DPSIR Analysis for China's Logistics Industry
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Towards a More Resource-Efficient and Circular Economy the Role of The
Towards a more resource-efficient and circular economy The role of the G20 | 1 A background report prepared for the 2021 G20 Presidency of Italy Towards a more resource-efficient and circular economy The role of the G20 PUBE TOWARDS A MORE RESOURCE-EFFICIENT AND CIRCULAR ECONOMY © OECD 2021 2 | Table of contents Executive Summary 4 1. Introduction 9 2. Past trends in material consumption and waste generation 10 3. Projections of future materials use 18 4. The environmental impacts of materials use 21 5. A transition to a circular economy can lower resource demands and environmental impacts and contribute to the economic and social recovery 24 6. Recent developments on resource efficiency and circular economy policies 27 7. The role of cities towards the circular economy transition 32 8. Towards a G20 policy vision on resource efficiency 38 References 47 TOWARDS A MORE RESOURCE-EFFICIENT AND CIRCULAR ECONOMY © OECD 2021 | 3 Tables Table 1. Selected environmental impacts of materials use 21 Table 2. Selected examples of national, regional and local strategies for resource efficiency, waste management and the circular economy of G20 countries 27 Figures Figure 1. Domestic Material Consumption in G20, OECD and BRIICS 10 Figure 2. Domestic material consumption per capita [tonnes] 11 Figure 3. Resource productivity levels differ substantially among G20 countries, but some improvements could be achieved 12 Figure 4. Despite improvements in resource productivity, domestic material consumption increased in G20 countries 13 Figure 5. Material footprint per capita remains high also for countries with low Domestic Material Consumption per capita 14 Figure 6. As income levels rise, waste generation increases [left], but waste treatment processes improve [right] 15 Figure 7. -
A Comprehensive and Absolute Corporate Sustainability Assessment and Enhanced Input Output Life Cycle Assessment
Copyright Warning & Restrictions The copyright law of the United States (Title 17, United States Code) governs the making of photocopies or other reproductions of copyrighted material. Under certain conditions specified in the law, libraries and archives are authorized to furnish a photocopy or other reproduction. One of these specified conditions is that the photocopy or reproduction is not to be “used for any purpose other than private study, scholarship, or research.” If a, user makes a request for, or later uses, a photocopy or reproduction for purposes in excess of “fair use” that user may be liable for copyright infringement, This institution reserves the right to refuse to accept a copying order if, in its judgment, fulfillment of the order would involve violation of copyright law. Please Note: The author retains the copyright while the New Jersey Institute of Technology reserves the right to distribute this thesis or dissertation Printing note: If you do not wish to print this page, then select “Pages from: first page # to: last page #” on the print dialog screen The Van Houten library has removed some of the personal information and all signatures from the approval page and biographical sketches of theses and dissertations in order to protect the identity of NJIT graduates and faculty. ABSTRACT A COMPREHENSIVE AND ABSOLUTE CORPORATE SUSTAINABILITY ASSESSMENT AND ENHANCED INPUT OUTPUT LIFE CYCLE ASSESSMENT by Joseph M. Wright Stresses due to economic activity are threatening to exceed environmental and societal limits with the potential to jeopardize local communities and create global crises. This research establishes new methodologies and analytic techniques to comprehensively assess corporate sustainability and enhance the efficiency of estimating environmental and social impacts with Input Output Life Cycle Assessment (IOLCA). -
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 -
Environmental Systems Analysis Tools for Decision-Making
Environmental systems analysis tools for decision-making LCA and Swedish waste management as an example Åsa Moberg Licentiate thesis Royal Institute of Technology Department of Urban Planning and Environment Environmental Strategies Research Stockholm 2006 Titel: Environmental systems analysis tools for decision‐making LCA and Swedish waste management as an example Author: Åsa Moberg Cover page photo: Marianne Lockner TRITA‐SOM 06‐002 ISSN 1653‐6126 ISRN KTH/SOM/‐‐06/002‐‐SE ISBN 91‐7178‐304‐0 Printed in Sweden by US AB, Stockholm, 2006 2 Abstract Decisions are made based on information of different kinds. Several tools have been developed to facilitate the inclusion of environmental aspects in decision‐making on different levels. Which tool to use in a specific decision‐making situation depends on the decision context. This thesis discusses the choice between different environmental systems analysis (ESA) tools and suggests that key factors influencing the choice of ESA tool are object of study, impacts considered and information type regarding site‐specificity and according to the DPSIR‐framework. Waste management in Sweden is used as an example to illustrate decision‐making situations, but discussions concerning choice of tools are also thought to be of general concern. It is suggested that there is a need for a number of ESA tools in waste management decision‐making. Procedural tools like Environmental Impact Assessment (EIA) and Strategic Environmental Assessment (SEA) should be used e.g. by companies applying for development of waste management facilities and by public authorities preparing plans and programmes. Within these procedural tools analytical tools providing relevant information could be used, e.g. -
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. -
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. -
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). -
The Foundations of the Environmental Rebound Effect and Its Contribution Towards a General Framework
Ecological Economics 125 (2016) 60–69 Contents lists available at ScienceDirect Ecological Economics journal homepage: www.elsevier.com/locate/ecolecon Methodological and Ideological Options The foundations of the environmental rebound effect and its contribution towards a general framework David Font Vivanco a,⁎, Will McDowall b, Jaume Freire-González c,RenéKempd, Ester van der Voet a a Institute of Environmental Sciences (CML), Leiden University, 2300, RA, Leiden, The Netherlands b UCL Energy Institute, UCL, Central House, 14 Upper Woburn Place, London WC1H 0NN, United Kingdom c Environmental Change Institute, University of Oxford, Oxford OX1 3QY, United Kingdom d ICIS and UNU-MERIT, Maastricht University, 6200, MD, Maastricht, The Netherlands article info abstract Article history: The study of the so-called rebound effect has traditionally pertained to the domain of neoclassical energy eco- Received 8 September 2015 nomics. In recent years, other disciplines have applied this concept in the context of the environmental assess- Received in revised form 25 January 2016 ment of products and policies, and multiple perspectives have unfolded more or less in parallel. Among these, Accepted 21 February 2016 the environmental rebound effect (ERE) perspective, focused on efficiency changes and indicators that go beyond Available online 14 March 2016 energy to multiple environmental issues, has remained relatively unnoticed. This article thus asks the following questions: What are the foundational aspects of the ERE and how these relate to other perspectives? Are there Keywords: Rebound effect irreconcilable differences between perspectives? And what is the value of the ERE towards a general framework? Consumption We map the fundamental ideas behind the ERE and find that the lack of articulation has resulted in inconsistent Energy economics usage and lack of clarity.