<?xml version="1.0" encoding="UTF-8"?><rss version="2.0"
	xmlns:content="http://purl.org/rss/1.0/modules/content/"
	xmlns:wfw="http://wellformedweb.org/CommentAPI/"
	xmlns:dc="http://purl.org/dc/elements/1.1/"
	xmlns:atom="http://www.w3.org/2005/Atom"
	xmlns:sy="http://purl.org/rss/1.0/modules/syndication/"
	xmlns:slash="http://purl.org/rss/1.0/modules/slash/"
	>

<channel>
	<title>construction and demolition waste management &#8211; Science</title>
	<atom:link href="https://scienmag.com/tag/construction-and-demolition-waste-management/feed/" rel="self" type="application/rss+xml" />
	<link>https://scienmag.com</link>
	<description></description>
	<lastBuildDate>Sun, 06 Sep 2026 06:38:52 +0000</lastBuildDate>
	<language>en-US</language>
	<sy:updatePeriod>
	hourly	</sy:updatePeriod>
	<sy:updateFrequency>
	1	</sy:updateFrequency>
	<generator>https://wordpress.org/?v=7.1</generator>

<image>
	<url>https://scienmag.com/wp-content/uploads/2024/07/cropped-scienmag_ico-32x32.jpg</url>
	<title>construction and demolition waste management &#8211; Science</title>
	<link>https://scienmag.com</link>
	<width>32</width>
	<height>32</height>
</image> 
<site xmlns="com-wordpress:feed-additions:1">73899611</site>	<item>
		<title>Recycling concrete waste into resources for a sustainable circular built environment</title>
		<link>https://scienmag.com/recycling-concrete-waste-into-resources-for-a-sustainable-circular-built-environment/</link>
		
		<dc:creator><![CDATA[Sloane Callahan]]></dc:creator>
		<pubDate>Sun, 06 Sep 2026 06:38:49 +0000</pubDate>
				<category><![CDATA[Climate]]></category>
		<category><![CDATA[carbon emissions from cement production]]></category>
		<category><![CDATA[challenges in concrete recycling implementation]]></category>
		<category><![CDATA[challenges in concrete waste recycling]]></category>
		<category><![CDATA[Concrete recycling]]></category>
		<category><![CDATA[Concrete waste recycling]]></category>
		<category><![CDATA[construction and demolition waste management]]></category>
		<category><![CDATA[demolition debris conversion into building materials]]></category>
		<category><![CDATA[environmental impact of concrete disposal]]></category>
		<category><![CDATA[environmental impact of concrete waste]]></category>
		<category><![CDATA[environmental policy for construction waste]]></category>
		<category><![CDATA[global construction waste statistics]]></category>
		<category><![CDATA[innovative concrete recycling technologies]]></category>
		<category><![CDATA[life cycle assessment of recycled concrete]]></category>
		<category><![CDATA[policies for concrete debris reuse]]></category>
		<category><![CDATA[policy frameworks for waste reuse]]></category>
		<category><![CDATA[reducing carbon emissions from construction]]></category>
		<category><![CDATA[sustainable building materials]]></category>
		<category><![CDATA[sustainable circular construction]]></category>
		<category><![CDATA[sustainable circular economy in construction]]></category>
		<category><![CDATA[urbanization and construction debris]]></category>
		<category><![CDATA[urbanization and construction waste]]></category>
		<guid isPermaLink="false">https://scienmag.com/recycling-concrete-waste-into-resources-for-a-sustainable-circular-built-environment/</guid>

					<description><![CDATA[Concrete is the most consumed man-made material on Earth, and it is quietly burying us. Every year, the global construction sector generates roughly 2.36 billion tons of construction and demolition waste, and by some estimates waste concrete accounts for as much as 70 percent of that figure. Now, a systematic review published in the journal [&#8230;]]]></description>
										<content:encoded><![CDATA[<p>Concrete is the most consumed man-made material on Earth, and it is quietly burying us. Every year, the global construction sector generates roughly 2.36 billion tons of construction and demolition waste, and by some estimates waste concrete accounts for as much as 70 percent of that figure. Now, a systematic review published in the journal Clean Technologies and Environmental Policy has mapped out precisely why so little of this rubble is recycled, and what it would take to change that. Led by Margaret D. Oyewole of The Hong Kong Polytechnic University, together with Daniel W. M. Chan, Benjamin I. Oluleye and Tunde A. Folorunso, the study distills two decades of research into a framework that policymakers and industry practitioners can use to turn demolition debris back into building material.</p>
<p>The scale of the problem is difficult to overstate. The construction industry contributes an estimated 33 percent of global carbon emissions, driven by energy-intensive cement production, the depletion of non-renewable aggregates, and the sheer volume of debris generated by rapid urbanization. In regions experiencing construction booms, and in areas devastated by earthquakes or severe weather, mountains of broken concrete accumulate faster than they can be absorbed. Traditional disposal through landfilling is becoming untenable, as land grows scarce and disposal costs climb. Recycling, the authors argue, is the most viable circular-economy strategy available once a concrete structure reaches the end of its service life and direct reuse or refurbishment is no longer feasible.</p>
<p>The technical logic of concrete waste recycling is straightforward in principle. Demolished concrete is collected, sorted and processed through crushing, screening and contaminant removal, with steel reinforcement, impurities and off-specification particle sizes separated out. The output is a family of secondary materials: recycled coarse aggregates, recycled fine aggregates and recycled concrete powder. These can partially replace natural aggregates in new concrete mixes, and the fine powder can substitute for a portion of cement in suitable proportions. The environmental payoff is twofold: waste is diverted from landfill, and the demand for virgin aggregates and cement, both of which carry heavy carbon footprints, is reduced. Empirical studies cited in the review also point to economic benefits, including revenue generation, job creation and technological development.</p>
<p>Yet the reality on the ground is far less circular than the theory suggests. Following the Preferred Reporting Items for Systematic Reviews and Meta-Analyses, or PRISMA, methodology, the team searched the Scopus and Web of Science databases for English-language peer-reviewed publications from 2000 onwards. An initial haul of 1,642 records was progressively filtered down through language and year screening, duplicate removal and full-text assessment, ultimately yielding 65 scholarly publications for detailed analysis. These studies, published between 2004 and 2025, spanned 25 countries, with China contributing the most research (14 studies), followed by Australia (8), Malaysia (5), and the United Kingdom and Hong Kong (4 each). The geographic distribution reveals a striking imbalance: research on concrete recycling is heavily concentrated in parts of Asia, Europe and Oceania, while African and many developing-country contexts remain largely underrepresented in the literature.</p>
<p>From these 65 studies, the researchers identified 30 distinct barriers to concrete waste recycling, grouped into six categories: regulatory and policy, financial and economic, technical and technological, social and behavioural, market, and organizational and operational. Five barriers dominated the literature. High initial investment costs for recycling equipment and infrastructure were the most frequently reported, appearing in 14 studies. Close behind were poor quality and limited applications of recycled concrete products (12 studies), lack of comprehensive governmental regulations and guidelines (10), limited availability of advanced recycling technologies (10) and insufficient recycling facilities (10).</p>
<p>The quality problem deserves particular attention because it is fundamentally rooted in materials science. Recycled aggregates typically carry a layer of adhered cement mortar on their surfaces, which increases water absorption and porosity. This porous structure degrades the mechanical strength and durability of new concrete made with these aggregates, which is why recycled products are frequently restricted to lower-grade applications such as road base, pavements and drainage systems rather than structural concrete. Various treatment techniques have been developed to strip away the adhered mortar, including mechanical, thermal, chemical, microbial and supplementary cementitious material-based approaches. Among these, carbonation-based conditioning, in which recycled aggregates are exposed to carbon dioxide, has attracted growing interest because it can simultaneously improve aggregate performance and lock away carbon, contributing to emissions reduction.</p>
<p>Social and behavioural factors compound the technical ones. The review found that stakeholder resistance, ingrained preference for traditional practices, skepticism about recycled material quality and limited awareness of recycling benefits all slow adoption. Theoretical framing in the study draws on Diffusion of Innovation theory, which explains how new practices spread through social systems at different rates depending on perceived benefits, compatibility and complexity, and on Attitude theory, which holds that individual and collective attitudes shape behaviour. If industry leaders champion concrete recycling, the authors note, others are more likely to follow; conversely, misconceptions about recycled product quality can harden into industry-wide reluctance.</p>
<p>The study&#8217;s answer to these barriers is a set of 19 critical success factors organized into four domains. Legal and regulatory drivers include clear technical standards, quality certification systems, recycling targets, landfill restrictions, minimum recycled-content requirements, public procurement criteria and landfill taxes, all backed by enforcement, audits and accountability mechanisms. Economic and market drivers encompass grants, subsidies, tax reductions, competitive pricing of recycled aggregates and the strategic location of recycling centers near demolition sites to optimize transport logistics. Infrastructure and technology drivers involve government-supported land allocation for regional recycling hubs, investment in advanced processing technologies, and digital tools such as Building Information Modelling, RFID-enabled material tracking, material passports and AI-supported logistics platforms. Knowledge and education drivers include targeted professional training, public awareness campaigns, collaborative knowledge-sharing platforms, and pilot and demonstration projects that validate recycled concrete performance.</p>
<p>The most novel contribution of the review is its integrated conceptual framework, which links these success factors to the specific barriers they mitigate and assigns roles to the stakeholders across the concrete recycling value chain. Governments and regulatory authorities set policy direction and enforce standards. Construction and demolition enterprises practice selective demolition and waste segregation. Clients and project owners stimulate demand by writing recycled-content requirements into project briefs and tenders. Consultants and built-environment professionals influence material selection through design specifications. Recycling enterprises process the waste, concrete producers incorporate the resulting aggregates into new mixes, and educational institutions generate the evidence base and train the workforce. The public and non-governmental organizations round out the picture through awareness-building and implementation monitoring.</p>
<p>The authors are candid about the limitations of their work. The review drew only on Scopus and Web of Science, restricted to English-language publications from 2000 onwards, which may have narrowed the temporal, geographic and linguistic diversity of the evidence. The frequency analysis indicates how often barriers and success factors appear in the literature, not their relative severity or causal influence. Future research, they suggest, should empirically validate the framework across different regulatory and economic contexts, pursue longitudinal studies of policy instruments and market-development strategies, and pay far more attention to developing countries, where weak infrastructure and enforcement may shape recycling outcomes very differently.</p>
<p>Still, the message of the review is unambiguous. Concrete waste recycling is not merely a technical challenge to be solved with better crushers. It is a systemic problem requiring coordinated interventions across policy, finance, technology, markets and human behaviour. With the right mix of regulation, incentives, advanced processing and stakeholder collaboration, the rubble of yesterday&#8217;s cities could become the raw material of tomorrow&#8217;s, closing one of the largest and most stubborn material loops in the global economy.</p>
<div class="scienmag-article-metadata"><strong>Subject of Research:</strong> Barriers and critical success factors for concrete waste recycling implementation toward a circular economy in the built environment</p>
<p><strong>Article Title:</strong> From rubble to resource: overcoming challenges and drivers in concrete waste recycling for a sustainable circular economy in the built environment</p>
<p><strong>Article References:</strong> Oyewole, M. D., Chan, D. W. M., Oluleye, B. I., &amp; Folorunso, T. A. (2026). From rubble to resource: overcoming challenges and drivers in concrete waste recycling for a sustainable circular economy in the built environment. <em>Clean Technologies and Environmental Policy, 28</em>(9), Article 221. <a href="https://doi.org/10.1007/s10098-026-03565-x" target="_blank" rel="noopener noreferrer">https://doi.org/10.1007/s10098-026-03565-x</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s10098-026-03565-x" target="_blank" rel="noopener noreferrer">10.1007/s10098-026-03565-x</a></p>
<p><strong>Keywords:</strong> concrete waste recycling, circular economy, construction and demolition waste, recycled aggregates, barriers, critical success factors, built environment, sustainable construction, waste management, PRISMA systematic review</p>
</div>
]]></content:encoded>
					
		
		
		<post-id xmlns="com-wordpress:feed-additions:1">188530</post-id>	</item>
		<item>
		<title>Estimating uncertainty in end-of-life costs and embodied carbon of construction projects</title>
		<link>https://scienmag.com/estimating-uncertainty-in-end-of-life-costs-and-embodied-carbon-of-construction-projects/</link>
		
		<dc:creator><![CDATA[Sloane Callahan]]></dc:creator>
		<pubDate>Thu, 03 Sep 2026 20:20:01 +0000</pubDate>
				<category><![CDATA[Climate]]></category>
		<category><![CDATA[benchmarking and cost performance in construction]]></category>
		<category><![CDATA[carbon emission reduction in construction projects]]></category>
		<category><![CDATA[carbon emissions in construction sector]]></category>
		<category><![CDATA[circular economy in construction]]></category>
		<category><![CDATA[construction and demolition waste management]]></category>
		<category><![CDATA[Construction environmental impact assessment]]></category>
		<category><![CDATA[construction industry environmental impact]]></category>
		<category><![CDATA[construction project sustainability benchmarking]]></category>
		<category><![CDATA[deconstruction and material reuse]]></category>
		<category><![CDATA[embodied carbon in building materials]]></category>
		<category><![CDATA[environmental footprint of construction projects]]></category>
		<category><![CDATA[environmental impact of construction industry]]></category>
		<category><![CDATA[estimating end-of-life construction costs]]></category>
		<category><![CDATA[estimation of end-of-life construction costs]]></category>
		<category><![CDATA[life cycle assessment of buildings]]></category>
		<category><![CDATA[lifecycle cost analysis of buildings]]></category>
		<category><![CDATA[reducing embodied carbon through circular practices]]></category>
		<category><![CDATA[structural salvage and reuse]]></category>
		<category><![CDATA[sustainability strategies in construction]]></category>
		<category><![CDATA[sustainable building deconstruction strategies]]></category>
		<category><![CDATA[uncertainty analysis in construction cost estimation]]></category>
		<guid isPermaLink="false">https://scienmag.com/estimating-uncertainty-in-end-of-life-costs-and-embodied-carbon-of-construction-projects/</guid>

					<description><![CDATA[The building and construction sector is one of the most environmentally consequential industries on the planet. According to the United Nations Environment Programme, it accounts for 37% of global carbon emissions and 34% of worldwide energy use, while also generating roughly 30% of the planet&#8217;s solid waste. The scale of the problem is staggering: the [&#8230;]]]></description>
										<content:encoded><![CDATA[<p>The building and construction sector is one of the most environmentally consequential industries on the planet. According to the United Nations Environment Programme, it accounts for 37% of global carbon emissions and 34% of worldwide energy use, while also generating roughly 30% of the planet&#8217;s solid waste. The scale of the problem is staggering: the United States alone produces 600 million tons of construction and demolition (C&amp;D) waste every year—double the amount of its municipal solid waste. Other regions report even more troubling figures. China generates approximately 2,300 million tons of C&amp;D waste annually, and the European Union produces 834 million tons. At the same time, the construction industry is an economic juggernaut, with global expenditures of roughly $10 trillion per year, making cost performance and benchmarking central to every project decision.</p>
<p>Against this backdrop, the circular economy has emerged as one of the most promising sustainability strategies in construction. Rather than demolishing buildings and sending the debris to landfills, circular approaches emphasize deconstruction—carefully disassembling structures so that beams, slabs, blocks, and other components can be salvaged, reused, remanufactured, or recycled in new projects. In some cases, this can simultaneously reduce embodied carbon (the emissions associated with producing construction materials), divert waste from landfills, and lower project costs. Yet industry practitioners remain hesitant, and one reason stands out above the rest: uncertainty. Cost is consistently identified by professionals as one of the main impediments to adopting carbon-reduction measures, and salvaged materials introduce a host of unknowns that virgin products simply do not have.</p>
<p>That uncertainty has now been quantified. A new study published in the open-access journal Cleaner Engineering and Technology by Alberto E. Pozzer, Nikiforos Repousis, Fernanda Leite, and Christopher Rausch presents the first comprehensive framework for measuring the uncertainty in both embodied carbon and cost assessments for reclaimed construction products. The research addresses a glaring gap in the scientific literature. While previous studies have applied uncertainty analysis to the manufacturing of construction materials, to whole-building product stages, and even to full project lifecycles, none had extended that analysis to the end-of-life and &#8220;beyond-life&#8221; stages—where materials from one project are salvaged and given a second life in another.</p>
<p>The central hypothesis of the research was straightforward but consequential: reused products likely have a lower mean embodied carbon and cost compared with virgin materials, but they inherently carry higher variability. If that variability goes unmeasured, procurement decisions based on average values alone could be misleading, or even wrong. As the authors put it, quantifying this spread is essential to ensure &#8220;meaningful and transparent procurement decision-making.&#8221; The study also posed a follow-up question with real-world implications: does a higher level of uncertainty itself influence whether decision-makers choose circularity in the first place?</p>
<p>To model that uncertainty, the researchers turned to Monte Carlo simulation, a computational technique that has become the workhorse of uncertainty analysis in lifecycle assessment (LCA). Rather than producing a single deterministic estimate of embodied carbon or cost, Monte Carlo simulation treats key input parameters as random variables, each characterized by a probability distribution. The model then generates random samples from these distributions—10,000 iterations in this study, a figure consistent with prior research showing that results converge at that scale—yielding thousands of possible outcomes. From these, the team derived means, standard deviations, and full probability density functions describing the range of plausible results.</p>
<p>Identifying which variables to model was itself a substantial undertaking. Drawing on a scoping review of prior literature, the researchers distilled the uncertainty sources specific to salvaged materials into measurable variables across four scopes: project end-of-life, transportation, reclaimed material properties, and beyond-life pathways. At the project end-of-life stage, the uncertainty of the deconstruction schedule and the emission factors of the equipment used become critical, since deconstruction demands more detailed planning than conventional demolition, and studies have flagged risks such as inaccurate labor estimates, insufficient skilled workers, and inadequate heavy equipment. Transportation introduces variability in distances and vehicle emission factors. The reclaimed materials themselves bring perhaps the thorniest uncertainties: their quantity, their properties—which the team modeled as a binary pass/fail against required conditions—and their durability, expressed as an uncertain remaining service life. Finally, the beyond-life stage adds scenario alternatives (reuse, recycling, remanufacturing) and process emission factors.</p>
<p>The study adopted a pragmatic approach to characterizing these variables statistically. Using @RISK, a Microsoft Excel–based risk analysis tool, the team identified best-fitting probability distributions wherever sufficient data existed. Where data was sparse, they applied simpler distributions: uniform distributions when only minimum and maximum values were known, and triangular distributions when an expected value, minimum, and maximum were available. This flexibility matters, because previous work has shown that when Monte Carlo simulations exceed 10,000 iterations, results tend to converge regardless of whether inputs are characterized as normal, uniform, or lognormal—meaning the choice of distribution matters less than capturing the plausible range. For virgin materials, the team used the same uncertainty factors established in earlier studies of the product, transportation, and construction stages.</p>
<p>The lifecycle accounting followed ISO 14040 and ISO 14044 standards, organized into four stages: the product stage (A1–A3), covering raw material extraction, transportation, and manufacturing for virgin products; the use stage (B1–B5), covering maintenance, repair, replacement, and refurbishment for both virgin and salvaged materials; the end-of-life stage (C), covering deconstruction and transportation of reclaimed materials; and stage D, covering reuse and recycling. The embodied carbon equations summed material quantities multiplied by emission factors, equipment fuel consumption multiplied by fuel emission factors, and transportation distances multiplied by vehicle emission factors, with additional equations accounting for the project lifespan and the service life of reused components. The cost model mirrored the carbon model exactly, with emission factors replaced by unit costs—a structure aligned with traditional quantity-times-unit-price cost estimation. This parallel structure is significant, because cost estimates themselves suffer from uncertainty in cost data and gaps in project scope definition, yet cost uncertainty is rarely analyzed alongside carbon uncertainty.</p>
<p>To demonstrate the framework, the researchers built a case study anchored in real project data. The end-of-life data—schedule, equipment, transport logistics—came from a selective demolition project previously documented by Repousis, while emission factors were drawn from the OneClickLCA Building LCA software, an industry-standard tool containing a comprehensive repository of lifecycle inventory data and environmental product declarations. Equipment fuel consumption rates came from technical sheets and external sources. The beyond-life scenario was constructed by defining a hypothetical new project based on a masterplan, drawings, and specifications, allowing the team to simulate what would happen if the salvaged materials were incorporated into future construction.</p>
<p>The simulation results were then compared probabilistically. For each material alternative—new, reused, and recycled—the team computed the probability of not exceeding a reference embodied carbon and a reference cost established as project goals. This is the framework&#8217;s key innovation: instead of declaring one option &#8220;better&#8221; based on mean values, it tells decision-makers how confident they can be that a given option will actually meet their carbon and cost targets. A reused material with a lower average embodied carbon but wide variability may carry a lower probability of hitting a strict carbon target than a virgin material with a modest but tightly clustered footprint—and the framework makes that trade-off visible.</p>
<p>The significance of this work extends well beyond a single case study. The literature on concrete reuse illustrates why: reported carbon savings from reusing concrete elements have ranged wildly, from 40% to 82% across different studies, and some analyses of recycled aggregate concrete have even projected emissions increases rather than reductions. Case-specific studies—such as assessments of reusing concrete blocks for a pedestrian bridge, or repurposing beams, floors, columns, and hollow-core slabs—have demonstrated potential but never incorporated uncertainty analysis. Reviews of circular economy research have repeatedly flagged the lack of knowledge and data on the quality of recovered and recycled materials as a barrier to implementation, and have noted that the accuracy of LCAs for upcycling demolition waste is constrained by data uncertainty. Until now, however, no study had actually quantified that uncertainty.</p>
<p>The framework is also deliberately replicable. The authors emphasize that uncertainty sources in LCA are affected by geographical, temporal, and technological representativeness—emission factors vary by region, and practices for demolition, deconstruction, and transportation differ from one location to another. The value of the approach, therefore, lies not only in the results of this particular case but in providing a method that practitioners can adapt to their own projects, plugging in locally relevant input variables. There are limits, too: the study deliberately excludes supply chain and market dynamics—demand fluctuations, supplier availability—although the authors acknowledge these external factors as important candidates for future research.</p>
<p>What emerges is a practical answer to a question that has long haunted sustainable construction. Reused materials do tend to offer lower average embodied carbon and cost, but that advantage comes wrapped in variability that must be measured, not ignored. By quantifying that variability, the new framework gives architects, engineers, and contractors a way to weigh circular options with their eyes open—transforming salvage from a leap of faith into a calculated, transparent decision.</p>
<hr />
<div class="scienmag-article-metadata"><strong>Subject of Research:</strong> Quantifying uncertainty in embodied carbon and cost assessments for salvaged and reclaimed construction materials across end-of-life and beyond-life lifecycle stages</p>
<p><strong>Article Title:</strong> Quantifying Uncertainty in Cost and Embodied Carbon for the End-of-Life and Post-Use Phases of Construction Projects</p>
<p><strong>Article References:</strong> Pozzer, A. E., Repousis, N., Leite, F., &amp; Rausch, C. (2026). Quantifying Uncertainty in Cost and Embodied Carbon for the End-of-Life and Post-Use Phases of Construction Projects. <em>Cleaner Engineering and Technology</em>, Article 101308. <a href="https://doi.org/10.1016/j.clet.2026.101308" target="_blank" rel="noopener noreferrer">https://doi.org/10.1016/j.clet.2026.101308</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1016/j.clet.2026.101308" target="_blank" rel="noopener noreferrer">10.1016/j.clet.2026.101308</a></p>
<p><strong>Keywords:</strong> embodied carbon, construction and demolition waste, circular economy, Monte Carlo simulation, lifecycle assessment, salvaged materials, deconstruction, uncertainty analysis, sustainable construction, cost estimation</p>
</div>
]]></content:encoded>
					
		
		
		<post-id xmlns="com-wordpress:feed-additions:1">186678</post-id>	</item>
	</channel>
</rss>
