing to restore numerous and the list of endangered and threatened organ- Northeastern Pine Barrens 48 wildlife species that isms continues to grow every year. Why are these Tall Grass Prairie 961 were in trouble, includ- additional species in trouble, while other species Palouse Prairie 98 ing white-tailed deer, are increasing their populations and ranges? Where did we go wrong? Why, almost immedi- Blackbelt Prairies 98 wild turkeys, wood ducks, elk, and prong- ately after passage of the Endangered Species Act, Midwestern Oak Savanna 981 horn antelope. -
Ecosystem Health Demystified: an Ecological Concept Determined By
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Lincoln University Research Archive Ecosystem health demystified © An ecological concept determined by economic means By E. J. S. Hearnshaw1, R. Cullen1 and K. F. D. Hughey2 1Commerce Division, Lincoln University, 2Environment, Society and Design Division, Lincoln University Abstract This paper addresses “ecosystem health”, a concept recently popularised as the way forward in evaluating nature. The concept is often defined in vague expressions and is being seen more as a broad societal aspiration rather than a specific performance measure of ecosystem management. As such, the paper aims to demystify ecosystem health, that is, to demarcate an accurate and feasible characterisation of the concept. To achieve this aim an examination of the various viewpoints of nature is undertaken. Models of ecosystem health, such as the notions of naturalness, genetic fitness, climax, diversity, stability and keystone species are each considered and subsequently deemed inappropriate, especially when viewing ecosystems as “complex self-organising systems”. Complex self-organising systems are non-linear dynamic systems that have multiple steady states and have emergent and chaotic properties. One model that captures this self- organisation process is Holling’s adaptive cycle. However, when investigating this model it was concluded that there is no means to determining which phase within a system state, or state within a system is ecologically “better”. Therefore, ecosystem health cannot be considered in a positive manner established by scientific objectivity. Rather, the concept must be determined in a normative fashion through it is suggested the elicitation of subjective societal values, so to define an optimal management strategy. -
State of the Amazon: Freshwater Connectivity and Ecosystem Health WWF LIVING AMAZON INITIATIVE SUGGESTED CITATION
REPORT LIVING AMAZON 2015 State of the Amazon: Freshwater Connectivity and Ecosystem Health WWF LIVING AMAZON INITIATIVE SUGGESTED CITATION Macedo, M. and L. Castello. 2015. State of the Amazon: Freshwater Connectivity and Ecosystem Health; edited by D. Oliveira, C. C. Maretti and S. Charity. Brasília, Brazil: WWF Living Amazon Initiative. 136pp. PUBLICATION INFORMATION State of the Amazon Series editors: Cláudio C. Maretti, Denise Oliveira and Sandra Charity. This publication State of the Amazon: Freshwater Connectivity and Ecosystem Health: Publication editors: Denise Oliveira, Cláudio C. Maretti, and Sandra Charity. Publication text editors: Sandra Charity and Denise Oliveira. Core Scientific Report (chapters 1-6): Written by Marcia Macedo and Leandro Castello; scientific assessment commissioned by WWF Living Amazon Initiative (LAI). State of the Amazon: Conclusions and Recommendations (chapter 7): Cláudio C. Maretti, Marcia Macedo, Leandro Castello, Sandra Charity, Denise Oliveira, André S. Dias, Tarsicio Granizo, Karen Lawrence WWF Living Amazon Integrated Approaches for a More Sustainable Development in the Pan-Amazon Freshwater Connectivity Cláudio C. Maretti; Sandra Charity; Denise Oliveira; Tarsicio Granizo; André S. Dias; and Karen Lawrence. Maps: Paul Lefebvre/Woods Hole Research Center (WHRC); Valderli Piontekwoski/Amazon Environmental Research Institute (IPAM, Portuguese acronym); and Landscape Ecology Lab /WWF Brazil. Photos: Adriano Gambarini; André Bärtschi; Brent Stirton/Getty Images; Denise Oliveira; Edison Caetano; and Ecosystem Health Fernando Pelicice; Gleilson Miranda/Funai; Juvenal Pereira; Kevin Schafer/naturepl.com; María del Pilar Ramírez; Mark Sabaj Perez; Michel Roggo; Omar Rocha; Paulo Brando; Roger Leguen; Zig Koch. Front cover Mouth of the Teles Pires and Juruena rivers forming the Tapajós River, on the borders of Mato Grosso, Amazonas and Pará states, Brazil. -
Carlos Zambrana-Torrelio Associate VP for Conservation and Health Research Into the Critical Connections Between Human, Wildlife Health and Ecosystems
Red List of Ecosystems Carlos Zambrana-Torrelio Associate VP for Conservation and Health Research into the critical connections between human, wildlife health and ecosystems. • How human activities (land use change) could lead to disease emergence (Ebola, Zika, …) • Disease regulation as an ecosystem service: Estimate the economic impact of infectious diseases due to land use change Red List of Ecosystems: a quantitative framework to evaluate ecosystem condition Red List of Ecosystems Goal: develop a consistent global framework for monitoring the status of ecosystems and identifying those most at risk of biodiversity loss. • How great are the risks? • How soon are the changes likely to occur? Assessing risks to ecosystems 1989 2008 • Unlike species, ecosystems do not go extinct! • Cannot sustain its defining features: Characteristic native biota and Ecological processes that structure & sustain the system • Ecosystem collapse ~ species extinction - Analogous concepts • Ecosystem collapse affects capacity to deliver ecosystem Aral sea: collapsed ecosystem services Freshwater aquatic ephemeral steppe + hypersaline lakes Keith et al. (2013). Scientific foundations for an IUCN Red List of Ecosystems. PLoS ONE in press Supplementary material 14 TAPIA FOREST, MADAGASCAR contributed by Justin Moat & Steven Bachman, Royal Botanic Gardens, Kew CLASSIFICATION National: Tapia Forest is recognised as a major vegetation type in the Atlas of vegetation of Madagascar (Rabehevitra and Rakotoarisoa 2007). IUCN Habitats Classification Scheme (Version 3.0): 1. Forest / 1.5 Subtropical/Tropical Dry Forest ECOSYSTEM DESCRIPTION Characteristic native biota A forest comprising an evergreen canopy of 10–12 m, with an understorey of ericoid shrubs. Lianas are frequent, but epiphytes are few. The herbaceous layer is dominated by grasses (Rabehevitra & Rakotoarisoa 2007). -
Carbon Balance in Salt Marsh and Mangrove Ecosystems: a Global Synthesis
Journal of Marine Science and Engineering Review Carbon Balance in Salt Marsh and Mangrove Ecosystems: A Global Synthesis Daniel M. Alongi Tropical Coastal & Mangrove Consultants, 52 Shearwater Drive, Pakenham, VIC 3810, Australia; [email protected]; Tel.: +61-4744-8687 Received: 5 September 2020; Accepted: 27 September 2020; Published: 30 September 2020 Abstract: Mangroves and salt marshes are among the most productive ecosystems in the global coastal 1 1 ocean. Mangroves store more carbon (739 Mg CORG ha− ) than salt marshes (334 Mg CORG ha− ), but the latter sequester proportionally more (24%) net primary production (NPP) than mangroves (12%). Mangroves exhibit greater rates of gross primary production (GPP), aboveground net primary production (AGNPP) and plant respiration (RC), with higher PGPP/RC ratios, but salt marshes exhibit greater rates of below-ground NPP (BGNPP). Mangroves have greater rates of subsurface DIC production and, unlike salt marshes, exhibit active microbial decomposition to a soil depth of 1 m. Salt marshes release more CH4 from soil and creek waters and export more dissolved CH4, but mangroves release more CO2 from tidal waters and export greater amounts of particulate organic carbon (POC), dissolved organic carbon (DOC) and dissolved inorganic carbon (DIC), to adjacent waters. Both ecosystems contribute only a small proportion of GPP, RE (ecosystem respiration) and NEP (net ecosystem production) to the global coastal ocean due to their small global area, but contribute 72% of air–sea CO2 exchange of the world’s wetlands and estuaries and contribute 34% of DIC export and 17% of DOC + POC export to the world’s coastal ocean. -
Ecological Consequences of Human Niche Construction: Examining Long-Term Anthropogenic Shaping of Global Species Distributions Nicole L
SPECIAL FEATURE: SPECIAL FEATURE: PERSPECTIVE PERSPECTIVE Ecological consequences of human niche construction: Examining long-term anthropogenic shaping of global species distributions Nicole L. Boivina,b,1, Melinda A. Zederc,d, Dorian Q. Fuller (傅稻镰)e, Alison Crowtherf, Greger Larsong, Jon M. Erlandsonh, Tim Denhami, and Michael D. Petragliaa Edited by Richard G. Klein, Stanford University, Stanford, CA, and approved March 18, 2016 (received for review December 22, 2015) The exhibition of increasingly intensive and complex niche construction behaviors through time is a key feature of human evolution, culminating in the advanced capacity for ecosystem engineering exhibited by Homo sapiens. A crucial outcome of such behaviors has been the dramatic reshaping of the global bio- sphere, a transformation whose early origins are increasingly apparent from cumulative archaeological and paleoecological datasets. Such data suggest that, by the Late Pleistocene, humans had begun to engage in activities that have led to alterations in the distributions of a vast array of species across most, if not all, taxonomic groups. Changes to biodiversity have included extinctions, extirpations, and shifts in species composition, diversity, and community structure. We outline key examples of these changes, highlighting findings from the study of new datasets, like ancient DNA (aDNA), stable isotopes, and microfossils, as well as the application of new statistical and computational methods to datasets that have accumulated significantly in recent decades. We focus on four major phases that witnessed broad anthropogenic alterations to biodiversity—the Late Pleistocene global human expansion, the Neolithic spread of agricul- ture, the era of island colonization, and the emergence of early urbanized societies and commercial net- works. -
Ecosystem Health: Definitions, Assessment, and Case Studies- David J
ECOLOGY- Vol. II - Ecosystem Health: Definitions, Assessment, and Case Studies- David J. Rapport, William S. Fyfe, Robert Costanza, Jerry Spiegel, Annalee Yassi, György M. Böhm, G. P. Patil, Robert Lannigan, Christopher M. Anjema, Walter G. Whitford and Pierre Horwitz ECOSYSTEM HEALTH: DEFINITIONS, ASSESSMENT, AND CASE STUDIES David J. Rapport College Faculty of Environmental Design and Rural Development, University of Guelph, Canada; Faculty of Medicine and Dentistry, The University of Western Ontario, London, Canada William S. Fyfe Department of Earth Sciences, The University of Western Ontario, London, Canada Robert Costanza Institute for Ecological Economics, University of Maryland, Solomons, Maryland, USA Jerry Spiegel Liu Centre for the Study of Global Issues, University of British Columbia, Vancouver, British Columbia, Canada; Department of Community Health Services, University of Manitoba, Winnipeg, Canada Annalee Yassi Institute of Health Promotion Research, University of British Columbia, Vancouver, British Columbia, Canada; Department of Community Health Services, University of Manitoba, Winnipeg, Canada György M. Böhm Laboratory of Experimental Air Pollution, Faculty of Medicine, University of São Paulo, Brazil G. P. Patil Center for Statistical Ecology and Environmental Statistics, Department of Statistics, The Pennsylvania State University, USA Robert Lannigan Department of Microbiology and Immunology, Faculty of Medicine and Dentistry, The University of Western Ontario, London, Canada UNESCO – EOLSS Christopher M. Anjema Department of Ophthamology, Ivey Institute of Ophthalmology, Faculty of Medicine and Dentistry, TheSAMPLE University of Western Ontario, CHAPTERS London, Canada Walter G. Whitford USDA-ARS Jornada Experimental Range, MSC 3JER, New Mexico State University, Las Cruces, USA Pierre Horwitz Centre for Ecosystem Management; Consortium for Ecosystem Health, Edith Cowan University, Joondalup, Western Australia ©Encyclopedia of Life Support Systems (EOLSS) ECOLOGY- Vol. -
Developing a Standardized Definition of Ecosystem Collapse for Risk Assessment
Developing a standardized definition of ecosystem collapse for risk assessment Citation: Bland, Lucie M., Rowland, Jessica A., Regan, Tracey J., Keith, David A., Murray, Nicholas J., Lester, Rebecca E., Linn, Matt., Rodríguez, Jon Paul. and Nicholson, Emily 2018, Developing a standardized definition of ecosystem collapse for risk assessment, Frontiers in ecology and the environment, vol. 16, no. 1, pp. 29-36. DOI: http://www.dx.doi.org/10.1002/fee.1747 ©2018, The Ecological Society of America Downloaded from DRO: http://hdl.handle.net/10536/DRO/DU:30106000 DRO Deakin Research Online, Deakin University’s Research Repository Deakin University CRICOS Provider Code: 00113B REVIEWS REVIEWS REVIEWS Developing a standardized definition of 29 ecosystem collapse for risk assessment Lucie M Bland1,2*, Jessica A Rowland1, Tracey J Regan2,3, David A Keith4,5,6, Nicholas J Murray4, Rebecca E Lester7, Matt Linn1, Jon Paul Rodríguez8,9,10, and Emily Nicholson1 The International Union for Conservation of Nature (IUCN) Red List of Ecosystems is a powerful tool for classifying threatened ecosystems, informing ecosystem management, and assessing the risk of ecosystem collapse (that is, the endpoint of ecosystem degradation). These risk assessments require explicit definitions of ecosystem collapse, which are currently challenging to implement. To bridge the gap between theory and practice, we systematically review evidence for ecosystem collapses reported in two contrasting biomes – marine pelagic ecosystems and terrestrial forests. Most studies define states of ecosystem collapse quantitatively, but few studies adequately describe initial ecosystem states or ecological transitions leading to collapse. On the basis of our review, we offer four recommendations for defining ecosystem collapse in risk assessments: (1) qualitatively defining initial and collapsed states, (2) describing collapse and recovery transitions, (3) identify- ing and selecting indicators of collapse, and (4) setting quantitative collapse thresholds. -
ECOSYSTEM INSIDER the Ecosystem Insider Brings You News from the IUCN Commission on Ecosystem Management
Forward to a friend | View in browser ECOSYSTEM INSIDER The Ecosystem Insider brings you news from the IUCN Commission on Ecosystem Management June 2018 - Edition 2 Dear IUCN CEM member, Follow us for more news and updates We are pleased to bring you the Second issue of the IUCN Commission on Ecosystem Management (CEM) Newsletter for 2018 CEM HIGHLIGHT Technical Expert Meeting on Adaptation 2018 The technical examination process on adaptation (TEP-A) was established at COP 21 as part of the enhanced action prior to 2020 in the decision adopting the Paris Agreement. The TEP-A seeks to identify concrete opportunities for strengthening resilience, reducing vulnerabilities, and increasing the understanding and implementation of adaptation actions. During its May meeting in Bonn, Angela Andrade participated in Session #1 Adaptation Planning for Vulnerable Ecosystems where two issues led the discussion: 1) What are the barriers to more widespread adoption of ecosystem-based adaptation at the national level? How can these barriers be overcome? Does ecosystem-based adaptation contribute to increasing the resilience of vulnerable communities and groups? To learn more about the Technical Expert Meeting, visit their page. To learn more about this event, please visit the Earth Negotiation Bulletin. CEM was present in the 3rd EbA Knowledge Day celebrated as a UNFCCC SB48 Side Event. The 3rd EbA Knowledge Day was organized by GIZ and IUCN under the Friends of EbA (FEBA) network in the framework of UNFCCC SBSTA 48 with the aim to enhance knowledge on strategies and partnerships for upscaling EbA at policy and implementation level especially in the context of NDC implementation, public finance and key sector strategies such as agriculture/food security, water, forestry and fisheries.