Resource Conservation in the Anthropocene
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Life Cycle Assessment
Life cycle assessment http://lcinitiative.unep.fr/ http://lca.jrc.ec.europa.eu/lcainfohub/index.vm http://www.lbpgabi.uni-stuttgart.de/english/referenzen_e.html "Cradle-to-grave" redirects here. For other uses, see Cradle to the Grave (disambiguation). Recycling concepts Dematerialization Zero waste Waste hierarchy o Reduce o Reuse o Recycle Regiving Freeganism Dumpster diving Industrial ecology Simple living Barter Ecodesign Ethical consumerism Recyclable materials Plastic recycling Aluminium recycling Battery recycling Glass recycling Paper recycling Textile recycling Timber recycling Scrap e-waste Food waste This box: view • talk • edit A life cycle assessment (LCA, also known as life cycle analysis, ecobalance, and cradle-to- grave analysis) is the investigation and valuation of the environmental impacts of a given product or service caused or necessitated by its existence. Contents [hide] 1 Goals and Purpose of LCA 2 Four main phases o 2.1 Goal and scope o 2.2 Life cycle inventory o 2.3 Life cycle impact assessment o 2.4 Interpretation o 2.5 LCA uses and tools 3 Variants o 3.1 Cradle-to-grave o 3.2 Cradle-to-gate o 3.3 Cradle-to-Cradle o 3.4 Gate-to-Gate o 3.5 Well-to-wheel o 3.6 Economic Input-Output Life Cycle Assessment 4 Life cycle energy analysis o 4.1 Energy production o 4.2 LCEA Criticism 5 Critiques 6 See also 7 References 8 Further reading 9 External links [edit] Goals and Purpose of LCA The goal of LCA is to compare the full range of environmental and social damages assignable to products and services, to be able to choose the least burdensome one. -
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 -
Material Flows and Stocks in the Urban Building Sector: a Case Study from Vienna for the Years 1990–2015
sustainability Article Material Flows and Stocks in the Urban Building Sector: A Case Study from Vienna for the Years 1990–2015 Jakob Lederer 1,2,*, Andreas Gassner 1, Florian Keringer 3, Ursula Mollay 3, Christoph Schremmer 3 and Johann Fellner 1 1 Christian Doppler Laboratory for Anthropogenic Resources, Institute for Water Quality and Resource Management, TU Wien, Karlsplatz 13/226, 1040 Vienna, Austria; [email protected] (A.G.); [email protected] (J.F.) 2 Institute of Chemical, Environmental and Bioscience Engineering, TU Wien, Getreidemarkt 9/166-01, 1060 Vienna, Austria 3 Austrian Institute of Regional Studies (OIR GmbH), Franz-Josefs-Kai 27, 1010 Vienna, Austria; [email protected] (F.K.); [email protected] (U.M.); [email protected] (C.S.) * Correspondence: [email protected] Received: 2 December 2019; Accepted: 27 December 2019; Published: 30 December 2019 Abstract: Population growth in cities leads to high raw material consumption and greenhouse gas emissions. In temperate climates were heating of buildings is among the major contributors to greenhouse gases, thermal insulation of buildings became a standard in recent years. Both population growth and greenhouse gas mitigation may thus have some influence on the quantity and composition of building material stock in cities. By using the case study of Vienna, this influence is evaluated by calculating the stock of major building materials (concrete, bricks, mortar, and plaster, steel, wood, glass, mineral wool, and polystyrene) between the years 1990 and 2015. The results show a growth of the material stock from 274 kt in the year 1990 to 345 kt in the year 2015, resulting in a total increase of 26%. -
Quantification of Anthropogenic Metabolism Using Spatially Differentiated Continuous MFA Across the Country
Change Adaptation Socioecol. Syst. 2017; 3: 119–132 Research Article Georg Schiller, Karin Gruhler, Regine Ortlepp* Quantification of anthropogenic metabolism using spatially differentiated continuous MFA https://doi.org/10.1515/cass-2017-0011 across the country. In Germany, such disparities mean that received April 13, 2017; accepted January 16, 2018 there will be a shortfall in RA of 6.3 Gt by the year 2020, Abstract: Coefficient-based, bottom-up material flow while the technically available but unusable RA (due to a analysis is a suitable tool to quantify inflows, outflows regional mismatch of potential supply and demand) will and stock dynamics of materials used by societies, and total 3.2 Gt. Comprehensive recycling strategies have to thus can deliver strategic knowledge needed to develop combine high-quality recycling with other lower-grade circular economy policies. Anthropogenic stocks and flows applications for secondary raw materials. Particularly in are mostly of bulk nonmetallic mineral materials related the case of building materials, essential constraints are to the construction, operation and demolition of buildings not only technical but also local conditions of construction and infrastructures. Consequently, it is important to be and demolition. These interrelations should be identified able to quantify circulating construction materials to and integrated into a comprehensive system to manage help estimate the mass of secondary materials which can the social metabolism of materials in support of circular be recovered such as recycled aggregates (RA) for fresh economy policies. concrete in new buildings. Yet as such bulk materials are high volume but of low unit value, they are generally Keywords: continuous material flow analysis (C-MFA), produced and consumed within a region. -
REFERENCES Abufayed, AA, & Schroeder, ED
REFERENCES Abufayed, A. A., & Schroeder, E. D. (1986) Performance of SBR/denitrification with a primary sludge carbon source. Journal WPCF 5 (58); 387 Adriaanse, A., Bringezu, S., Hamond, A., Moriguchi, Y., Rodenburg, E., Rogich, D., Schütz, H. (1997). Resource Flows: The Material Base of Industrial Economies. World Resource Institute, Washington. Agamuthu P. & Fauziah,S.H. (2010) Impact of Landfill Gas on Climate Change, International Conference on Climate Change and Bioresource (ICCCB 2010) 9th- 12th February 2010, Department of Biotechnology, Bharathidasan University India. Agamuthu,P., Fauziah, S.H. and Khidzir, K.M. (2009) Evolution of solid waste management in Malaysia : Impacts and implications of the solid waste bill 2007. Journal of Material Cycles and Waste Management, 11(2): 96-103. Agamuthu,P., Fauziah, S.H. and Lingesveeramani, M (2004) Evolution of MSW in Malaysia- An overview. Paper presented in the World Congress ISWA 2004, 17-21 October 2004, Rome Italy. Agamuthu,P.,Fauziah,S.H. and Khidzir,K.M.,(2003) Municipal solid waste management; A comparative study on selected landfill in Selangor.In Proceedings of Environment 2003 Environmental Management and Sustainable Development for Better Future Growth.18th- 19th February 2003: pp434-437.Penang, Malaysia. Agamuthu, P. (2001) Solid Waste : Principle and Management. University of Malaya Press: 9-27 Albers, H. & Krückeberg, G, 1992) Combination of aerobic pre-treatment, carbon adsorption and coagulation. Landfilling of waste: leachate. Elsevier applied science. London and New York.305pp. Alhumoud, J.M.(2005)Municipal solid waste recycling in the Gulf Co-operation Council states. Resources,Conservation and Recycling 45(2):142-158. Alhumoud,J.M., Al-Ghusain, I. -
MATERIAL INTENSITY of the ECONOMY Consumption and Material Consumption Core Indicator Production Patterns
MATERIAL INTENSITY OF THE ECONOMY Consumption and Material Consumption Core indicator Production Patterns 1. INDICATOR (a) Name: Material Intensity of the Economy. (b) Brief Definition: Ratio of Domestic Material Consumption (DMC) to Gross Domestic Product (GDP) at constant prices. (c) Unit of Measurement: Kilograms per $1,000 of GDP. (d) Placement in the CSD Indicators Set: Consumption and Production Patterns/Material Consumption. 2. POLICY RELEVANCE (a) Purpose: The indicator provides a basis for policies to increase the efficient use of raw materials in order to conserve natural resources and reduce environment degradation resulting from primary extraction, material processing, manufacturing and waste disposal. (b) Relevance to Sustainable/Unsustainable Development (theme/sub-theme): Improving the efficiency with which materials are used and consequently reducing stresses on the environment are the subjects of chapter 4 of Agenda21, Changing Consumption Patterns. Primary extraction of raw materials, processing of the materials into products, and ultimate disposal of the waste material has major environmental impacts. Reducing the material intensity of production and consumption of goods and services is essential to environmental protection and resource conservation. Reductions in intensity of material use can be achieved by more efficient use of natural resources in production and consumption, by recycling used and waste material, and by shifts in consumption patterns to less material intensive goods and services. The indicator allows an analysis of consumption of natural resources, as well as trends in recovery and recycling. Per-capita consumption of the materials could also be determined, facilitating the interpretation of trends in material intensity. The indicator can also be used as a proxy for assessing trends in industrial pollution. -
Sustainable Cycles and Management of Plastics a Brief Review of RCR Publications in 2019 and Early 2020
Resources, Conservation & Recycling 159 (2020) 104822 Contents lists available at ScienceDirect Resources, Conservation & Recycling journal homepage: www.elsevier.com/locate/resconrec Editorial Sustainable cycles and management of plastics: A brief review of RCR publications in 2019 and T early 2020 ARTICLE INFO ABSTRACT Keywords: Plastics have been playing a vital role in the industrialized economy, resulting in the growing amount of plastic waste Plastics and the surging attentions to plastics sustainability challenge. This is well reflected in the growing amount of sub- Material flow analysis missions to and publications in Resources, Conservation, and Recycling on plastics, which made the editorial board Life cycle assessment decide to edit a Virtual Special Issue (VSI) on the “sustainable cycles and management of plastics” in 2018. The call for Circular economy the VSI has attracted many submissions and twelve were accepted for publication. Together with several other re- Recycling levant studies, we collected and summarized a total of 26 papers published in RCR mainly during 2019–2020 in this Waste management editorial. These papers mostly apply system approach and cover very wide topics such as material flows analysis and circular economy, life cycle assessment and eco-design, regional and global plastic emissions, and human consumption behavior. The whole collection of them offer a comprehensive view of the plastic waste challenges, as well as insights into achieving sustainability in plastic cycles and management. We believe these papers are helpful for government, industries, and individuals in exploring policy implications for building a more sustainable plastics system. 1. Introduction including 1) Material flow analysis (MFA) and plastic circularity, 2) Emissions and pollution, 3) Life cycle assessment (LCA) and eco-design, Plastics are widely used in industrial production throughout the and 4) Public attitude, human behavior, and policymaking. -
Resource Productivity As Sustainability Indicator May Need Developing Resource Productivity Has Become a Popular Indicator of Environmental Sustainability
26 May 2011 Resource productivity as sustainability indicator may need developing Resource productivity has become a popular indicator of environmental sustainability. However, new research has demonstrated that it is influenced by national income and its current use tends to support a simultaneous growth in economic productivity and resource consumption. In order to shape policy effectively, the study suggests that targets should directly emphasise resource consumption and emissions. In order for environmental policy to set effective targets, representative indicators of sustainability are needed. ‘Resource productivity’ is the Gross Domestic Product (GDP) output per resource input (measured in tonnes). It is interpreted as a sign of efficient use of resources and is now used widely as an indicator of environmental sustainability. However, there are some concerns about how this measure is used and interpreted. The researchers conducted an international study of resource productivity for a range of resources in the year 2000. They measured the income elasticities of resource consumption, i.e. the degree that resource consumption varies with national income. They divided resources into the categories of biomass, fossil fuels and ‘other’ (which includes hydraulic and nuclear energy, construction materials and ores and industrial minerals). The results indicated that the consumption of fossil fuels has a high income elasticity, which means that as the national income increases, so too does fossil fuel consumption. However, biomass consumption is inelastic and does not vary with income. Consumption in the ‘other’ category has an intermediate income elasticity. Further analysis indicated that if resource consumption varies with income, resource productivity does not. This is most likely because resource productivity is calculated by dividing income by consumption, so if consumption is proportional to income, there will be no variation in productivity. -
Measuring Resource Productivity a Background Paper by David Pearce
measuring resource productivity a background paper by David Pearce for the Department of Trade and Industry & Green Alliance conference: Revolutionising resource use: measuring radical improvements in resource productivity London, 14 February 2001 “green alliance... This paper is intended as a brief background 'benchmark' paper to assist with discussion of the notion of resource productivity.A far more detailed paper, prepared for DG Environment of the European Commission, and titled Public Policy and Natural Resources Management: a Framework for Integrating Concepts and Methodologies for Policy Evaluation, is available on the Commission's web site at www.europa.eu.int/comm/environment/enveco/s tudies2.htm, or by contacting the author at [email protected] extended paper deals with related notions such as 'sustainable consumption', 'sustainable development', 'ecological footprints', 'environmental space', 'genuine savings' etc. which are not addressed here. David Pearce David Pearce, Department of Economics, University College London and OXERA Ltd, Oxford. Department of Trade and Industry Department of Trade and Industry Environment Directorate 151 Buckingham Palace Road London SW1W 9SS tel: 020 7215 1975 fax: 020 7215 1621 e-mail: [email protected] contents web: www.dti.gov.uk/sustainability/ preface 1 Green Alliance summary of key issues and options 2 Green Alliance 1 defining resource productivity 3 40 Buckingham Palace Road London SW1W 0RE 2 is the notion of resource tel: 020 7233 7433 fax: 020 7233 9033 productivity new? 3 e-mail: [email protected] 3 why raise resource productivity? 3 web: www.green-alliance.org.uk 4 How far can resource productivity be raised? 4 Green Alliance is a registered charity number 1045395. -
Urban Metabolism and Its Applications to Urban Planning and Design
Environmental Pollution xxx (2010) 1e9 Contents lists available at ScienceDirect Environmental Pollution journal homepage: www.elsevier.com/locate/envpol Review The study of urban metabolism and its applications to urban planning and design C. Kennedy a,*, S. Pincetl b, P. Bunje b a Department of Civil Engineering, University of Toronto, Toronto, Canada b Institute of the Environment, UCLA, CA, United States The presents a chronological review of urban metabolism studies and highlights four areas of application. article info abstract Article history: Following formative work in the 1970s, disappearance in the 1980s, and reemergence in the 1990s, Received 12 October 2010 a chronological review shows that the past decade has witnessed increasing interest in the study of Accepted 15 October 2010 urban metabolism. The review finds that there are two related, non-conflicting, schools of urban metabolism: one following Odum describes metabolism in terms of energy equivalents; while the second Keywords: more broadly expresses a city’s flows of water, materials and nutrients in terms of mass fluxes. Four Cities example applications of urban metabolism studies are discussed: urban sustainability indicators; inputs Energy to urban greenhouse gas emissions calculation; mathematical models of urban metabolism for policy Materials Waste analysis; and as a basis for sustainable urban design. Future directions include fuller integration of social, Urban planning health and economic indicators into the urban metabolism framework, while tackling the great Urban design sustainability challenge of reconstructing cities. Greenhouse gas emissions Ó 2010 Elsevier Ltd. All rights reserved. Sustainability indicators 1. Introduction humans, animals and vegetation. Thus, the notion that cities are like ecosystems is also appropriate. -
Boosting Resource Productivity by Adopting the Circular Economy
BOOSTING RESOURCE PRODUCTIVITY BY ADOPTING THE CIRCULAR ECONOMY Davos I Switzerland MEETING REPORT WRF 2015 WRF is an independent non-profit international organization that serves as a platform connecting and fostering knowledge exchange on resources ma- nagement amongst business leaders, policy-makers, NGOs, scientists and the public. This report was drafted by Xaver Edelmann, Bas de Leeuw, Mathias Schluep, Sonia Valdivia, Cecilia Matasci, María Lucía Híjar and Angel Versetti based upon inputs from workshop reporters, speakers and participants. The report has not been reviewed by the speakers. Photos Robert Stürmer. Contact: www.stuermerfoto.ch Technical assistance and design María Lucía Híjar (WRF) St. Gallen, Switzerland, March 2016 ISBN 978-3-906177-11-3 Contact information Lerchenfeldstrasse 5, CH-9014 St. Gallen, Switzerland WRF Secretariat Phone + 41 71 554 09 00 [email protected] www.wrforum.org Visit us on Facebook, Twitter and LinkedIn WORLD RESOURCES FORUM TABLE OF CONTENTS Chairman‘s Summary.....................................................5 1 Photo Gallery..................................................10 2 Plenary Highlights............................................13 3 Selected Workshops Highlights..........................19 4 Selected Master Classes Highlights.....................66 5 Overview Scientific Sessions and Awards.............70 6 Overview Side Events.......................................72 7 WRF Cinema..................................................76 8 Exhibition and UN Lounge.................................78 -
Resource Productivity in 7 Steps
Wuppertal Institute for Climate, Environment and Energy Michael Lettenmeier In cooperation with Holger Rohn Katrin Bienge Christa Liedtke Dafne Mazo Urbaneja Friedrich Schmidt-Bleek Jade Buddenberg Resource productivity in 7 steps How to develop eco-innovative products and services and improve their material footprint 41 SPEZIAL WUPPERTAL WUPPERTAL Authors: Michael Lettenmeier, Holger Rohn, Christa Liedtke, Friedrich Schmidt-Bleek in cooperation with Katrin Bienge, Dafne Mazo Urbaneja and Jade Buddenberg Contact: Michael Lettenmeier, Dr. Christa Liedtke Wuppertal Institute for Climate, Environment and Energy Research Group 4: Sustainable Production and Consumption D-42103 Wuppertal, Döppersberg 19, Germany Phone: + 49 202 2492 -175 / -130, Fax -138 E-Mail: [email protected] [email protected] Holger Rohn Trifolium – Beratungsgesellschaft mbH D-61169 Friedberg, Alte Bahnhofstraße 13, Germany Phone: + 49 6031 68754 -64, Fax -68 E-Mail: [email protected] Prof. Dr. Friedrich Schmidt-Bleek Factor 10 Institute F-83660 Carnoules, La Rabassière, Carrère des Bravengues Phone and Fax: +33 494 332458 Images: Photos: PhotoDisc Figures 1 and 3: Wuppertal Institute, Vislab. Figure 2: Ritthoff et al. 2002 Cover Layout: VisLab, Wuppertal Institute Printing: Hitzegrad, Wuppertal This booklet has been produced during the Living Lab project in order to show how the sustainability of product and service innovations can be measured and documented. The project LIVING LAB – Design Study for the LIVING LAB Research Infrastructure, to research human interaction with, and stimulate the adoption of, sustainable, smart and healthy innovations around the home is funded by the Seventh Framework Programme of the European Union (grant agreement no. 212498). www.livinglabproject.org © Wuppertal Institute for Climate, Environment and Energy 2009 The authors are responsible fort he content of this booklet.