All official European Union website addresses are in the europa.eu domain.
See all EU institutions and bodiesDo something for our planet, print this page only if needed. Even a small action can make an enormous difference when millions of people do it!
Briefing
This briefing provides an overview of the links between circular economy and construction and demolition waste management and builds on a report compiled by the EEA and the European Topic Centre on Waste and Materials in a Green Economy (ETC/WMGE). For further details and underpinning references, read the ETC report. The EEA will continue to investigate the effects of circular economy actions on the construction sector. An additional briefing is expected to be published this spring and will explore the potential reduction of greenhouse gas emissions through circular actions in the construction sector.
C&DW is the largest waste stream in the EU in terms of mass (374 million tonnes in the EU-28, in 2016, excluding excavated soil). Data on C&DW generation, although not entirely credible, show that it has been relatively stable in recent years at the European level but that large variations in per capita generation exist across countries.
A circular economy represents a fundamental alternative to the linear ‘take-make-consume-dispose’ economic model that still predominates. This linear model is based on the assumption that natural resources are available, abundant, easy to source and cheap to dispose of. However, the linear model is not sustainable, as the world is moving towards (and is in some cases exceeding) planetary boundaries.
The circular economy is restorative in nature, and it aims to maintain the utility of products, components and materials for as long as possible while also retaining their value. It thus minimises the need for new inputs of virgin materials and energy, while reducing environmental pressures linked to resource extraction, emissions and waste management. This goes beyond just waste and requires natural resources to be managed efficiently and sustainably throughout their life cycles (EEA, 2016).
Driven by the recovery target of 70 % by 2020 (set by the 2008 Waste Framework Directive and defined as including all recycling and other recovery operations such as backfilling), countries report increasingly high recovery rates. Most of them exceeded the 2020 target in 2016.
Many EU countries have succeeded in establishing markets for recovered C&D materials. This may suggest that the European construction sector is highly circular, as it manages to reintroduce large quantities of its waste into the economy by avoiding disposal options such as incineration and landfilling. However, as a result of building practices in the past and the lack of generation of high-purity materials during demolition, currently the material streams arising from demolition and renovation works are not suitable for reuse or closed-loop recycling. This hampers full implementation of circular economy objectives.
In fact, closer scrutiny of the data reveals that the high recovery of C&DW is based, to a large extent, on backfilling (Figure 1) or on low-grade recovery, e.g. using recycled aggregates from the mineral part of C&DW on applications such as road sub-bases. Therefore, the inherent value of the materials composing C&DW is eroded, qualitative aspects of recycling are not systematically addressed and recycling is not performed in closed loops. The latter would help preserve the value of recycled materials.
Note: Recycling, backfilling, energy recovery, incineration and landfilling of the mineral part of construction and demolition waste presented as percentage of total treated waste.
There is a big potential for making C&DW management truly circular. This is consistent with the objectives of the 2015 circular economy action plan, which includes C&DW among the ‘priority’ waste streams.
Circular economy-inspired interventions focus not only on increasing recycling quantitatively but also on:
This would result in greater prevention of C&DW (as materials are kept in the economy as long as possible) and in a reduction in the (less circular) recovery of low-grade material.
Commission Decision 2011/753/EU defines backfilling as‘a recovery operation where suitable waste is used for reclamation purposes in excavated areas or for engineering purposes in landscaping and where the waste is a substitute for non-waste materials’.
In the revised Waste Framework Directive of 2018, the definition of backfilling is strengthened as ‘waste used for backfilling must … be limited to the amount strictly necessary to achieve those purposes’, which might limit the amount of material that will be reported as being backfilled in the future.
Backfilling can be considered low-quality recovery, as it replaces a natural resource (soil) that is abundant without high environmental impacts from its production.
The analysis of the examples presented above reveals that many have common barriers, preventing their implementation. New policy actions would be more effective if these barriers were taken into account. Removing these barriers would also have a direct effect in fulfilling the waste policy objectives and in adopting circular economy thinking by the sector.
What? |
Why? |
Potential |
Price competition with virgin alternatives |
Stakeholders tend to favour cheaper and credible solutions, and virgin (a) minerals are in many cases cheaper than secondary materials due to the latter’s processing costs |
A competitive secondary materials market would create demand for both quantity and quality of waste material, thus directly increasing circularity |
Confidence in quality and structural properties of secondary materials (traceability) |
Stakeholders tend to choose virgin materials that are quality assured through warranties and standards |
Engaging in the development of standards for secondary raw materials would increase the trust in their properties and quality |
Hazardous substances content |
Polluted materials are not suitable for recycling, and removal of the hazardous content is costly |
Develop technology for efficient removal of hazardous substances and eliminate use of hazardous materials in new construction |
Lack of sufficient and reliable data on (historical) buildings |
The composition of material streams from demolition activities cannot always be predicted |
Pre-demolition audits and, in the future, material passports help register the type and volume of materials in the existing building stock |
Time delay |
The time delay between implementing a circular action and its benefits due to the long life spans of buildings may discourage stakeholders |
Not applicable |
(a) Virgin materials are raw materials that originate from nature as opposed to secondary materials originating from waste processing.
A range of interventions are available to policymakers to facilitate the uptake of circular economy actions that will improve C&DW management. The following are examples of generic options that can be further specified as robust policy instruments and they broadly address all the barriers identified above.
For references, please go to https://www.eea.europa.eu/publications/construction-and-demolition-waste-challenges/construction-and-demolition-waste-challenges or scan the QR code.
PDF generated on 08 Dec 2024, 08:32 PM
Engineered by: EEA Web Team
Software updated on 26 September 2023 08:13 from version 23.8.18
Software version: EEA Plone KGS 23.9.14
Document Actions
Share with others