Fundamentals of Building Deconstruction As a Circular Economy Strategy for the Reuse of Construction Materials
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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. -
Vermiculite Concrete Introduction Vermiculite Concrete Is a Low Density Non-Structural Construction Product
Vermiculite Concrete Introduction Vermiculite concrete is a low density non-structural construction product. It is insulating (both thermally and acoustically) and intrinsically fire resistant. It is normally made simply by mixing exfoliated vermiculite as the aggregate, with cement and water, plus additives such as plasticisers if required. The ratio of exfoliated vermiculite aggregate to cement and the vermiculite grade can be varied to the properties such as strength and insulation as required for the concrete. The applications for vermiculite concrete are however, all non-structural. Vermiculite concretes can also be produced containing other lightweight aggregates, such as expanded perlite, to give differing physical properties. Normally the type of cement used in these mixes is Ordinary Portland Cement (O.P.C), although a higher initial strength may be obtained using Rapid Hardening Portland Cement (R.H.P.C). For high temperature refractory applications, high alumina (luminate in the USA) cements may be used with great success to manufacture lightweight in-situ cast insulation mixes and back up insulation products. However, these applications are beyond the scope of this specific application note. Applications for Vermiculite Concrete The principal applications for vermiculite concrete are for in-situ site mixed applications such as: • Floor and roof screeds • Void filling insulation mixes around chimneys, back boilers and fire backs • Blocks and slabs • Swimming pool bases [see separate application note for this application] Vermiculite concrete can be easily cut, sawed, nailed or screwed. The lower density vermiculite concrete screeds are usually covered with a denser topping mix of 4:1 or 5:1 sand to cement mix to a minimum depth of 25mm (1 inch); the screed and denser more load distributing topping should ideally be laid monolithically to prevent dis-bonding and shear fracturing between the screed and the topping. -
Recycling of Autoclaved Aerated Concrete in Screed and Stabilized Sand
RECYCLING OF AUTOCLAVED AERATED CONCRETE IN SCREED AND STABILIZED SAND Jef Bergmans1, Peter Nielsen2, Kris Broos3, Ruben Snellings4, Mieke Quaghebeur5 1 Researcher, VITO, [email protected] 2 Senior Researcher, VITO, [email protected] 3 Team Leader, VITO, [email protected] 4 Researcher, VITO, [email protected] 5 Program Manager, VITO, [email protected] ABSTRACT Autoclaved aerated concrete (AAC) is a lightweight cellular concrete that has been used for more than 80 years. Currently, however, no good recycling options for AAC from construction and demolition waste exist. The amount of AAC waste that can be recycled in the production of new AAC is limited because of quality issues. Furthermore, recycling AAC into traditional concrete or as unbound aggregate causes both technical and environmental problems because of the low compressive strength (2-8 MPa) of AAC and its high amount of leachable sulfate: typically > 10,000 mg/kg dm (L/S = 10). In this paper, recycled AAC waste was evaluated as a replacement of sand in a traditional screed (subfloor) and in cement stabilized sand products. A range of cements (CEM I, CEM II and CEM III), were used in combination with the crushed AAC waste aggregate (0-8 mm). During hydration a reaction of the AAC leachable sulfate and the aluminate contained in the cement resulted in the formation of (insoluble) ettringite. The main conditions influencing the formation of ettringite, and hence the leaching of sulfate, were examined in cement stabilized sand products. A sufficiently high pH was found to be crucial to meet sulfate leaching standards. -
5 Steps to Responsible E-Waste Management at Your School
By Caprice Lawless Steps to Responsible E-waste 5 Management at Your School aste management infra Step 1. Educate yourself about local, national, and international legislation. structure is expanding While recycling standards and certifications are still in the developmental stag Was we wrestle with how es, many cities and states are leading the way with ambitious and comprehen best to gather, sort, and recycle the sive programs addressing the situation. California’s landmark Electronic Waste 50 million tons of e-waste we are Recycling Act of 2003, for example, requires retailers to collect a fee from con generating annually worldwide. sumers on covered electronic devices. The fees are then submitted to the state Awareness and education are the to pay for recycling efforts. first steps, followed by programs In February 2008, New York City became the first U.S. city to pass a manda and industries to address the issue. tory producer-responsibility ordinance. The law requires computer, TV, and Schools, districts, and colleges of MP3 manufacturers to take responsibility for the collection of their own elec education contribute their share of tronic products for New Yorkers who discard 25,000 tons of e-waste each year. e-waste and need to be concerned In January 2008, New Jersey joined California, Connecticut, Maine, Minnesota, with its disposal, but they can also North Carolina, Oregon, Texas, and Washington, in passing “take-back” laws put into place their own refurbish requiring manufacturers to collect and recycle e-waste. It is already illegal to ing programs and partnerships and dump e-waste in 10 states, with similar legislation pending in many others. -
Estimating the Deep Decarbonization Benefits of the Electric Mobility Transition: a Review of Managed Charging Strategies and Second-Life Battery Uses
Estimating the Deep Decarbonization Benefits of the Electric Mobility Transition: A Review of Managed Charging Strategies and Second-Life Battery Uses Matthew D. Dean1 and Kara M. Kockelman, Ph.D., P.E.2 1Department of Civil, Architectural and Environmental Engineering, University of Texas at Austin, 1 University Station (Mail Code C1761), Austin, TX 78712; email: [email protected] 2Department of Civil, Architectural and Environmental Engineering, University of Texas at Austin, 1 University Station (Mail Code C1761), Austin, TX 78712; email: [email protected] ABSTRACT Emissions-reduction pathways in transportation are often characterized as a “three-legged stool”, where vehicle efficiency, fuel carbon content, and vehicle miles traveled (VMT) contribute to lower emissions. The electric mobility (e-mobility) transition provides fast savings since plug-in electric vehicles (PEVs) are nearly three times more energy efficient than internal combustion engines (ICEs) and most nations’ power grids are lowering their carbon intensity irrespective of any further climate policy. The transportation sector’s greenhouse gas (GHG) savings via electrification are subject to many variables – such as power plant feedstocks, vehicle charging locations and schedules, vehicle size and weight, driver behavior, and annual mileage, which are described in existing literature. Savings will also depend on emerging innovations, such as managed charging (MC) strategies and second-life battery use in energy storage systems (B2U- ESS). This paper’s review of MC strategies and B2U-ESS applications estimates additional GHG savings to be up to 33% if chargers are widely available for MC-enabled passenger cars, and up to 100% if B2U-ESS abates peaker plants over its second-use lifetime. -
The EPR Trilogy
The EPR Trilogy ©2012 Nancy Gorrell Together At Last: Extended Producer Responsibility (EPR) and Total Recycling Total Recovery for Reuse, Recycling, and Composting: How to Make It So Extended Producer Responsibility in British Columbia – A Work at Risk These articles were written individually for publication elsewhere and are collected here pre-publication for distribution to attendees at the Northern California Recycling Association’s Recycling Update XVII, March 27, 2012. They are presented in the order written. The EPR Trilogy, Urban Ore, for NCRA’s Recycling Update March 27, 2012 1 ©2012 Nancy Gorrell©2012 The authors and artist retain their copyrights. Booklet ©2012 Urban Ore, Inc. 900 Murray St., Berkeley, CA 94710 http://urbanore.com No part of this publication may be reproduced without written permission from the appropriate copyright owner. 2 The EPR Trilogy, Urban Ore, for NCRA’s Recycling Update March 27, 2012 Together At Last: Extended Producer Responsibility (EPR) and Total Recycling Daniel Knapp, Ph.D. years ago developed a rhetoric that The CPSC Webinar focused on just assumed recycling was in the way one commodity type: batteries. The and had to be set aside for EPR to speakers were actually part of the EPR versus Total Recycling. work. This rhetoric often resorted to battery reclamation supply chain in Sometime in the cold wet spring sloganeering: recycling was “so last various parts of California. My big of 2011, NCRA President Arthur century,” recycling “enables wasting.” takeaway from a day of listening: Boone set up what he hoped would They said EPR, pursued correctly, as EPR ideas are being tested and be a stirring and member-pleasing made recycling outmoded and refined in actual practice, reality is debate between opponents on the unnecessary, because products would forcing EPR and total recycling back EPR issue. -
Governments Struggle with Zero Waste Planning, Policy
GOVERNMENTS STRUGGLE WITH ZERO WASTE PLANNING, POLICY, AND IMPLEMENTATION The challenges faced by local to national governments that are planning for and implementing zero waste initiatives and the synchronicity necessary to achieve it. by BRIANNA BEYNART A thesis submitted to Johns Hopkins University in conformity with the requirements for the degree of Master of Arts. Baltimore, Maryland December 2019 © 2019 Brianna Beynart All Rights Reserved Abstract With growing concern over the shortage of landfill space and the health hazards of waste incineration, governments are looking towards sustainable waste management processes for the health of their communities. Zero waste is the goal to direct 100 percent of waste from landfills and incinerators, which is ultimately the most sustainable waste management strategy. Many governments have been working towards zero waste but none have achieved 100 percent waste diversion. Using a comparative context, it is the goal of this research to determine what planning practices are shared across varying levels of governments and from diverse geographic locations to determine what obstacles are preventing them from achieving 100 percent waste diversion. This research builds on the discoveries of each preceding finding and topics of this research include zero waste planning, waste management and processing methods, best practices for zero waste management, public outreach, public resource requirements for a zero waste community, and the role of the producer in the waste management cycle. The first section compares the zero waste plans of three American cities to reveal common best practices. Success was shared through outreach and the availability of public resources. The cities ultimately struggled to separate and process the waste after it had been collected. -
Chapter 8 - Concrete
Chapter 8 - Concrete Chapter 8 - Concrete Chapter 8 - Concrete Concrete is formed from a hardened mixture of cement, water, sand, rock, air and certain admixtures through the chemical reaction called Hydration. Chapter 8 - Concrete Nearly every structure constructed in SD will utilize concrete in one form or another. The chapter will cover concrete from the point it is delivered to the construction site in its plastic state to its use in its final position. Inspection at Plant: This is covered in the Concrete Plants Manual Haul ticket Project Material Date Truck Number Water: Maximum Water: Actual Batch Size Time Start Mix Inspector: Plant Revolution: Initial Inspection at Delivery Your inspection of the concrete begins when the concrete reaches the structure site. Your inspection focuses on items that affect the strength and durability of the concrete. You will be tasked with performing the fresh concrete testing and also to closely monitor the operations of the pour. Inspection at Delivery Time Limits Inspection items Amount of Mixing which ultimately Slump affect strength and durability of concrete Air Content Temperature Concrete Cylinders Unit Weight Time Limits If concrete placement takes too long, it will start to “set up”. The following limits have been specified: Concrete mixed in hauling unit (Redi-mix truck) 50 – 80o F Discharge within 90 min. & screed within 105 min. 80 – 90o F Discharge within 45 min. & screed within 60 min. Concrete not mixed in hauling unit (uncommon for structures) 50 – 80o F - Discharge within 45 min. & screed within 60 min. 80 – 90o F - Discharge within 30 min. & screed within 45 min. -
A 30-Day Roadmap to Zero Waste
#MAKEITAHABIT A 30-DAY ROADMAP TO ZERO WASTE www.greatforest.com What is Zero Waste? In short, Zero Waste is a holistic way of thinking that views materials as resources within a circular, closed-loop system. As officially defined by the Zero Waste International Alliance (ZWIA), Zero Waste is “The conservation of all resources by means of responsible production, consumption, reuse, and recovery of products, packaging, and materials without burning and with no discharges to land, water, or air that threaten the environment or human health.” Instructions This 30-day roadmap was developed to provide simple, actionable ways for you to get started on your Zero Waste journey from home. While Great Forest works to help businesses nationwide reduce waste and increase sustainability, we firmly believe that good zero waste habits and climate action starts at home. Each action within the roadmap can be completed independently of the other actions, we recommend following the order laid out to help reinforce Zero Waste-inspired themes that build on each other. Each action comes with a short description, simple tip(s), and resources for you to get started right away. The Great Forest consultant team had a fun time creating this toolkit and hope you will enjoy following along with us. The key is to get creative and involve your family, friends, and neighbors whenever possible! #MAKEITAHABIT Take stock of your Zero Waste journey. Assess your at-home waste footprint. Determining the amount of waste you produce through your daily routine is the first step to fixing it. This is one of those things you can't "un-know" once you know. -
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 -
A Review on Upcycling: Current Body of Literature, Knowledge Gaps and a Way Forward
Venice Italy Apr 13-14, 2015, 17 (4) Part I A Review on Upcycling: Current Body of Literature, Knowledge Gaps and a Way Forward Kyungeun Sung related books have been published since 1999.1 Most books Abstract—Upcycling is a process in which used materials are (96%; 115 out of 120 books) in the sample were published converted into something of higher value and/or quality in their between 2008 and 2014 with higher publication rate between second life. It has been increasingly recognised as one promising 2012 and 2014 as 62.5% of all samples (75 books between means to reduce material and energy use, and to engender sustainable 2012 and 2014; 21 books in 2012; 28 in 2013; and 26 in production and consumption. For this reason and other foreseeable benefits, the concept of upcycling has received more attention from 2014). 53% (64/120) of the sampled books are categorised as numerous researchers and business practitioners in recent years. This ‘craft and hobbies’ whereas the other book categories show has been seen in the growing number of publications on this topic similar percentages (art & design: 10%; house & home DIY: since the 1990s. However, the overall volume of literature dealing 10%; science & technology: 9%; business & economics: 8%; with upcycling is still low and no major review has been presented. and the rest as miscellaneous).2 The theses search on Google Therefore, in order to further establish this field, this paper analyses Scholar simultaneously conducted by the author showed a and summarises the current body of literature on upcycling, focusing similar recent surge of publication: 90% (37/41) of these in the on different definitions, trends in practices, benefits, drawbacks and 3 barriers in a number of subject areas, and gives suggestions for future sample (since 2001) were published between 2009 and 2014.