Towards a More Resource-Efficient and Circular Economy the Role of The
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How to Regulate Our Waste-Full World
STILL ONLY ONE EARTH: Lessons from 50 years of UN sustainable development policy BRIEF #23 How to Regulate Our Waste-Full World Jen Allan, Ph.D. July 2021 Key Messages and Recommendations • There is a long history of dumping hazardous wastes in the seas, on land, and in developing countries; management efforts only started in the 1970s. • The 1989 Basel Convention on the Control of Transboundary Movements of Hazardous Wastes and Their Disposal has expanded to include new wastes and to ban shipments from developed to developing countries. • Proactive management that scans the horizon for new hazardous waste streams has often been missing and is necessary to protect human health and the environment. • The legitimacy of global governance of hazardous wastes may rest on its ability to enable governments protect the most vulnerable. Waste is the most tangible form of pollution. medications, paints, and electronic waste At every stage of production and consumption, (e-waste). we create waste and throw it away, rendering But the products we dispose of do not it invisible from of our lives. Hazardous waste disappear. Much of our waste has value in its takes many forms. It includes the by-products second, discarded life. Minerals and metals of manufacturing or industrial processes, can be recovered and reused. Some types of like toxic ash or sludge. It can be discarded waste can be recycled. In fact, there are entire commercial products, like pesticides. We industries that dispose, recover, and recycle produce hazardous wastes from our homes, our waste. Some of our trash can be another’s by throwing away asbestos-laden insultation, treasure. -
LIFE and Resource Efficiency: Decoupling Growth from Resource Use
LIFE and resource efficiency Decoupling growth from resource use LIFE Focus I LIFE and resource efficiency: Decoupling growth from resource use EUROPEAN COMMISSION ENVIRONMENT DIRECTORATE-GENERAL LIFE (“The Financial Instrument for the Environment”) is a programme launched �y the European Commission and co-ordinated �y the Environment Directorate-General �L�FE Units - E.3. and E.4.). The contents of the pu�lication “L�FE and Resource Efficiency: Decoupling growth from resource use” do not necessarily reflect the opinions of the institutions of the European Union. Authors: Ga�riella Camarsa �Environment expert), Justin Toland, Eamon O’Hara, Tim Hudson, Wendy Jones, Ed Thorpe, Christophe Thévignot �AE�DL, Communications Team Coordinator). Managing Editor: Hervé Martin, European Commission, Environment DG, L�FE E.4 – BU-9, 02/1, 200 rue de la Loi, B-1049 Brussels. LIFE Focus series coordination: Simon Goss �L�FE Communications Coordinator), Evelyne Jussiant �DG Environment Communications Coordinator). Technical assistance: Audrey Thénard, Nicolas Tavitian, Agnese Roccato �Astrale GE�E). The following people also worked on this issue: Al�an De Villepin, Federico Nogara, Simona Bacchereti, Santiago Urquijo-Zamora, Sylvie Ludain �Environment DG, L�FE Environment and Eco-innovation Unit), Carina Vopel, Jonathan Murphy �Environment DG, Communication Unit), Ro�in Miege �Environment DG, Green Week Task Force). Production: Monique Braem �AE�DL). Graphic design: Daniel Renders, Anita Cortés �AE�DL). Photos database: Sophie Brynart. Acknowledgements: Thanks to all L�FE project �eneficiaries who contri�uted comments, photos and other useful material for this report. Photos: Unless otherwise specified; photos are from the respective projects. HOW TO OBTAIN EU PUBLICATIONS Free publications: • via EU Bookshop �http://�ookshop.europa.eu); • at the European Commission’s representations or delegations. -
Extended Producer Responsibility and the Impact of Online Sales
Extended Producer Responsibility and the Impact of Online Sales RE-CIRCLE POLICY HIGHLIGHTS Resource Efficiency & Circular Economy Project Extended Producer Responsibility and the Impact of Online Sales Extended Producer Responsibility (EPR) schemes generate much needed funding for waste management and can be an effective means of boosting collection and recycling rates. However, free-riding associated with the rapid growth of online sales is compromising the viability of these schemes, and has led to the realisation that additional measures are needed to support their operation. RE-CIRCLE Resource Efficiency & Circular Economy Project Key Messages The emergence of the internet, and the resulting growth in online retailing, has improved market access and generated important benefits for consumers. At the same time, online retailing – particularly where it exists in concert with cross-border sales – has begun to adversely affect the functioning of traditional regulatory frameworks. Free-riding on Extended Producer Responsibility (EPR) schemes – where products placed on the market are not accompanied, or only partially accompanied, by required EPR fees – is one such example. Consumers now have much improved access to sellers abroad but, in many cases, these sellers do not comply with EPR regulations in the country of sale. This creates several problems: • Free-riding that consists in not undertaking physical ‘take-back’ obligations leads to lower collection rates for end of life products. • Free-riding by not paying EPR fees results in financing problems for waste management activities. • Free-riding by under-estimating the number of products placed on the market results in a potential over-estimation of national recycling rates. -
3.2 Plastics and Eco-Labelling Schemes
1 Contents 1 Introduction ..................................................................................................................... 3 2 Added value & strategic orientation of PLASTECO workshops ........................................... 4 3 Thematic background ....................................................................................................... 5 3.1 Green Public Procurement (GPP) for promoting alternatives to single-use plastics ....... 5 3.1.1 Policy framework .............................................................................................. 5 3.1.2 Case study 1: Different governmental approaches from Slovakia and Belgium ... 7 3.1.3 Case study 2: GPP criteria for eliminating single-use plastic cups and bottles in medical centres ................................................................................................................ 8 3.1.4 Case study 3: Public procurement as a circular economy enabler ...................... 10 3.2 Plastics and eco-labelling schemes .............................................................................. 10 3.3 Developing secondary raw plastic markets ................................................................. 14 3.3.1 The need to align supply and demand .............................................................. 14 3.3.2 The role of waste management ........................................................................ 16 3.3.3 Case study: Developing new methods for higher-quality secondary plastics ...... 18 3.4 Barriers to the adoption -
Reduce, Reuse and Recycle (The 3Rs) and Resource Efficiency As the Basis for Sustainable Waste Management
CSD-19 Learning Centre “Synergizing Resource Efficiency with Informal Sector towards Sustainable Waste Management” 9 May 2011, New York Co-organized by: UNCRD and UN HABITAT Reduce, Reuse and Recycle (the 3Rs) and Resource Efficiency as the basis for Sustainable Waste Management C. R. C. Mohanty UNCRD 3Rs offer an environmentally friendly alternatives to deal with growing generation of wastes and its related impact on human health, eco nomy and natural ecosystem Natural Resources First : Reduction Input Reduce waste, by-products, etc. Production (Manufacturing, Distribution, etc.) Second : Reuse Third : Material Recycling Use items repeatedly. Recycle items which cannot be reused as raw materials. Consumption Fourth : Thermal Recycling Recover heat from items which have no alternatives but incineration and which cannot Discarding be recycled materially. Treatment (Recycling, Incineration, etc.) Fifth : Proper Disposal Dispose of items which cannot be used by any means. (Source: Adapted from MoE-Japan) Landfill disposal Stages in Product Life Cycle • Extraction of natural resources • Processing of resources • Design of products and selection of inputs • Production of goods and services • Distribution • Consumption • Reuse of wastes from production or consumption • Recycling of wastes from consumption or production • Disposal of residual wastes Source: ADB, IGES, 2008 Resource efficiency refers to amount of resource (materials, energy, and water) consumed in producing a unit of product or services. It involves using smaller amount of physical -
Circular Economy Action Plan for a Cleaner and More Competitive Europe
Circular Economy Action Plan For a cleaner and more competitive Europe #EU GreenDeal 2 Contents 1. INTRODUCTION .......................................................................... 4 2. A SUSTAINABLE PRODUCT POLICY FRAMEWORK ................. 6 2.1. Designing sustainable products .................................................................. 6 2.2. Empowering consumers and public buyers .................................................... 7 2.3. Circularity in production processes ............................................................................... 8 3. KEY PRODUCT VALUE CHAINS .................................................................................................. 10 3.1. Electronics and ICT ............................................................................................................................. 10 3.2. Batteries and vehicles ........................................................................................................................... 11 3.3. Packaging .......................................................................................................................................................... 11 3.4. Plastics ................................................................................................................................................................... 12 3.5. Textiles ....................................................................................................................................................................... 13 3.6. -
The Nordic Swan Ecolabel Promotes Circular Economy
The Nordic Swan Ecolabel promotes circular economy The Nordic Swan Ecolabel is an obvious tool for promoting The Nordic Swan Ecolabel has a circular approach to the life circular economy - thus strengthening corporate cycle and this particular approach is a premise for circular competitiveness, enhancing corporate resource efficiency economy. Because this means that focus is on how actions and contributing to the creation of new business models and taken in one stage have a positive effect on several stages of innovative solutions. the life cycle. And this means that you avoid moving a nega- tive environmental impact to another stage of the life cycle. The objective of the Nordic Swan Ecolabel is to reduce the overall environmental impact of consumption. This is why the Circular economy does not only mean focus on closed re- whole product life cycle – from raw materials to production, source loops for the individual product system. Joint circular use, disposal and recycling – is included in the assessment resource systems may also be the solution. The Nordic Swan when the requirements for Nordic Swan Ecolabelled products Ecolabel shares this approach; for some products, joint circu- are established. This is primarily done on the basis of the lar resource systems will be more effective and will as such following six parameters: be preferable. Requirements for renewable, recycled There are several ways to stimulate circular economy in the and sustainable raw materials life cycle of the product or service. In general, it is important to focus on an efficient and sustainable use of resources and Strict chemical requirements on safe materials without problematic chemicals, so they can be recycled. -
Global Waste Trade Chaos: Rising Environmentalism Or Cost-Benefit Analysis? by Margareth Sembiring1
NTS Insight, no. IN19-02, July 2019 Global Waste Trade Chaos: Rising Environmentalism or Cost-Benefit Analysis? By Margareth Sembiring1 Abstract Contents International garbage disputes are rare. Lately, however, the world witnesses waves • Abstract of newsworthy trash saga.the From Philippines shipping containers of rubbish back • Global Waste Trade Industry to Canada, to Malaysia planning to return tons of garbage back to countries of origin, • Waste Smuggling to China’s near-total ban of plastic waste import, it is hard not to wonder whether this • China’s Plastic Waste Import Ban is a real sign of rising environmentalism. Have countries begun to think that the • Environmental Consciousness or Cost-Benefit Analysis? environment is worthy of a similar priority as the economy? This Insight argues that behind the seemingly growing pro-environment attitudes, it still remains to be seen whether this trend is sustainable in the long run. Considering that the global waste trade is a multi-billion dollar industry, the balance may tip to favour the economic activities again once the dust has settled back. The paper first looks at a brief description of the global waste trade industry. It then discusses some of the contemporary development in the global waste industry particularly on the issues of waste smuggling and China’s plastic waste import ban. It describes related experiences in Indonesia, Malaysia, Vietnam, the Philippines and Thailand. Recommended citation: Margareth Sembiring, ‘Global Waste Trade Chaos: Rising Environmentalism or Cost-Benefit Analysis?’, NTS Insight, No. IN19-02 (Singapore: RSIS Centre for Non-Traditional Security Studies (NTS Centre)). Photo credit: Shutterstock 1 Margareth Sembiring is Associate Research Fellow with the Centre for Non-Traditional Security (NTS) Studies at the 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 -
Disentangling Circular Economy, Sustainability, and Waste Management Principles
ISSUE BRIEF 07.29.21 Disentangling Circular Economy, Sustainability, and Waste Management Principles Rachel A. Meidl, LP.D., CHMM, Fellow in Energy and Environment With the introduction of circular economy to a regenerative circular system where the (CE) principles in major regions of the societal value of products, materials, and world, interest in the concept has increased resources is maximized over time. significantly in the past several years. It is Ubiquitously interwoven into the gaining momentum in the political, economic, decarbonization, energy transition, and and scientific fields and growing in popularity waste minimization narrative is the in corporate strategies. Local and national term “sustainability,” arguably the most governments—including China, Japan, misconstrued descriptor of the decade the U.K., France, Germany, Canada, the and oftentimes used in conjunction or Netherlands, Sweden, and Finland—are also synonymously with CE. Although there is a embracing CE principles. China, ostensibly relationship between sustainability and a CE, the global trailblazer in CE, has made circular these two concepts are vastly distinct. strategies a part of their national priorities since the early 2000s, recently releasing its 14th Five-Year Plan (2021-25).1 The concept SUSTAINABILITY: A SYSTEMS-LEVEL was introduced to the mainstream by the APPROACH Ellen MacArthur Foundation and is heavily Sustainability in its truest form is a systems- promoted by the European Union. Although level approach that considers the wide array the United States does not have a national of environmental, social, and economic CE strategy, the framework is trickling into A comprehensive factors associated with a process or product federal and state-level policy discussions understanding of the and assesses how they interact (Figure 2). -
Exergy As a Measure of Resource Use in Life Cyclet Assessment and Other Sustainability Assessment Tools
resources Article Exergy as a Measure of Resource Use in Life Cyclet Assessment and Other Sustainability Assessment Tools Goran Finnveden 1,*, Yevgeniya Arushanyan 1 and Miguel Brandão 1,2 1 Department of Sustainable Development, Environmental Science and Engineering (SEED), KTH Royal Institute of Technology, Stockholm SE 100-44, Sweden; [email protected] (Y.A.); [email protected] (M.B.) 2 Department of Bioeconomy and Systems Analysis, Institute of Soil Science and Plant Cultivation, Czartoryskich 8 Str., 24-100 Pulawy, Poland * Correspondance: goran.fi[email protected]; Tel.: +46-8-790-73-18 Academic Editor: Mario Schmidt Received: 14 December 2015; Accepted: 12 June 2016; Published: 29 June 2016 Abstract: A thermodynamic approach based on exergy use has been suggested as a measure for the use of resources in Life Cycle Assessment and other sustainability assessment methods. It is a relevant approach since it can capture energy resources, as well as metal ores and other materials that have a chemical exergy expressed in the same units. The aim of this paper is to illustrate the use of the thermodynamic approach in case studies and to compare the results with other approaches, and thus contribute to the discussion of how to measure resource use. The two case studies are the recycling of ferrous waste and the production and use of a laptop. The results show that the different methods produce strikingly different results when applied to case studies, which indicates the need to further discuss methods for assessing resource use. The study also demonstrates the feasibility of the thermodynamic approach. -
The Sustainability of Waste Management Models in Circular Economies
sustainability Article The Sustainability of Waste Management Models in Circular Economies Carmen Avilés-Palacios 1 and Ana Rodríguez-Olalla 2,* 1 Escuela Técnica Superior de Ingeniería de Montes, Forestal y del Medio Natural, Universidad Politécnica de Madrid, c/José Antonio Novais 10, 28040 Madrid, Spain; [email protected] 2 Departamento Economía de la Empresa (ADO), Economía Aplicada II y Fundamentos Análisis Económico, Universidad Rey Juan Carlos, Paseo de los Artilleros s/n, Vicálvaro, 28032 Madrid, Spain * Correspondence: [email protected]; Tel.: +34-910671632 Abstract: The circular economy (CE) is considered a key economic model to meet the challenge of sustainable development. Strenous efforts are focused on the transformation of waste into resources that can be reintroduced into the economic system through proper management. In this way, the linear and waste-producing value chain problems are solved, making them circular, and more sustainable solutions are proposed in those chains already benefiting from circular processes, so that waste generation and waste are reduced on the one hand, and on the other, the non-efficient consumption of resources decreases. In the face of this current tide, there is another option that proposes a certain nuance, based on the premise that, although circular systems promote sustainability, it does not mean that they are in themselves sustainable, given that, in the first place, the effects of CE on sustainable development are not fully known and, on the other hand, the CE model includes the flow of materials, with only scant consideration of the flow of non-material resources (water, soil and energy).