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Building materials are not legally protected from future destruction and demolition.

Created on 21-11-2024

Design, planning and building Policy and financing
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Political challenges lie in legally protecting buildings and housing from future destruction. Currently, designing housing to be circular – with the intention for future disassembly and reuse – does not guarantee the current or future asset owner will not choose to demolish. Demolition is common practice and in fact at times rewarded. In the UK for example, new build projects, which often entail demolition, are exempt from Value Added Tax (VAT) in contrast to refurbishment projects. Retention of whole buildings should be prioritised, and where feasible building parts, such as the structure should be saved from demolition.

Systems knowledge

Actors

National government

This actor represents the central governing body and authority responsible for overseeing and managing the affairs of a nation, including policymaking, legislation, and implementation within a certain geographic area.

Architects and designers

Policy makers

Policy makers are individuals or groups responsible for developing and implementing strategies, regulations, and initiatives aimed at addressing housing-related issues within a given region or jurisdiction. Their primary role is to create policies that influence housing affordability, accessibility, and quality, while also considering social, economic, and environmental factors.

Method

Sustainability assessment systems

Frameworks, tools or methodologies used to assess and measure the sustainability performance of various entities, such as buildings, infrastructure projects, organisations and communities. These systems help assess and quantify environmental, social and economic impacts so that stakeholders can make informed decisions and improve sustainability practises.

Policy reform

This refers to the process of making changes, revisions, or amendments to existing policies, laws, or regulations to improve their effectiveness, relevance, or desirability of outcomes.

Tools

Sustainability assessment systems

Frameworks, tools, or methodologies used to assess and measure the sustainability performance of various entities, such as buildings, infrastructure projects, organisations, and communities. These systems help assess and quantify environmental, social and economic impacts so stakeholders can make informed decisions and improve sustainability practices.

Building Information Modeling (BIM)

Material Passports

Framework

A framework is a structured set of guiding principles providing a foundation for understanding, solving problems, or making decisions in a specific context, serving as a fundamental structure to guide processes and actions.

Survey

Target knowledge

Topic

Building regulations

A set of government-mandated standards, rules, and requirements that define how building and construction projects should be designed and executed.

Building sustainability

The practise of designing, constructing and operating buildings in a way that minimises their negative impact on the environment and promotes long-term environmental, social and economic sustainability.

Environmental sustainability

The responsible and balanced use of environmental resources to ensure that they are conserved and available for present and future generations. It involves protecting and conserving the natural environment while promoting human well-being.

Housing policy

Housing policy refers to a set of rules, regulations, and government initiatives designed to address various aspects of housing, including affordability, accessibility, quality, and housing market stability. These policies are developed to guide and influence the housing sector to meet the housing needs of a specific population or region, and they can encompass a wide range of measures, from subsidies and zoning regulations to support for affordable housing and addressing homelessness.

Dimension

Institutional

The structure of government institutions that have the responsibility and power to create building regulation and monitor compliance with them

Environmental

This dimension focuses on understanding and addressing the environmental challenges and concerns related to human activities and their impact on the natural world.

Governance

This involves networks, systems and processes that steer decision-making, service delivery and policy implementation.

Level

Building

The structure, project or development that is directly impacted by the various building regulations.

Country

The political structure governs a specific geographical area and accommodates a specific population group.

Transformation Knowledge

Policy

Fostering more industrialized/off-site approach to construction

Decarbonization strategy

Policies can contribute to advancing sustainability in housing provision

Advocacy to evidence-based policies and cooperation

Related cases

Related vocabulary

Sustainability

Circular Economy

Life Cycle Assessment (LCA)

Area: Community participation

Contemporary scholars generally accept the multidimensional understanding of sustainability - social, political, economic, cultural and environmental amongst other dimensions – but the concept used to be defined more narrowly as the ‘conservation of natural resources’ and the ‘restoration of ecological balance’ (Meadows et al. 1972). While the ‘Brundtland Report’ was instrumental in broadening the definition and bridging the environmental and economic dimensions (WCED 1987), it was Elkington who stressed the social dimension in the ‘triple bottom line’ of ‘people, planet, profit’ (1998). However, the role of community participation as an elementary part of social sustainability was only established after the turn of the millennium by Giddings et al. (2002). They emphasised the participation aspect of procedural equity “so that people are able to shape their own futures” (ibid., p.194). Dempsey et al. (2011) drew upon this contribution when they considered urban sustainability from a community approach and concluded that communities thrive upon social interaction between community members, organisational initiative through collective groups and networks, the relative stability of a neighbourhood in terms of net migration and turnover, a positive identification or sense of place and the level of trust that follows from a perception of safety. These factors are summarised by Dixon and Woodcraft (2013, p.475) as “the extent to which a neighbourhood supports individual and collective well-being (…) It combines design of the physical environment with a focus on how the people who live in and use a space relate to each other and function as a community”. While most community participation researchers look into social sustainability on the neighbourhood level, Putnam’s book ‘Bowling alone’ (2000) described how a lack of social capital, here understood as strong civic participation and localised empowerment, could prevent collective action and undermine democracy on the macro-level. 

Created on 21-07-2021

Author: T.Croon (ESR11), J.Hoekstra (Supervisor)

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Area: Design, planning and building

Circular Economy (CE), also referred to as circularity, is a sustainability concept applied to various industries – including the built environment – which aims to improve the way products are made and consumed, and essentially to prevent the unnecessary destruction of resources. The CE idea is founded on the rejection of the current take-make-waste model and instead supports a system that is “restorative or regenerative by intention and design” (EMF, 2013, p.7). The European Commission defines CE as “a system which maintains the value of products, materials and resources in the economy for as long as possible and minimises the generation of waste” (EUR-Lex, 2021). CE builds upon concepts such as Cradle-to-Cradle (McDonough & Braungart, 2002) and The Performance Economy (Stahel, 2010). The term has recently grown in popularity, as evidenced in a study by Kirchherr et al., who identified 221 CE definitions, though the meaning of the term remains largely ambiguous (2023). CE encompasses both design and business considerations to better ensure products are responsibly managed and retained at their highest value possible within the value chain, rather than being destroyed. Business strategies include shifting consumption from selling products to services; this can take the form of Product-as-as-Service models or take-back schemes (Tukker, 2015). Several prominent theoretical frameworks support the CE transition, these include the R-Ladder outlining a decision-making hierarchy (Potting et al., 2017), the Ellen MacArthur Foundation’s Butterfly diagram which distinguishes technological materials from biological materials (EMF, 2013), and Bocken et al.’s four strategies defining the need to close, slow, narrow, and regenerate resource loops (2016). Key circular construction approaches that facilitate circularity in a systematic way include design for disassembly and industrialised construction. Several political instruments under the European Green Deal promote the progression towards a circular economy in buildings and housing, most notably the Circular Economy Action Plan (European Commission, 2020) and the Waste Framework Directive (EC, 2008). Despite these initiatives and the potential for the CE transition to improve both the environmental sustainability and affordability of housing, it is still in the early stages in Europe. This is largely due to building complexity, short-term financial barriers, and the persistence of common practices such as the extraction of raw materials and building demolition. However, several practical advancements that have been implemented include Circular Economy Statements within the London Plan (GLA, 2022), the Building Circularity Indicator (BCI) in the Netherlands (Alba Concepts, n.d.), and the Building Circularity Tool by OneClick LCA (n.d.).

Created on 30-09-2024

Author: A.Davis (ESR1)

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Area: Design, planning and building

Life Cycle Assessment (LCA) is a standardised method to comprehensively quantify environmental impacts caused by the production of goods and services, which can be used to inform decision-making in building design. Measurable indicators include Global Warming Potential (GWP), acidification, eutrophication, and water use to name a few (European Commission, 2010). LCA can be used to account for all input and output flows related to the entire building life cycle, from raw material acquisition, manufacture, use and maintenance (e.g. while the building is occupied), to the deconstruction and beyond End-of-Life phase (Sartori et al., 2021). Calculating an LCA requires information for building products and processes usually found in the Bill of Quantities, which includes the type of material and its density combined with the amount of material, measured in either volume or area. The European standard EN 15978 (2011) provides guidance for the calculation method, which breaks down the life cycle into phases A to D, these are: A Production and Construction, B Use, C End-of-Life, and D Beyond End-of-Life. It should be noted however, that it is difficult to compare different buildings using LCA, as methodologies and assumptions vary, impacting results (Ramboll, 2023). An LCA that includes stage D is known as a ‘cradle-to-cradle’ assessment, this supports a circular approach and considers scenarios relating to the building after its ‘useful service life’. It is crucial for stakeholders to consider the beyond End-of-Life impacts when planning and designing housing to support the circular economy transition, primarily through promoting future material reuse. LCA is an increasingly relevant component of sustainability assessments for buildings following demand for transparency from the construction industry and trends in performance-based design (Sartori et al., 2021). The LCA method has been incorporated into the European Level(s) framework (Dodd & Donatello, 2020), and BREEAM and LEED assessments. The European Commission advocates for LCA, describing it as the "best framework for assessing the potential environmental impacts of products" (European Commission, n.d.). LCA therefore plays an increasingly prominent role in supporting EU policy and meeting the ambitions of the European Green Deal and related initiatives, such as the Circular Economy Action Plan (European Commission, 2020). At the national level, several European countries utilise LCA to regulate embodied carbon, with other countries expected to follow suit in the coming years (Röck et al., 2022).

Created on 30-09-2024

Author: A.Davis (ESR1)

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Related publications

Davis, A. (2024). Circular Housing: Insights from Solar Decathlon Europe 2022. In European Network for Housing Research (ENHR) Conference 2024 [Poster Presentation]. Delft, the Netherlands.

Posted on 13-01-2025

Conference

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Blogposts

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Solar Decathlon Competition and LCA | Secondment with UPV

Posted on 27-10-2022

Leading up to the summer I completed my first secondment of three months at the Universitat Politènica de València (UPV), which was conveniently only a three-hour journey south along the Spanish coast from my host institution in Barcelona.   Life in Valencia involved drinking copious amounts of horchata (a local drink made from tiger nuts called Xufa) and enjoying Jardin del Turia, a park that was once a river which today hosts attractions such as gardens, sports facilities, and futuristic cultural buildings designed by architect Santiago Calatrava. I had the pleasure of working with my co-supervisor Ignacio Guillén and Life Cycle Assessment (LCA) expert Alberto Quintana Gallardo, Ph. D. in the department of Applied Physics. Together they provided excellent support with my plans to investigate housing projects from this year’s Solar Decathlon competition and to learn and apply LCA to built case studies during my stay.   As my project investigates Design for Disassembly (DfD) – in addition to Industrialised Construction – the Solar Decathlon competition was an exciting and unique opportunity to observe the disassembly and reassembly of sustainable homes, including the Spanish entry from team Azalea at UPV. As a former practicing architect where I worked with sustainability consultants who normally carry out LCA’s, I was also very eager to learn how to actually do an LCA myself.   Solar Decathlon So what is the Solar Decathlon competition? It is an international competition where teams from universities build prototype homes known as ‘House Demonstration Units’ (HDU) that showcase the best in innovation and energy efficiency using renewable energy. Although the design aspect of the competition focusses on minimising operational carbon, the build challenge requires teams to first construct their HDU at a site in their home country, disassemble it, then transport and reassemble it in only two weeks at the competition site, also known as the Solar Campus. This means designing for disassembly is integral to the competition, making it a fantastic opportunity to study how housing can be more resource efficient over the building life cycle and understand practical building issues.   The competition and reassembly of the houses took place this year in May at the Solar Campus in Wuppertal, Germany. The 16 teams that made it to the build phase heralded from the Netherlands, France, Sweden, Romania, Czech Republic, Turkey, Taiwan, Germany itself, and of course Spain.   I seized the opportunity to observe and ask questions about the disassembly process, the reassembly process, and carry out interviews with each of the Solar Decathlon teams. When I arrived at UPV at the start of May, Team Azalea from UPV had finished building their HDU called the Escalà project on campus and had just held their inauguration event. Over the first two weeks of my secondment, I visited the house every day whilst it was slowly disappearing as it was taken apart and loaded onto five trucks headed to Germany, where the team would shortly reassemble it all over again! During this time, I got to know the team members who had bonded immensely during the intense competition period until this point. Before heading to Wuppertal myself, I was able to pilot interview questions covering technical and environmental sustainably aspects of the project with the Azalea team, as well as remotely with the SUM team from TU Delft.   The energy at the Solar Campus in Wuppertal was palpable as the teams were busy reassembling their HDU’s, each had an internal floor area of around 70m2 to give an idea of scale. I quickly got to know each of the projects and schedule interviews with the 16 teams, who kindly volunteered their time during the middle of the hectic reassembly period before the houses were judged and opened to the public. I managed to interview 13 teams on-site (the remaining teams were later interviewed online), including participants from different fields and both students and professors. Each team had a unique solution to the brief which called for either vertical and horizontal extensions or in-fill proposals. It was not only insightful but a pleasure speaking with true pioneering experts in housing designed for disassembly. Now’s time to complete the analysis of all that data!   Check out my Instagram highlights of SDE-22 for some on-the-ground footage.   LCA Life Cycle Assessment (LCA) is an increasingly popular methodology and decision-supporting tool used by industry professionals and scholars to measure and compare the environmental impacts of buildings (European Commission, 2010). An LCA can be used to calculate Whole Life Carbon (WLC), which includes both embodied carbon from all the materials, processes, and transport to construct buildings and the operational carbon produced whilst a building is inhabited. WLC assessments are crucial to set environmental targets to decarbonise our building stock. There is currently a big knowledge gap around LCA amongst architectural practitioners and other stakeholders involved in the delivery of housing, partly due to the time-consuming nature of LCA’s. An LCA can be calculated simply with an excel spreadsheet or using various online platforms and plug-ins such as OneClick LCA, but amongst scholars more heavy software is called for, such as SimaPro – which is was what I would be learning to use whilst at UPV. My aim here was to carry out cradle-to-cradle LCA’s of case studies to quantify the benefits of DfD and the consideration of different lifespans for different parts of the building.   Work began on the first case study of a house designed and delivered by my co-supervisor Ignacio Guillén called Edificación Eco-Eficiente, or ‘EEE’, this was awarded a Class A energy rating and was the first single-family home in Spain to achieve the maximum VERDE* rating of 5 leaves. EEE was built using Industrialised Construction and prefabricated 2D elements that were assembled on-site in only 19 days. I was also able to visit the house on the UPV campus, though due to security reasons it can’t be used as a living-lab, which is a shame as it could provide some great in-use data on energy efficiency!   Using Simapro was (and still is) a steep learning curve with an incredible amount of precise and technical information that needs to be included. Imagine having to enter every single built element manually into a software, and not just modelled 3D objects but also coatings such as the surface area of zinc needed to galvanise steel, the grouting between tiles… the list goes on. Needless to say, LCA is an invaluable tool and will contribute greatly to my doctoral research project.     ¡Hasta pronto! I will be seeing my colleagues in Valencia again next month for the VIBRArch conference held by UPV to present my ongoing work on LCA. My secondment was invaluable in learning new skills and creating connections, particularly through the Solar Decathlon competition that I am continuing to follow up. Thank you to everyone at UPV, the Azalea team, and Solar Decathlon participants who provided such positive experiences and research opportunities!      *VERDE is a sustainability certification developed by Green Building Council Spain     Bibliography   Solar Decathlon Europe Competition website and knowledge platform with previous year’s entries https://sde21.eu/sde21 https://building-competition.org/   Team Azalea’s Instagram page and website https://www.instagram.com/azaleaupv/?hl=en   https://www.azaleaupv.com/   London Energy Transformation Initative ‘LETI’ provide an excellent embodied carbon primer for further reading on Whole Life Carbon   https://www.leti.uk/_files/ugd/252d09_8ceffcbcafdb43cf8a19ab9af5073b92.pdf     References European Commission. (2010). ILCD Handbook - General Guide for Life Cycle Assessment: Detailed Guidance (1st ed.). Publications Office of the European Union.  

Author: A.Davis (ESR1)

Secondments

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WasteBuild Zero conference in Amsterdam

Posted on 18-05-2023

During my current secondment in the Netherlands at TU Delft, I attended the two-day WasteBuild Zero conference at the NSDM in Amsterdam, which pushes circularity in the built environment to the forefront. There was so much to unpack after many great presentations and panel discussions with people passionate about sustainability. Speakers included practicing architects, engineers, deconstruction and demolition experts, sustainability experts, economists, and researchers. Here are some of my key takeaways:   Defining circularity: There are inconsistent ways to calculate circularity across industries and stakeholder groups, it still needs to be defined with a series of agreed metrics and measures. Embodied carbon on the other hand has clear metrics, but few countries regulate it*. Economic incentive: Circular construction and bio-based materials are more expensive; we need to make these solutions more attractive. This can be achieved by shifting taxation from labour to resources. Otherwise, demolition and downcycling are inevitable. In the UK the problem of 20% VAT levy on reuse and refurbishments as opposed to zero on demolition or new-build needs to be fixed. A lack of timber industry: For designers to responsibly specify mass timber (which also sequesters carbon) that doesn’t incur excessive embodied carbon in transport, countries other than Austria and Scandinavia need their own local timber industries. Early interdisciplinary engagement: Figuring out solutions and identifying opportunities for material reuse early-on makes it more likely to be cheaper. Demolition teams and contractors have a lot of knowledge and should lead in strategies from the get-go. Furthermore, demolition companies should also provide a disassembly team to minimise destruction and increase reuse. Flexibility: The design, budget, and scope should have more flexibility and not be fixed to test new methods and products to innovate and challenge the status quo. Pre-demolition audits: Documenting all existing materials on-site helps them go back into the supply chain, maximise reuse and know-how, and should inform the design process. Waste classification: Bodies such as the Environmental Agency are preventing the reuse of existing materials on-site such as excavated clay to make earth-blocks and tiles - there were several examples of this presented in case studies. Procurement: Contractors are not incentivised to incorporate reuse and accept a higher level of risk. Tender documents should also state on the first page the requirement for second-life materials, if it’s on page five it won’t get looked at. Warranties: We need more protocols and standardisation to speed up the warranty process, otherwise each material must be tested which takes too long and is too expensive. Risk engineers and insurers should be engaged early on. If possible, try to involve the company that originally produced the material/product. Supply chains: There is a huge gap in the supply chain, lots of materials are available but performance criteria and a lack of warranties prevent reuse. The supply chain should provide a breakdown of materials and as-built information, and should be engaged to take materials back and remanufacture them. Material passports: These are key at the demolition/disassembly and preparation stage, but there is concern over the level of information needed, it is useful at an element level (products made from few materials) otherwise we could get bogged down with too much data.   It’s tough for construction teams to make sustainable choices when we are living and working in a broken system, where it is currently acceptable to landfill almost absolutely everything and it’s often cheaper and easier to source products from China than to reuse local materials. Architects cannot rely on ‘enlightened clients’ during the continued climate crisis, to quote Hans Hammink from De Architekten Cie, we should rethink the role of the architect as “protector of materials”.   Lastly, the lack of information sharing is holding back more widespread and urgent change, research in industry is usually confidential and money is still the main driver. The transition to a circular economy will require a true sharing economy of both materials and knowledge, and we need to ensure lessons learnt are also looped back into the cycle.   See you next year WasteBuild!   *The Architects Climate Action Network UK are continuing to push forward a bill to regulate embodied carbon: https://www.architectscan.org/embodiedcarbon

Author: A.Davis (ESR1)

Conferences, Secondments

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