How Circular Economy and Industrial Ecology Concepts Are Intertwined?
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Assessment of the Possible Reuse of Extractive Waste Coming from Abandoned Mine Sites: Case Study in Gorno, Italy
sustainability Article Assessment of the Possible Reuse of Extractive Waste Coming from Abandoned Mine Sites: Case Study in Gorno, Italy Neha Mehta 1,2, Giovanna Antonella Dino 1,*, Iride Passarella 3, Franco Ajmone-Marsan 4, Piergiorgio Rossetti 1 and Domenico Antonio De Luca 1 1 Department of Earth Sciences, University of Turin, 10125 Torino, Italy; [email protected] (N.M.); [email protected] (P.R.); [email protected] (D.A.D.L.) 2 School of Mechanical and Aerospace Engineering, Queen’s University Belfast, Belfast, BT9 5AH, UK 3 Horizon s.r.l., 10095 Grugliasco (TO), Italy; [email protected] 4 Department of Agricultural, Forestry and Food Sciences, University of Turin, 10095 Grugliasco (TO), Italy; [email protected] * Correspondence: [email protected]; Tel.: +39-011-6705150 Received: 21 January 2020; Accepted: 17 March 2020; Published: 21 March 2020 Abstract: Supply of resources, a growing population, and environmental pollution are some of the main challenges facing the contemporary world. The rapid development of mining activities has produced huge amounts of waste. This waste, found in abandoned mine sites, provides the potential opportunity of extracting raw material. The current study, therefore, focuses on testing the validation of a shared methodology to recover extractive waste from abandoned mines, and applies this methodology to a case study in Gorno, northwest Italy. The methods focused on: (1) analyzing the impact of tailings and fine fraction of waste rock (<2 mm) on plants (Cress - Lepidium Sativum) to assess usability of both as soil additive, and (2) recovering raw materials from tailings and coarse fraction (>2 mm) of waste rock, by means of dressing methods like wet shaking table and froth flotation. -
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 Apple Inc., 19, 178 B Basel Action Network, 116, 126 Basel
Index A E Apple Inc., 19, 178 End-of-life returns, 149 End-of-use returns, 149 B Environmental legislation, 86, 133, 144, 145 Basel Action Network, 116, 126 E-waste, 8, 82–91, 107, 108, 110, 115–120, Basel Convention, 83, 86, 117, 118 125–127, 129–131, 142 Bio-fuel, 7, 30, 31, 33–35 Extended producer responsibility, 88, 117, 119, Blood supply chain, 50, 51, 57, 58, 63–65, 121, 123, 127, 144, 202 67, 68 British, 180, 182, 202 F Brominated Fire Retardants (BFRs), 116 Feedstocks, 29, 35 Footprint, 8, 14, 26, 31, 35, 36, 38, 77, 78, 92–95, 113, 123, 127, 175–180, 182, 183, C 185–191, 195 C40, 3, 14, 16, 24 Fossil hydrocarbon fuels, 35 Cap and Trade, 176, 202 Carbon-dioxide, 1, 4, 7, 9, 10, 30, 39, 81, G 115, 193 GHG emissions, 9, 10, 14, 16, 19, 23, 175–180, CDP project, 14, 190, 191 182, 185–191 Certifier, 168–170, 173 GHG Protocol, 19, 177, 180, 182, 189 Chemicals, 39, 85, 118, 119, 121, 176, 179 Green building, 81, 82, 176, 185 Clinton Climate Initiative, 14 Green building history, 101 Closed-loop supply chain, 8, 133, 149, 163 Green Electronics Council (GEC), 123 Cloud computing, 92–95 Green IT, 74–77, 80, 81, 90, 91 CO2-eq., 10, 11, 14, 16, 19, 21, 23, 175, 182, Greenpeace, 4, 117, 127 186–188 Collective producer responsibility (CPR), H 130–132, 135, 142, 143 Health care, 39, 42, 49–51, 70, 71 Construction, 54, 60, 81, 82, 120, 171, 180, Herman Miller, 179, 180, 191 185 Hewlett-Packard, 73, 76, 125 Credibility, 166, 169, 171 I D ICLEI, 16 Data center, 75, 76, 78–80, 82, 92–95, 123, 185 India, 2, 4, 7, 11, 14, 25, 74, 78, 79, 81–86, 90, Dell, 25, 76, 121, 123, 125, 143, 186, 190 91, 94, 95, 110, 117–119 Disposition decision, 150–153, 156, 158, 160, Industrial ecology, 219 161, 163 In-house manufacturing, 132 T. -
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 -
Participating in Food Waste Transitions: Exploring Surplus Food Redistribution in Singapore Through the Ecologies of Participation Framework
Journal of Environmental Policy & Planning ISSN: (Print) (Online) Journal homepage: https://www.tandfonline.com/loi/cjoe20 Participating in food waste transitions: exploring surplus food redistribution in Singapore through the ecologies of participation framework Monika Rut , Anna R. Davies & Huiying Ng To cite this article: Monika Rut , Anna R. Davies & Huiying Ng (2020): Participating in food waste transitions: exploring surplus food redistribution in Singapore through the ecologies of participation framework, Journal of Environmental Policy & Planning, DOI: 10.1080/1523908X.2020.1792859 To link to this article: https://doi.org/10.1080/1523908X.2020.1792859 © 2020 The Author(s). Published by Informa UK Limited, trading as Taylor & Francis Group Published online: 16 Jul 2020. Submit your article to this journal Article views: 79 View related articles View Crossmark data Full Terms & Conditions of access and use can be found at https://www.tandfonline.com/action/journalInformation?journalCode=cjoe20 JOURNAL OF ENVIRONMENTAL POLICY & PLANNING https://doi.org/10.1080/1523908X.2020.1792859 Participating in food waste transitions: exploring surplus food redistribution in Singapore through the ecologies of participation framework Monika Rut a, Anna R. Davies a and Huiying Ng b aDepartment of Geography, Museum Building, Trinity College, Dublin, Ireland; bIndependent Scholar, Singapore ABSTRACT KEYWORDS Food waste is a global societal meta-challenge requiring a sustainability transition Food waste; transitions; involving everyone, including publics. However, to date, much transitions research has participation; ecologies of been silent on the role of public participation and overly narrow in its geographical participation; Singapore reach. In response, this paper examines whether the ecologies of participation (EOP) approach provides a conceptual framing for understanding the role of publics within food waste transitions in Singapore. -
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. -
Profits from the Past
Reprocessing and tailings reduction.qxp_proof 29/04/2020 09:50 Page 1 REPROCESSING AND TAILINGS REDUCTION In Colombia, AuVert's technology is being combined with CDE's experience in dewatering Profits from the past and tailings management to extract the remaining precious metals existing in the ground, while removing up to 93% of residual mercury which has to date prevented this land from being used by the local population reasons why mining companies may be cautious about using tailings as backfill material or relocating current day ‘waste’ to an inaccessible area of the mine, according to Gerritsen. “As technology improves, the opportunity to recover more of the metals/minerals increases,” he said. “There are elements where that may not be the case – coal ash, for example, cannot be reprocessed but can be used to produce cement. While tailings dam liabilities and falling water resources are There are certainly opportunities with gold, affecting the ability of miners to start new mines, or expand copper and even coal, for instance.” The strategies companies ultimately pursue for existing ones, these issues are strengthening the case for these ‘waste streams’ depend on the technology reprocessing and retreating ‘waste’ sites or streams. Dan available and the safety of the facilities, Gerritsen Gleeson explores an increasingly diverse market focused on remarked. revenue generation and risk reduction “For instance, it may not be economically viable to reprocess the material currently in a ith improved transparency around recycling and thickening, or SART, plant from BQE tailings storage facility and, therefore, the owner tailings dams and waste stockpiles now Water will only bolster cash reserves through the may decide to close it or put it into a non-active Wpart and parcel of being a responsible recovery of a high-grade saleable copper sulphide state,” he said. -
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. -
Permaculture
Permaculture What might it have to offer a green economist? Definition ‘The use of systems thinking and design principles that provide the organising framework for implementing a vision of consciously designed landscapes that mimic the relationships and patterns found in nature’ ‘Linear relationships are easy to think about: the more the merrier. Linear equations are solvable, which makes them suitable for textbooks. Linear systems have an important modular virtue: you can take them apart and put them together again—the pieces add up. Non-linear systems generally cannot be solved and cannot be added together . Non-linearity means that the act of playing the game has a way of changing the rules . That twisted changeability makes non-linearity hard to calculate, but it also creates rich kinds of behavior that never occure in linear systems’ James Gleick, Chaos: Making a New Science Traditional wisdom ‘Because of feedback delays within complex systems, by the time a problem becomes apparent it may be unnecessarily difficult to solve’ Translation: ‘A stitch in time saves nine’ ‘A diverse system with multiple pathways and redundancies is more stable and less vulnerable to external shock than a uniform system with little diversity’ Translation: Don’t put all your eggs in one basket Odum developed Howard Odum methods for tracking and measuring the flows of energy and nutrients through complex living systems Ways of understanding the links between flows of money and goods in society and the flows of energy in ecosystems ‘industrial man . eats potatoes largely made of oil’ Environment, Power and Society, 1971 ‘Odum proposed that a measurement of the amount of transformed solar energy embodied in any product of the biosphere or human society—for which he coined the term ‘emergy’—could provide a kind of ‘universal currency’ which would allow fair and accurate comparison of the human and natural contributions to any particular economic process. -
Procter & Gamble “Zero Manufacturing Waste to Landfill”
Procter & Gamble “Zero Manufacturing Waste to Landfill” Background One of P&G’s 2020 goals for Operations is that <0.5% of Manufacturing Waste is disposed (to either landfill or incineration without energy recovery) versus a 2010 baseline and our corporate long term vision is to have zero consumer or manufacturing waste go to landfills. This goal and vision will drive an increase in the diversion of P&G waste materials away from disposal to reuse, recycling and recovery solutions and it will drive more sites to achieve zero manufacturing waste to landfill status. All P&G sites will adopt the definition of zero manufacturing waste to landfill below and will follow the subsequent guidelines on measurement, reporting and communications to ensure a consistent approach to zero manufacturing waste to landfill across the company. Definition of Zero Manufacturing Waste to Landfill “Zero manufacturing waste to Landfill means zero manufacturing waste is disposed directly to landfill or to Incineration without energy recovery by the site, except where local legal requirements specify that regulated wastes must be disposed in a landfill” Beneficial Reuse Beneficial Reuse simply includes P&G waste sent for Reuse, Recycling or Incineration with Energy Recovery. Incineration without Energy Recovery and Landfill will count as Disposal. Incineration From an environmental perspective Incineration without Energy Recovery is considered to have few benefits over landfill and much less benefit than Incineration with Energy Recovery. This position is reflected in the globally accepted Waste Hierarchy. Therefore sending waste to incineration without energy recovery will not count as diverting the material from landfill. -
Industrial Ecology: a New Perspective on the Future of the Industrial System
Industrial Ecology: a new perspective on the future of the industrial system (President's lecture, Assemblée annuelle de la Société Suisse de Pneumologie, Genève, 30 mars 2001.) Suren Erkman Institute for Communication and Analysis of Science and Technology (ICAST), P. O. Box 474, CH-1211 Geneva 12, Switzerland Introduction Industrial ecology? A surprising, intriguing expression that immediately draws our attention. The spontaneous reaction is that «industrial ecology» is a contradiction in terms, something of an oxymoron, like «obscure clarity» or «burning ice». Why this reflex? Probably because we are used to considering the industrial system as isolated from the Biosphere, with factories and cities on one side and nature on the other, the problem consisting in trying to minimize the impact of the industrial system on what is «outside» of it: its surroundings, the «environment». As early as the 1950’s, this end-of-pipe angle was the one adopted by ecologists, whose first serious studies focused on the consequences of the various forms of pollution on nature. In this perspective on the industrial system, human industrial activity as such remained outside of the field of research. Industrial ecology explores the opposite assumption: the industrial system can be seen as a certain kind of ecosystem. After all, the industrial system, just as natural ecosystems, can be described as a particular distribution of materials, energy, and information flows. Furthermore, the entire industrial system relies on resources and services provided by the Biosphere, from which it cannot be dissociated. (It should be specified that .«industrial», in the context of industrial ecology, refers to all human activities occurring within the modern technological society.