The Natural Resource Degradation and Vulnerability Nexus
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Assessing Resource Depletion in LCA: a Review of Methods and Methodological Issues
Assessing resource depletion in LCA: a review of methods and methodological issues Serenella Sala www.jrc.ec.europa.eu Serving society Stimulating innovation Supporting legislation Outline Sustainability and resources Key concepts and perspectives Review on current impact assessment methodologies for Resources 27 November 2012 2 Resources and sustainability -1 One of the father of the definition of “sustainability” was Hans Carl von Carlowitz. The concept was founded in forestry and was strictly resource-based and stayed so for centuries (Carlowitz 1713, Cotta 1828). The concept was developed by foresters because timber had been excessively overused and become a very scarce resource in the process of the industrial revolution and urbanisation. Carlowitz HC (1713)Sylvicultura oeconomica, oder haußwirthliche Nachricht und Naturmäßige Anweisung zur wilden Baum-Zucht 27 November 2012 3 Resources and sustainability _2 Around 1700, the mining industry and livelihood of thousands was threatened in Saxony. It was not that the mines had been exhausted of their ores, the problem was an acute scarcity of timber. The mining industry and smelting of ores had consumed whole forests. In the vicinity of places of mining activity the old growth forests had disappeared completely. Trees had been cut at unsustainable rates for decades without efforts to restore the forests. First, the river systems in the Erzgebirge was engineered, so logs could be transported from ever more distant forest areas, but these measures only postponed the crisis. The prices for timber rose ever more, which led to bankruptcy and closure of parts of the mining industry. 27 November 2012 4 Resources and sustainability _3 • Environmental as well as economic and social dimension • Interplay between socio-economic drivers, environmental and socio economic impacts Should resources be included in LCIA? Scientific debate For sure they should be part of the impact assessment in LCSA…. -
How Do the Extinctions of Other Creatures Affect Humans Directly?
4/30/2020 How Do the Extinctions of Other Creatures Affect Humans Directly? How Do the Extinctions of Other Creatures Affect Humans Directly? ••• Updated March 10, 2018 By Milton Kazmeyer While extinction of animal species is part of the natural process of evolution, the expansion of the human species has led to significant increases in the extinction rate. Because humans share ecosystems with endangered species, our quality of life and our survival is linked to them. Habitat destruction, climate change, resource depletion and other factors have increased the extinction rate by a factor of 1,000, putting substantial pressure on thousands of the most vulnerable creatures on the planet. American Bison One example of how the depletion of a species affected humans is what occurred after the American bison nearly vanished in the 19th century. Originally, the bison was a common animal on the central plains, with an estimated population of 15 million, and the Native Americans of the region depended on the animal for food, leather, fur and many https://sciencing.com/extinctions-other-creatures-affect-humans-directly-20692.html 1/11 4/30/2020 How Do the Extinctions of Other Creatures Affect Humans Directly? other goods vital to a nomadic lifestyle. By 1890, however, there were only a few thousand bison left in America. Tribal hunters were able to kill more of the animals with the aid of firearms, and in some cases the United States government encouraged the widespread slaughter of bison herds. The vanishing species forced tribes dependent on the animal to move to new lands in search of food, and eventually those tribes could no longer support themselves and had to deal with the United States government for survival. -
Plight, Plunder, and Political Ecology
1 Plight, Plunder, and Political Ecology CIVIL STRIFE in the developing world represents perhaps the greatest international security challenge of the early twenty-first century.1 Three-quarters of all wars since 1945 have been within countries rather than between them, and the vast majority of these conflicts have oc curred in the world’s poorest nations.2 Wars and other violent conflicts have killed some 40 million people since 1945, and as many people may have died as a result of civil strife since 1980 as were killed in the First World War.3 Although the number of internal wars peaked in the early 1990s and has been declining slowly ever since, they remain a scourge on humanity. Armed conflicts have crippled the prospect for a better life in many developing countries, especially in sub-Saharan Africa and parts of Asia, by destroying essential infrastructure, deci mating social trust, encouraging human and capital flight, exacerbat ing food shortages, spreading disease, and diverting precious financial resources toward military spending.4 Compounding matters further, the damaging effects of civil strife rarely remain confined within the afflicted countries. In the past de cade alone tens of millions of refugees have spilled across borders, pro ducing significant socioeconomic and health problems in neighboring areas. Instability has also rippled outward as a consequence of cross- border incursions by rebel groups, trafficking in arms and persons, dis ruptions in trade, and damage done to the reputation of entire regions in the eyes of investors. Globally, war-torn countries have become ha vens and recruiting grounds for international terrorist networks, orga nized crime, and drug traffickers.5 Indeed, the events of September 11, 2001, illustrate how small the world has become and how vulnerable even superpowers are to rising grievances and instabilities in the de veloping world. -
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World Bank Document
THE WORLD BANK POLICY PLANNING AND RESEARCH STAFF Public Disclosure Authorized Environment Department Economic Analysis of Sustainable· Growth and Sustainable Development Public Disclosure Authorized JohnPezzey Public Disclosure Authorized March 1989 1ment Department Working Paper No. 15 ) n3 .15 Public Disclosure Authorized --,-·., use. The views and interpretations herein are those of I to the World Bank, to its affiliated organizations or to SLC004236 This paper has been prepared by John Pezzey, a consultant to the Environment Department of the World Bank. He is an economist specializing on the roles of environmental resources and discount rates in growth theory, and is a visiting research fellow in the Environment and Behavior Program of the Institute of Behavioral Science at the University of Colorado at Boulder. The author is grateful to Robert Ayres, Edward Barbier, Herman Daly, Salah El Serafy, John English, Jonathan Fisher, Philip Graves, Stein Hansen, David Heigham, Jeffrey Krautkraemer, Nancy Olewiler, David Pearce, Henry Peskin, Barry Poulson, Ray Prince, David Ulph, Jeremy Warford and Tomasz Zylicz for helpful comments and discussions on earlier drafts of this paper. Departmental Working Papers are not formal publications of the World Bank. They present preliminary and unpolished results of country analysis or research that is circulated to encourage discussion and comment; citation and the use of such a paper should take account of its provisional content. The findings, interpretations, and conclusions expressed in this paper are entirely those of the author, and should not be attributed in any manner to the World Bank, to its affiliated organizations, or to members of its Board of Executive Directors or the countries they represent. -
Using Game Theory to Develop Sustainability Strategies in an Era
ering & ine M g a n n E a Seifi and Crowther, Ind Eng Manage 2018, 7:1 l g a i e r m t Industrial Engineering & DOI: 10.4172/2169-0316.1000240 s e u n d t n I Management ISSN: 2169-0316 Research Article Open Access Using Game Theory to Develop Sustainability Strategies in an Era of Resource Depletion Shahla Seifi and David Crowther* Faculty of Business and Law, De Montfort University, The Gateway, Leicester, LE1 9BH, UK *Corresponding author: David Crowther, Faculty of Business and Law, De Montfort University, The Gateway, Leicester, LE1 9BH, UK, Tel: +44(0)7971629198; Fax: +44(0)1332720660; E-mail: [email protected] Received date: 02 November 2017; Accepted date: 07 March 2018; Published date: 14 March 2018 Copyright: © 2018 Seifi S, et al. 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. Abstract Objective: Sustainability is recognized as an important objective in business planning and is of equal relevance to policy makers. It is equally accepted, almost universally, that the resources of the planet are finite and are being over consumed on an annual basis. The prognosis therefore is that resources are being depleted and competition for access to remaining resources must ensue, as countries seek to grow and develop. This will have the effect of increasing the transaction costs of business activity as they find greater difficulty in seeking restricted supply of resources. -
NIGER : REGION DE TAHOUA Rapport Mensuel Au 30 Septembre 2020
NIGER : REGION DE TAHOUA Rapport mensuel Au 30 Septembre 2020 Ce rapport est produit par OCHA Niger en collaboration avec les partenaires humanitaires. Il couvre la période du 1er au 30 septembre 2020. FAITS SAILLANTS Chiffres clés 4M Habitants 113k MALI TASSARA Agadez Superficie (en km2) TILLIA Incidents* de sécurité (au 31/08) TCHINTABARADEN 56k ABALAK Personnes déplacées internes Zinder TAHOUA nnes déplacées internes KEITA Tillabery BAGAROUA BOUZA 20k ILLELA Maradi Personnes MADAOUA MALBAZA Dosso réfugiées BIRNI N'KONNI NIGERIA The boundaries and names shown and the designations used on this map do not imply official endorsement or acceptance by the United Nations. Source : UNHCR, Carte 1: Carte référentielle de Tahoua cluster Protection, INS Situation sécuritaire La situation sécuritaire est toujours volatile dans la région de Tahoua. Les forces de défense et de sécurité poursuivent les opérations de ratissage, des patrouilles régulières sont organisées dans les zones nord et nord-ouest qui sont encore sous état d’urgence. Néanmoins, les exactions des GANES contre la population civile à travers des razzias de bétail en guise de prélèvement de la Zakat, les violences physiques et autres extorsions ont continué. www.unocha.org/niger Le Bureau des Nations Unies pour la Coordination des Affaires Humanitaires a pour mission de mobiliser et coordonner une réponse efficace et fondée sur des principes humanitaires en partenariat avec les acteurs nationaux et internationaux. Rapport bimensuel – Tahoua | 2 Les populations vulnérables qui ont un accès limité aux services sociaux de base font également face à des opportunités économiques réduites. Dans la région d’Agadez, les actes récurrents de banditisme urbain et d’attaques à main armée sur les axes routiers continuent d’inquiéter les populations. -
Defining, Valuing, and Providing Ecosystem Goods and Services*
THOMAS C. BROWN,- JOHN C. BERGSTROM" & JOHN B. LOOMIS*** Defining, Valuing, and Providing Ecosystem Goods and Services* ABSTRACT Ecosystem services are the specific results of ecosystem processes that either directly sustain or enhance human life (as does natural protectionfrom the sun's harmful ultraviolet rays) or maintain the quality of ecosystem goods (as water purification maintains the quality of streamflow). "Ecosystem service" has come to represent several related topics ranging from the measurement to the marketing of ecosystem service flows. In this article we examine several of these topics by first clarifying the meaning of "ecosystem service" and then (1) placing ecosystem goods and services within an economic framework, emphasizing the role and limitations of substitutes;(2) summarizing the methodsfor valuationof ecosystem goods and services; and (3) reviewing the various approachesfor their provision and financing. Many ecosystem services and some ecosystem goods are received without monetary payment. The "marketing" of ecosystem goods and services is basically an effort to turn such recipients - those who benefit without ownership- into buyers, thereby providing market signals that serve to help protect valuable goods and services. We review various formal arrangementsfor making this happen. I. INTRODUCTION "Ecosystem service" is the latest environmental buzzword.1 It appeals to ecologists, who have long recognized the many benefits derived from well-functioning ecosystems. It appeals to resource economists, who . Economist and Project Leader, Rocky Mountain Research Station, U.S. Forest Service, Fort Collins, Colorado. Address for correspondence: [email protected], T.C. Brown, RMRS, 2150-A Center Avenue, Fort Collins, CO 80526. - Richard B. Russell, Jr., Professor of Public Policy, Department of Agricultural and Applied Economics, University of Georgia. -
Rapport Sur Les Indicateurs De L'eau Et De L'assainissement
REPUBLIQUE DU NIGER ----------------------------------------- FRATERNITE – TRAVAIL - PROGRES ------------------------------------------- MINISTERE DE L’HYDRAULIQUE ET DE L’ASSAINISSEMENT ---------------------------------------- COMITE TECHNIQUE PERMANENT DE VALIDATION DES INDICATEURS DE L’EAU ET DE L’ASSAINISSEMENT RAPPORT SUR LES INDICATEURS DE L’EAU ET L'ASSAINISSEMENT POUR L’ANNEE 2016 Mai 2017 Table des matières LISTE DES SIGLES ET ACRONYMES I. INTRODUCTION ................................................................................................................ 1 II. DEFINITIONS ..................................................................................................................... 1 2.1. Définitions de quelques concepts et notions dans le domaine de l’hydraulique Rurale et Urbaine. ................................................................................................................ 1 2.2. Rappel des innovations adoptées en 2011 ................................................................... 2 2.3. Définitions des indicateurs de performance calculés dans le domaine de l’approvisionnement en eau potable ................................................................................... 3 2.4. Définitions des indicateurs de performance calculés dans le domaine de l’assainissement .................................................................................................................... 4 III. LES INDICATEURS DES SOUS – PROGRAMMES DU PROSEHA .......................... 4 IV. CONTRAINTES ET PROBLEMES -
The Measurement of Environmental and Resource Values: Theory and Methods
The Measurement of Environmental and Resource Values The first edition of this important work was the winner of the 2002 Publication of Enduring Quality award by the Association of Environmental and Resource Economists. The continuing premise for the book is that estimates of the economic values of environmental and natural resource services are essential for effective policy-making. Like previous editions, the third edition, which includes two additional co-authors, presents a comprehensive treatment of the theory and methods involved in estimating environmental benefits. Researchers, policy-makers, and practitioners will welcome the work as an up- to-date reference on recent developments. Students will gain a better understanding of the contribution that economics as a discipline can make to decisions concerning pollution control and human health, recreation, environmental amenities, and other critical issues concerning the way we use and interact with environmental and natural resource systems. To reflect recent progress in both the theory and practice of non-market valuation, this third edition includes more details on empirical approaches to measurement, expanded discussion of the reasons for divergence between “willingness to pay” and “willingness to accept compensation,” and increased coverage of econometric issues encountered in estimation. In keeping with its cutting-edge orientation, it also includes more discussion of survey design, equilibrium sorting models, and the implications of behavioral economics for welfare measurements and benefit cost analysis. A. Myrick Freeman III is William D. Shipman Professor of Economics Emeritus at Bowdoin College in Maine, USA, and a former Senior Fellow at Resources for the Future (RFF), Washington DC, USA. Joseph A. -
Bureau of Land Management Socioeconomics Program Guidance Economic Methods for Estimating Nonmarket Environmental Values
Bureau of Land Management Socioeconomics Program Guidance Economic Methods for Estimating Nonmarket Environmental Values Purpose. This guidance describes when and how to use economic methods to estimate nonmarket environmental values when preparing National Environmental Policy Act (NEPA) analyses for the Bureau of Land Management’s (BLM) resource management planning and other decision-making. These methods estimate the benefits individuals attribute to experiences of the environment, uses of natural resources, or the existence of particular ecological conditions that do not involve market transactions and therefore lack prices. At least a qualitative description of the most relevant nonmarket values should be included for the affected environment and the impacts of alternatives in NEPA analyses involving environmental impact statements (EIS), for both resource management plans (RMP) and project- level decisions. Such description may also be appropriate for inclusion in environmental assessments (EA). The use of quantitative valuation methods should contribute to the analysis of one or more issues to be addressed in the environmental analysis supporting planning or other decision-making. A quantitative analysis of nonmarket values in EIS-level NEPA analyses is strongly encouraged where one or more of the criteria provided below apply (see Criteria for Nonmarket Valuation). This guidance is directed to several audiences. For non-specialists, it explains the basic concepts of nonmarket valuation and provides direction on when and how such methods can best be used (see General Guidance). For economists and other socioeconomic specialists, it provides additional notes on the use of these methods (see Technical Guidance). The socioeconomics program is currently funding a series of field-based case studies on nonmarket economic valuation for resource management decisions. -
Defining Environmental Goods and Services: a Case Study of Mexico
couv 8-06-05 rouge 2ok 28/11/05 14:16 Page 4 October 2005 Trade and Environment ICTSD Project on Environmental Goods and Services Defining Environmental Goods and Services: A Case Study of Mexico The ICTSD project on Bridging Trade and Sustainable Development in Environmental Goods and Services aims at enhancing developing countries’ capacity to understand trade and sustainable development issue By Enrique Lendo linkages with respect to environmental goods and services and reflect regional perspectives and priori- Consultants in Environmental Strategy and Negotiations (COESNA) ties in regional and multilateral trade negotiations. The current phase of the project got underway in January 2005 and will continue until June 2006. Other project activities and resources include: ● Options for Liberalisation of Trade in Environmental Goods in the Doha Round. By Robert Howse and Petrus B. van Bork, November 2005. ● The Economics Of Trade In Environmental Services: The Implications For Developing Countries In The GATS. By Colin Kirkpatrick, forthcoming. ● Technology transfer Issues in environmental goods: Will the Doha Round of negotiations facilitate access? By Lynn Matelka, forthcoming. ● Latin American Consultation on Environmental Goods and Services, Diálogo regional sudamericano sobre bienes y servicios ambientales, Cartagena de Indias, Colombia, 1-2 June 2005. For further information, visit http://www.trade-environment.org/page/ictsd/projects/egs_desc.htm. One of the mandates of the CEC is to conduct an ongoing assessment of the environmental impacts of A study commissioned by the Commission for Environmental Cooperation trade liberalisation in North America. This assessment work shows that liberalised trading rules under NAFTA do not in and of themselves lead to the increased use of environmentally preferable products.