A Review on Upcycling: Current Body of Literature, Knowledge Gaps and a Way Forward
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Five Principles of Waste Product Redesign Under the Upcycling Concept
International Forum on Energy, Environment Science and Materials (IFEESM 2015) Five Principles of Waste Product Redesign under the Upcycling Concept Jiang XU1 & Ping GU1 1School of Design, Jiangnan University, Wuxi, China KEYWORD: Upcycling; Redesign principle; Green design; Industrial design; Product design ABSTRACT: It explores and constructs the principles of waste product redesign which are based on the concept of upcycling. It clarifies the basic concept of upcycling, briefly describes its current development, deeply discusses its value and significance, combines with the idea of upcycling which behinds regeneration design principle from the concept of “4R” of green design, and takes real-life case as example to analyze the principles of waste product redesign. It puts forward five principles of waste product redesign: value enhancement, make the most use of waste, durable and environmental protection, cost control and populace's aesthetic. INTRODUCTION Recently, environmental problems was becoming worse and worse, while as a developing country, China is facing dual pressures that economical development and environmental protection. However, large numbers of goods become waste every day all over the world, but the traditional recycling ways, such as melting down and restructuring, not only produce much CO2, but also those restruc- tured parts or products cannot mention in the same breath with raw ones. As a result, the western countries started to center their attention to the concept of “upcycling” of green design, which can transfer the old and waste things into more valuable products to vigorously develop the green econ- omy. Nevertheless, this new concept hasn’t been well known and the old notion of traditionally inef- ficient reuse still predominant in China, so it should be beneficial for our social development to con- struct the principles of waste products’ redesign which are based on the concept of upcycling. -
Resource Efficiency, Extended Producer Responsibility And
Resource Efficiency, Extended Producer Responsibility and Producer Ownership A presentation to the Annual Symposium of the Greening Growth Partnership and Economics and Environmental Policy Research Network By Professor Paul Ekins University College London and International Resource Panel Ottawa February 27th, 2020 The imperative of increasing resource efficiency The promise of double decoupling Key messages from the Summary for Policy Makers http://www.unep.org/resourcepanel/KnowledgeResources/AssessmentAreasReports/Cross-CuttingPublications/tabid/133337/Default.aspx Headline Message: “With concerted action, there is significant potential for increasing resource efficiency, which will have numerous benefits for the economy and the environment” By 2050 policies to improve resource efficiency and tackle climate change could • reduce global resource extraction by up to 28% globally. • cut global GHG emissions by around 60%, • boost the value of world economic activity by 1% How to increase resource efficiency? Waste/resource management focus • Make it easier to recycle materials by differentiating between wastes and recyclables (definition of waste, by-products) • Increase the quality of collected recyclates (separate collections) • Create markets for recycled materials through product specifications and green public procurement (standards and regulation) • Ban the incineration of recyclables • Facilitate industrial clusters that exchange materials while they are still resources to prevent them from becoming wastes (industrial symbiosis) -
Upcycling Wastes with Biogas Production: an Exergy and Economic Analysis
Venice 2012, Fourth International Symposium on Energy from Biomass and Waste Upcycling wastes with biogas production: An exergy and economic analysis M. Martin*, A. Parsapour* *Environmental Technology and Management, Linköping University, 581 83, Linköping, Sweden SUMMARY: The massive consumption of finite resources creates high economical and environmental costs due to material dispersion and waste generation. In order to overcome this, by-products and wastes may be used, to avoid the use of virgin materials and benefit from the useful inherent energy of the material. By adding value to the material, economic and environmental performance can be improve, which is called upcycling. In this paper, an exergy and economic analysis of a biogas process is examined. In order to investigate if biogas production from wastes can upcycle materials, biogas production from a by- product from the brewing process is examined. From the analysis, the process is found to upcycle the by-product with an increase in exergy and economic benefit due to the generation of biomethane and biofertilizer. This analysis thus shows that by using by-products as such, the sustainability of the system may improve. 1. INTRODUCTION Given the concerns for sustainable development, the availability of energy from fossil sources and their environmental effects continues to produce problems for nations worldwide. With the current availability of alternative energy sources, our dependence on fossil sources can thus be questioned. Among these, bioenergy and biofuels have great potential for development and improvement. However, many experts have criticized the environmental performance and energy efficiency of biofuel production (Wibe, 2010; Akinci, 2008; Searchinger, 2008). -
Responsible Manufacturing in the Marine Production
local repairers of ship spares. This study considers the UN “Responsible Manufacturing Sustainable Development Goals on climate change, in the marine production: sustainable production and consumption. The results on prospects offered by ΑΜ technology are based upon Legal and technical aspects” already successful upcycling of marine spare parts. The outcome is that shipowners, as users/consumers should 1 2 Yanna Pavlopoulou & Evanthia Kostidi be aware and support the expansion of a global new legislation that implements the “right to repair”, the 1 Managing Partner at CommonLawgic Research Center; mandatory concept of Extended Producer’s Responsibility PhD candidate at National Technical University of Athens (NTUA) Greece, Sector of Industrial Management and (EPR) and responsible innovation ethics. A new movement Operations Research, Environmental Economics and Su- has to emerge urging the manufacturers to design circular stainability Unit. Contact details: [email protected]* materials, upcycled products and shared services, with the 2 PhD Candidate at University of the Aegean (Greece) at support of additive manufacturing and circular makers. the Department of Shipping, Trade and Transport, MSc. Shipping in Transport and International Trade, MSc Keywords: responsible, circular innovation, additive Mechanical Engineering. Contact details: manufacturing,3D printing, EPR, maritime [email protected]** ABSTRACT INTRODUCTION Responsible innovation is an emerging concept aligned to Marine technology and business competition flourished in consumers’ business objectives. Corporate social the past decade, under the environmental umbrella, offering responsibility in contrast is a backward response to ways to combat shipping’s Sulphur and ocean footprint. challenges. The issue at stake is how to forward regulate the The Greek shipping combated but lost the battles on BWM competitive and socio-ethical aspects of technology and SOx policy measures. -
End-Of-Life Modelling
Best Practice LCA: End-of-Life Modelling October 28, 2014 Agenda 1. Modelling EoL in LCA 2. Recycled content approach 3. Avoided burden approach 4. Value-corrected substitution 5. PE’s recommendations 6. Current PEF discussions 2 Modelling EoL in LCA 3 Modelling EoL in LCA General challenge • “Allocation” is commonly used to assign burdens associated with the upstream supply chain to each product of multi-output processes. • EoL modelling gives rise to a similar problem due to its multi-functionality – treat waste and produce valuable products (material and/or energy) • Focus on how the burden of virgin material production and the burden of EoL treatment be allocated between the first application in one product system and its subsequent application in the same or another product system. • Chosen allocation approach will affect modelling of other EoL pathways as well (e.g., landfill). 4 Modelling EoL in LCA Most common approaches • Recycled content approach (a.k.a. cut-off, 100/0) • Avoided burden approach (a.k.a. End-of-Life recycling, 0/100) • Value-Corrected Substitution 5 Recycled content approach 6 Recycled content approach General description • Scrap inputs to the product system are modelled as being free of any primary material burden (all assigned to the first life cycle). • The recycling of scrap generated by the product system is not part of the product system and the system boundary is drawn at the point of scrap generation. No credits for subsequent recycling. • When modelling other disposal processes (e.g., incineration with energy recovery, landfill with landfill gas capture), burdens are included, but no credits should be given for energy recovery. -
Subject Index
Index 2-opt 287, 288, 291, 293 arc 18, 19, 240–242, 260, 280–284, 335, 368, 369 architecture 45, 58, 61, 65, 68, 74, 75, 77, A 93, 103, 236, 274, 277, 375, 376, 422 as-good-as-new 458, 460, 462 a priori data 267, 270, 271, 273, 297, 305 assembly 25, 26, 48, 49, 55, 58, 64, 73, 74, absolute technical importance rating 84, 86, 101, 118, 229–231, 237, 239, 243, (ATIR) 131, 133–135 245, 249, 250, 256, 259, 278, 306–309, abundance 20, 218 312, 313, 316, 328, 329, 332–339, 343, accumulation 20–22, 282, 426 351, 356–361, 365, 371, 391, 416, 423, activity modeling 45, 46 424, 474, 510 actor 9, 41, 42, 54, 56, 82, 114 assembly line balancing 239, 256, 259, acquisition 93, 102, 103, 225, 232, 234, 278, 306–309, 343 291, 385, 445, 446, 449, 452, 453, 455, asset management 459, 496, 497 457, 458, 461–465, 466, 510 attitude 3, 139, 140, 219, 223, 237, 455, 457, adaptability 347, 415, 430 458, 466, 524 adaptation 16, 62, 64, 66, 67, 69, 102, 356, automotive 222, 388–391, 411, 446, 449, 368, 392, 408, 422, 442 456–458, 466, 468, 474 adaptive disassembly process planning autonomous barrier 521 363, 375 adaptive kanban 314, 329 adaptive learning 375, 378, 379 B adjacent element hill climbing (AEHC) 236, 238, 240, 242, 274, 285, 287–290 backlog cost 477, 483 after-sale product condition Basel Action Network (BAN) 500, 506 monitoring 92 Basel convention 498, 499, 501, 503 aggregation 2, 11, 16–18 Bayesian forecasting 223, 224 analytic hierarchy process (AHP) 105, Bayesian updating 105, 110, 124–129, 212 110, 115–118, 197, 205, 212, 214 beginning of life -
Sorting of Automotive Manufacturing Wrought Aluminum Scrap
Sorting of Automotive Manufacturing Wrought Aluminum Scrap A Major Qualifying Project Submitted to the Faculty of Worcester Polytechnic Institute in partial fulfillment of the requirements for the Degree in Bachelor of Science in Mechanical Engineering By Shady J. Zummar Ghazaleh Date: 04/26/2018 Sponsoring Organization: Metal Processing Institute Approved by: ________________________________________ Professor Diran Apelian Alcoa-Howmet Professor of Engineering, Advisor Founding Director of Metal Processing Institute Abstract An increase of 250% in wrought aluminum usage in automotive manufacturing is expected by 2020. Consequently, the generation of new aluminum sheet scrap will also increase. Producing secondary aluminum only emits 5% of the CO2 compared to primary aluminum – a significant 95% decrease. With the advent of opto-electronic sorting technologies, recovery and reuse of new aluminum scrap (generated during manufacturing) is at hand. A series of interviews with industrial experts and visits to automotive stamping plants were performed in order to identify: (i) the most common wrought aluminum alloys from which scrap is generated; (ii) the present scenario — how scrap is collected today; and (iii) the types of contamination that must be accounted for during and after sortation. Recommendations are made herein that will support the development of an optimized scrap management system including sorting criteria that will enable closed loop recycling. 2 Table of Contents Abstract 2 Table of Contents 3 Acknowledgements 5 1 Introduction -
Upgrading Construction and Demolition Waste Management from Downcycling to Recycling in the Netherlands
Journal of Cleaner Production 266 (2020) 121718 Contents lists available at ScienceDirect Journal of Cleaner Production journal homepage: www.elsevier.com/locate/jclepro Upgrading construction and demolition waste management from downcycling to recycling in the Netherlands * Chunbo Zhang a, Mingming Hu a, b, , Xining Yang a, Brenda Miranda-Xicotencatl a, Benjamin Sprecher a, Francesco Di Maio c, Xiaoyang Zhong a, Arnold Tukker a, d a Institute of Environmental Sciences, Leiden University, 2300, RA, Leiden, Netherlands b School of Management Science and Real Estate, Chongqing University, Chongqing, 40045, China c Faculty of Civil Engineering and Geosciences, Delft University of Technology, 2628, CN, Delft, the Netherlands d Netherlands Organization for Applied Scientific Research TNO, 2595, DA, Den Haag, Netherlands article info abstract Article history: Urban mining from construction and demolition waste (CDW) is highly relevant for the circular economy Received 30 April 2019 ambitions of the European Union (EU). Given the large volumes involved, end-of-life (EoL) concrete is Received in revised form identified as one of the priority streams for CDW recycling in most EU countries, but it is currently largely 10 February 2020 downcycled or even landfilled. The European projects C2CA and VEEP have proposed several cost- Accepted 13 April 2020 effective technologies to recover EoL concrete for new concrete manufacturing. To understand the po- Available online 22 April 2020 tential effects of large-scale implementation of those recycling technologies on the circular construction, Handling editor: Yutao Wang this study deployed static material flow analysis (MFA) for a set of EoL concrete management scenarios in the Netherlands constructed by considering the development factors in two, technological and temporal Keywords: dimensions. -
E-Waste Management
E-waste Management "E-waste" is a popular, informal name for electronic products nearing the end of their "useful life. "E-wastes are considered dangerous, as certain components of some electronic products contain materials that are hazardous, depending on their condition and density. The hazardous content of these materials pose a threat to human health and environment. Discarded computers, televisions, VCRs, stereos, copiers, fax machines, electric lamps, cell phones, audio equipment and batteries if improperly disposed can leach lead and other substances into soil and groundwater. Many of these products can be reused, refurbished, or recycled in an environmentally sound manner so that they are less harmful to the ecosystem. This paper highlights the hazards of e-wastes, the need for its appropriate management and options that can be implemented. INTRODUCTION Industrial revolution followed by the advances in information technology during the last century has radically changed people's lifestyle. Although this development has helped the human race, mismanagement has led to new problems of contamination and pollution. The technical prowess acquired during the last century has posed a new challenge in the management of wastes. For example, personal computers (PCs) contain certain components, which are highly toxic, such as chlorinated and brominated substances, toxic gases, toxic metals, biologically active materials, acids, plastics and plastic additives. The hazardous content of these materials pose an environmental and health threat. Thus proper management is necessary while disposing or recycling ewastes. These days computer has become most common and widely used gadget in all kinds of activities ranging from schools, residences, offices to manufacturing industries. -
Waste to Energy in the Age of the Circular Economy Best Practice Handbook
WASTE TO ENERGY IN THE AGE OF THE CIRCULAR ECONOMY BEST PRACTICE HANDBOOK NOVEMBER 2020 ASIAN DEVELOPMENT BANK WASTE TO ENERGY IN THE AGE OF THE CIRCULAR ECONOMY BEST PRACTICE HANDBOOK NOVEMBER 2020 ASIAN DEVELOPMENT BANK Creative Commons Attribution 3.0 IGO license (CC BY 3.0 IGO) © 2020 Asian Development Bank 6 ADB Avenue, Mandaluyong City, 1550 Metro Manila, Philippines Tel +63 2 8632 4444; Fax +63 2 8636 2444 www.adb.org Some rights reserved. Published in 2020. ISBN: 978-92-9262-480-4 (print); 978-92-9262-481-1 (electronic); 978-92-9262-482-8 (ebook) Publication Stock No. TIM200330-2 DOI: http://dx.doi.org/10.22617/TIM200330-2 The views expressed in this publication are those of the authors and do not necessarily reflect the views and policies of the Asian Development Bank (ADB) or its Board of Governors or the governments they represent. ADB does not guarantee the accuracy of the data included in this publication and accepts no responsibility for any consequence of their use. The mention of specific companies or products of manufacturers does not imply that they are endorsed or recommended by ADB in preference to others of a similar nature that are not mentioned. By making any designation of or reference to a particular territory or geographic area, or by using the term “country” in this document, ADB does not intend to make any judgments as to the legal or other status of any territory or area. This work is available under the Creative Commons Attribution 3.0 IGO license (CC BY 3.0 IGO) https://creativecommons.org/licenses/by/3.0/igo/. -
"Sustainable Materials Management"?
Briefing Paper: What are “Sustainable Materials” and “Sustainable Materials Management”? October 4, 2011 Primary Authors: David Allaway & Peter Spendelow What is a sustainable level of material or resource consumption? The 1994 Oslo Symposium on Sustainable Consumption defined "sustainable consumption" as: "the use of services and related products which respond to basic needs and bring a better quality of life while minimizing the use of natural resources and toxic materials as well as the emissions of waste and pollutants over the life cycle of the service or product so as not to jeopardize the needs of future generations." While useful conceptually, the previous definition may be difficult to apply in practice. When it comes to materials, is it possible to define in more detail the meaning of “sustainable materials management”? How would we know if a material (and its management) actually is “sustainable”? What would be the attributes of such a material? More broadly, how would we know if any action is sustainable? Various thinkers and organizations have proposed a variety of answers to these questions – sometimes specific to materials, other times about sustainability more broadly. This paper briefly introduces six different responses, and summarizes some of the advantages and limitations of each. The six responses are: • William McDonough and Michael Braungart’s “Cradle to Cradle” and philosophy of “Waste Equals Food” • Zero Waste • The Natural Step • The Ecological Footprint • The Sustainable Packaging Coalition’s “Definition of Sustainable Packaging” • Internalizing Externalities / Least-Cost Planning Cradle to Cradle and “Waste Equals Food” Summary: Architect William McDonough and chemist Michael Braungart popularized the theory of “Cradle to Cradle,” explained in their 2002 book Cradle to Cradle: Remaking the Way We Make Things. -
Upcycling Food Waste Is More Likely to Have Been Adopted by Start-Ups and Smaller Work from an Economic Perspective If It Is Players
With the food and beverage Upcycling industry under mounting pressure to cut upstream food waste, upcycling is an food waste interesting prospect. In this whitepaper we consider how to make it viable and effective. The reduction of food waste is a complex, but urgent, issue. Room for improvement According to the Food and Agriculture Waste and Resources Action Programme Organization of the UN (FAO), a third of food (WRAP) has estimated total volumes of produced globally each year - 1.3 billion tonnes - is avoidable food waste across sub-sectors of wasted or lost1. If current trends continue the UK food and beverage manufacturing unchecked, by 2030 66 tonnes of food will be lost industry (Figure 1)4. Dairy production came out or thrown away per second2. top, accounting for almost a quarter (23 As food waste increases, conversely there is a percent) of total avoidable food waste in the growing number of mouths to feed. In 2050 it’s UK. This was followed by meat, poultry and predicted that the world population will reach 9.6 fish which accounted for 18 percent. Ambient billion. Unless changes are made, there’s risk of a products were also in the top three, generating global food gap: production will be insufficient to 15 percent of avoidable waste. meet the calorific needs of humanity. The World Resources Institute (WRI) identifies reduction of food loss and waste as a top priority in its suggested measures for a sustainable food future*. It suggests a 25 percent improvement would reduce the food gap by 12 percent3. For the first time we have