THE ECOLOGICAL WEALTH of NATIONS Earth’S Biocapacity As a New Framework for International Cooperation
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'Zero Carbon': the Wrong Problem Diagnosis, the Wrong 2050 Metric of Success, for New Zealand and the World
‘Zero Carbon’: The Wrong Problem Diagnosis, The Wrong 2050 Metric of Success, for New Zealand and The World. The government surely must agree?: Climate Change is 'merely' one symptom' of ‘The Real Problem’? ‘The Real Problem’ is that Humanity is living well beyond the bioregenerative capacity of the Planet's Ecosystem. (>70% Beyond!) 1970 was the last time the world was in balance, and ever since then the deficit has been steadily increasing without any sign of abating! (This with all the ‘amazing’ ‘Sustainability’ work going on around the world!) The ‘Issue’ is about ‘real’ 'Sustainable Living' and what ‘that’ really means for ‘The World’, a ‘Nation’, and right down to each, and every individual? I'm sure every New Zealander would agree: 'Sustainable Living', and being a 'Sustainable Nation', means: 'We' as a collective, should all be living within our 'fair share' of less than One Planet's, Ecological Regenerative Biocapacity limits? This surely must be, '‘The Ultimate Goal’' of humanity? It's well accepted that anthropogenic Carbon Emissions are a huge contributor to ‘The Real Problem’, but due to the inter-relationship between the Earth's bioregenerative resources, the solution, and particularly when looking to 2050, requires more than a simple, Carbon Emissions, or a ‘Zero Carbon’ focus. (This particularly for nation’s like NZ with strong and diverse Biocapacity Balance Sheets.) At an ‘enclosed system’, global level, a ‘Zero Carbon’ goal may have real relevance in solving ‘The Real Problem’, however, given the huge demographic, and biodiversity diversity between the nations of the world, setting ‘Zero Carbon’ goals at a nation level has the potential to delay, deceive, and confuse efforts to solve ‘The Real Problem’. -
New Perspectives for Mapping Global Population Distribution Using World Settlement Footprint Products
sustainability Article New Perspectives for Mapping Global Population Distribution Using World Settlement Footprint Products Daniela Palacios-Lopez 1,* , Felix Bachofer 1 , Thomas Esch 1, Wieke Heldens 1 , Andreas Hirner 1, Mattia Marconcini 1 , Alessandro Sorichetta 2, Julian Zeidler 1 , Claudia Kuenzer 1, Stefan Dech 1, Andrew J. Tatem 2 and Peter Reinartz 1 1 German Aerospace Center (DLR), German Remote Sensing Data Center (DFD), Oberpfaffenhofen, D-82234 Wessling, Germany; [email protected] (F.B.); [email protected] (T.E.); [email protected] (W.H.); [email protected] (A.H.); [email protected] (M.M.); [email protected] (J.Z.); [email protected] (C.K.); [email protected] (S.D.); [email protected] (P.R.) 2 WorldPop, Department Geography and Environment, University of Southampton, Southampton SO17 1B, UK; [email protected] (A.S.); [email protected] (A.J.T.) * Correspondence: [email protected]; Tel.: +49-81-5328-2169 Received: 3 September 2019; Accepted: 28 October 2019; Published: 31 October 2019 Abstract: In the production of gridded population maps, remotely sensed, human settlement datasets rank among the most important geographical factors to estimate population densities and distributions at regional and global scales. Within this context, the German Aerospace Centre (DLR) has developed a new suite of global layers, which accurately describe the built-up environment and its characteristics at high spatial resolution: (i) the World Settlement Footprint 2015 layer (WSF-2015), a binary settlement mask; and (ii) the experimental World Settlement Footprint Density 2015 layer (WSF-2015-Density), representing the percentage of impervious surface. -
The Ecological Footprint Emerged As a Response to the Challenge of Sustainable Development, Which Aims at Securing Everybody's Well-Being Within Planetary Constraints
16 Ecological Footprint accounts The Ecological Footprint emerged as a response to the challenge of sustainable development, which aims at securing everybody's well-being within planetary constraints. It sharpens sustainable development efforts by offering a metric for this challenge’s core condition: keeping the human metabolism within the means of what the planet can renew. Therefore, Ecological Footprint accounting seeks to answer one particular question: How much of the biosphere’s (or any region’s) regenerative capacity does any human activity demand? The condition of keeping humanity’s material demands within the amount the planet can renew is a minimum requirement for sustainability. While human demands can exceed what the planet renew s for some time, exceeding it leads inevitably to (unsustainable) depletion of nature’s stocks. Such depletion can only be maintained temporarily. In this chapter we outline the underlying principles that are the foundation of Ecological Footprint accounting. 16 Ecological Footprint accounts Runninghead Right-hand pages: 16 Ecological Footprint accounts Runninghead Left-hand pages: Mathis Wackernagel et al. 16 Ecological Footprint accounts Principles 1 Mathis Wackernagel, Alessandro Galli, Laurel Hanscom, David Lin, Laetitia Mailhes, and Tony Drummond 1. Introduction – addressing all demands on nature, from carbon emissions to food and fibres Through the Paris Climate Agreement, nearly 200 countries agreed to keep global temperature rise to less than 2°C above the pre-industrial level. This goal implies ending fossil fuel use globally well before 2050 ( Anderson, 2015 ; Figueres et al., 2017 ; Rockström et al., 2017 ). The term “net carbon” in the agreement further suggests humanity needs far more than just a transition to clean energy; managing land to support many competing needs also will be crucial. -
3Rd Plenary Assembly National Congress of Chile Valparaiso, Chile April 1St – 3Rd, 2004
FIPA/PA/2004/REP/e/vf Original: Spanish Report 3rd Plenary Assembly National Congress of Chile Valparaiso, Chile st rd April 1 – 3 , 2004 Report 3rd Plenary Assembly Vaparaiso, Chile, 1- 3 April 2004 FIPA/PA/2004/REP/e/vf Original: Spanish Contents 1. Introduction ............................................................................................................................2 2. Opening Ceremony................................................................................................................2 3. First Session of the Plenary Assembly ..................................................................................3 3.1 Election of the Chair of the 3rd Plenary Meeting ............................................................3 3.2 Report of the FIPA President..........................................................................................3 3.3 Establishment of the Working Groups ............................................................................3 3.4 Other Business ...............................................................................................................4 4. Final Session of the Plenary Assembly .................................................................................4 4.1 Working Group Reports..................................................................................................4 4.1.1 Group of Women Parliamentarians of the Americas ...............................................5 4.1.2 Working Group 1 – The Fight Against Terrorism.....................................................5 -
Partial Correlation Analysis of Association Between Subjective Well-Being and Ecological Footprint
sustainability Article Partial Correlation Analysis of Association between Subjective Well-Being and Ecological Footprint Jinting Zhang 1, F. Benjamin Zhan 2, Xiu Wu 2,* and Daojun Zhang 3 1 School of Resource and Environmental Science, Wuhan University, Wuhan 430079, China; [email protected] 2 Department of Geography, Texas State University, San Marcos, TX 78666, USA; [email protected] 3 College of Economics and Management, Northwest A&F University, Xianyang 712100, China; [email protected] * Correspondence: [email protected]; Tel.: +1-512-781-0041 Abstract: A spatial-temporal panel dataset was collected from 101 countries during 2006–2016. Using partial correlation (PC) and ordinary correlation (OR) analyses, this research examines the relation- ship between ecological footprint (EF) and subjective well-being (SWB) to measure environmental impacts on people’s happiness. Gross domestic product (GDP), urbanization rate (UR), literacy rate (LR), youth life expectancy (YLE), wage and salaried workers (WSW), political stability (PS), voice accountability (VA) are regarded as control variables. Total bio-capacity (TBC), ecological crop-land footprints (ECL), ecological grazing-land footprint (EGL), and ecological built-up land footprint (EBL) have significant positive influences on SWB, but ecological fish-land (EFL) has significant negative influences on SWB. Ecological carbon footprint (ECF) is significantly negatively related to SWB in developed countries. An increase in the amount of EF factors is associated with a country’s degree of development. Political social–economic impacts on SWB disguised environmental contribution on SWB, especially CBF impacts on SWB. The use of PC in examining the association between SWB and EF helps bridge a knowledge gap and facilitate a better understanding of happiness. -
Measuring Progress in the Degrowth Transition to a Steady State Economy
ECOLEC-03966; No of Pages 11 Ecological Economics xxx (2011) xxx–xxx Contents lists available at ScienceDirect Ecological Economics journal homepage: www.elsevier.com/locate/ecolecon Measuring progress in the degrowth transition to a steady state economy Daniel W. O'Neill ⁎ Sustainability Research Institute, School of Earth and Environment, University of Leeds, Leeds, LS2 9JT, UK Center for the Advancement of the Steady State Economy, 5101 S. 11th Street, Arlington, VA 22204, USA article info abstract Article history: In order to determine whether degrowth is occurring, or how close national economies are to the concept of a Received 27 January 2011 steady state economy, clear indicators are required. Within this paper I analyse four indicator approaches that Received in revised form 16 April 2011 could be used: (1) Gross Domestic Product, (2) the Index of Sustainable Economic Welfare, (3) biophysical Accepted 27 May 2011 and social indicators, and (4) a composite indicator. I conclude that separate biophysical and social indicators Available online xxxx represent the best approach, but a unifying conceptual framework is required to choose appropriate indicators and interpret the relationships between them. I propose a framework based on ends and means, Keywords: Indicators and a set of biophysical and social indicators within this framework. The biophysical indicators are derived Degrowth from Herman Daly's definition of a steady state economy, and measure the major stocks and flows in the Steady state economy economy–environment system. The social indicators are based on the stated goals of the degrowth Conceptual framework movement, and measure the functioning of the socio-economic system, and how effectively it delivers well- being. -
Globalization and Infectious Diseases: a Review of the Linkages
TDR/STR/SEB/ST/04.2 SPECIAL TOPICS NO.3 Globalization and infectious diseases: A review of the linkages Social, Economic and Behavioural (SEB) Research UNICEF/UNDP/World Bank/WHO Special Programme for Research & Training in Tropical Diseases (TDR) The "Special Topics in Social, Economic and Behavioural (SEB) Research" series are peer-reviewed publications commissioned by the TDR Steering Committee for Social, Economic and Behavioural Research. For further information please contact: Dr Johannes Sommerfeld Manager Steering Committee for Social, Economic and Behavioural Research (SEB) UNDP/World Bank/WHO Special Programme for Research and Training in Tropical Diseases (TDR) World Health Organization 20, Avenue Appia CH-1211 Geneva 27 Switzerland E-mail: [email protected] TDR/STR/SEB/ST/04.2 Globalization and infectious diseases: A review of the linkages Lance Saker,1 MSc MRCP Kelley Lee,1 MPA, MA, D.Phil. Barbara Cannito,1 MSc Anna Gilmore,2 MBBS, DTM&H, MSc, MFPHM Diarmid Campbell-Lendrum,1 D.Phil. 1 Centre on Global Change and Health London School of Hygiene & Tropical Medicine Keppel Street, London WC1E 7HT, UK 2 European Centre on Health of Societies in Transition (ECOHOST) London School of Hygiene & Tropical Medicine Keppel Street, London WC1E 7HT, UK TDR/STR/SEB/ST/04.2 Copyright © World Health Organization on behalf of the Special Programme for Research and Training in Tropical Diseases 2004 All rights reserved. The use of content from this health information product for all non-commercial education, training and information purposes is encouraged, including translation, quotation and reproduction, in any medium, but the content must not be changed and full acknowledgement of the source must be clearly stated. -
Population Growth & Resource Capacity
Population Growth & Resource Capacity Part 1 Population Projections Between 1950 and 2005, population growth in the U.S. has been nearly linear, as shown in figure 1. Figure 1 U.S. Population in Billions 0.4 0.3 0.2 Actual Growth 0.1 Linear Approximation - - - H L Year 1950 1960 1970 1980 1990 2000 2010 Source: Population Division of the Department of Economic and Social Affairs of the United Nations Secretariat. World Population Prospects: The 2010 Revision. If you looked at population growth over a longer period of time, you would see that it is not actually linear. However, over the relatively short period of time above, the growth looks nearly linear. A statistical technique called linear regression can create a linear function that approximates the actual population growth over this period very well. It turns out that this function is P = 0.0024444t + 0.15914 where t represents the time variable measured in years since 1950 and P represents the (approximate) population of the U.S. measured in billions of people. (If you take statistics, you’ll probably learn how to obtain this function.) The graph of this linear function is shown in the figure above. (1) Just to make sure that you understand how to work with this function, use it to complete the following table. The actual population values are given. If you are working with the function correctly, the values you obtain should be close to the actual population values! Actual Population t P Year (billions of people) (years) (billions of people) 1960 .186158 1990 .256098 2005 .299846 (2) Use the linear function to determine the approximate year when the population of the U.S. -
The Case Study Report Aims to Analyse More in Depth the Strategies
Rebound effects and the ecological rucksack in the light of resource policies ESDN Case Study No. 7 Nisida Gjoksi ESDN Office Team www.sd-network.eu June 2011 Table of Contents INTRODUCTION ..................................................................................................................................3 RESOURCE EFFICIENCY AND THE REBOUND EFFECTS .........................................................................3 DEFINITION OF THE REBOUND EFFECT ......................................................................................................4 TYPES OF REBOUND EFFECT ...................................................................................................................4 POLICY RESPONSES ..............................................................................................................................4 MAGNITUDE OF REBOUND EFFECTS .........................................................................................................5 RECOMMENDATIONS ...........................................................................................................................5 RESOURCE EFFICIENCY AND THE ECOLOGICAL RUCKSACK .................................................................6 DEFINITION OF THE ECOLOGICAL RUCKSACK ..............................................................................................6 WEAKNESSES OF THE ECOLOGICAL RUCKSACK FACTOR .................................................................................7 REFERENCES .......................................................................................................................................9 -
Ecologically Unequal Exchange and Ecological Debt
Ecologically unequal exchange and ecological debt Alf Hornborg1 Joan Martinez-Alier Lund University, Sweden Autonomous University of Barcelona, Catalonia, Spain Abstract This article introduces a Special Section on Ecologically Unequal Exchange (EUE), an underlying source of most of the environmental distribution conflicts in our time. The nine articles discuss theories, methodologies, and empirical case studies pertaining to ecologically unequal exchange, and address its relationship to ecological debt. Key words: Ecologically Unequal Exchange, ecological debt, political ecology Résumé Cet article présente une section spéciale sur échange écologique inégal (EUE en anglais), une source sous-jacente de la plupart des conflits de distribution environnementaux d'aujourd'hui. Les neuf articles discutent des théories, des méthodes et des études de cas empiriques relatives à l'échange écologique inégal, et aborder sa relation avec la dette écologique. Mots clés: l'échange écologique inégal, la dette écologique, l'écologie politique Resumen Este artículo presenta una sección especial sobre el intercambio ecológícamente desigual (EUE en inglés), que es una causa subyacente de la mayoría de los conflictos de distribución ambiental en la actualidad. Los artículos discuten nuevas teorías, métodos y estudios de casos empíricos sobre el intercambio ecológicamente desigual, y discuten su relación con la deuda ecológica. Palabras clave: comercio ecológicamente desigual, deuda ecológica, ecología política The articles in this Special Section of the Journal of Political Ecology are based on papers presented at a workshop on Ecologically unequal exchange and ecological debt organized in Lund, Sweden, March 27-28th, 2014. The workshop was part of the project Environmental Justice Organizations, Liabilities, and Trade (EJOLT), and most of the contributors were EJOLT project participants. -
Buen Vivir As an Alternative to Sustainable Development: the Case of Cotacachi, Ecuador
Buen Vivir as an Alternative to Sustainable Development: The case of Cotacachi, Ecuador by Natasha Chassagne Total words: 97, 589 Submitted in fulfilment of the requirements for the PhD in Business & Law Centre for Social Impact Swinburne University of Technology May 2019 Abstract Sustainable Development (SD) as a concept was introduced in the 1970s to incorporate environmental considerations into mainstream development practice. SD has arguably failed to achieve its aims of intergenerational sustainability and human wellbeing thus far. This research identifies the Latin American concept of Buen Vivir (BV) as an alternative to the mainstream concept of SD. BV is a plural, biocentric approach to achieving Sustainable Social and Environmental Wellbeing (SSEW). Its plurality refers to a plurality of being, as well as a plurality of knowledge and vision. Yet despite political efforts to operationalise BV, there is a gap in knowledge for a coherent articulation of what BV entails and how it is implemented at the community level. As such it this research aims to find a path for practical implementation. This thesis asks the question: can BV become a practical and viable alternative to sustainable development? Drawing on the literature, this thesis finds that BV is a contested concept with a set of core common principles. It is contextual, with no universal definition. To advance understandings of BV on the ground at the community level, I conducted a short-term ethnographic study in the Cotacachi County, Ecuador. This research found that BV can become a viable alternative to Sustainable Development if certain conditions are met. The most fundamental condition is the transition to a post-extractive economy, as BV is seen as incompatible with extractivism - defined as the extraction of natural resources to satisfy a capitalist market. -
Conceptual Bases of Optimum, Under & Over
CONCEPTUAL BASES OF OPTIMUM, UNDER & OVER POPULATION All the problems concerned with population are generally associated either with overpopulation or with under population. The deviations from the equilibrium state called optimum population give rise to overpopulation and under population. To know about the problems of overpopulation or under population the clear conception of optimum population is quite necessary. 1. Optimum Population: Optimum population is basically an economic concept which denotes balanced population resource relationship in an area. But there come innumerable practical difficulties in its measurement. Actually optimum is relative term which has to be measured in terms of quality of life. Robinson (1964) considers the concept of optimum population most interesting and ingenious but almost sterile. To him this concept is like feminine beauty, which is fascinating but defies any precise definition. The optimum level shows that size of population which yields the highest quality of life. According to Preston Cloud (1970), optimum population is the one that lies within limits, large enough to realise the potentialities of human creativity to achieve a life of high quality for all the inhabitants indefinitely, but not so large as to threaten dilution of quality or the potential to achieve it or the wise management of the ecosystem. Some definitions of optimum population are given:- 1. According to Boulding, “The population at which the standard of life is at maximum is called the optimum population.” 2. According to Dalton, “Optimum population is that which gives the maximum income per head.” 3. According to Peterson, “Optimum population is the number of people that in a given natural, cultural and social environment produces the maximum economic return.” 4.