Scottish Ecological Design Association The Scottish Executive
Scottish Ecological Design Association

Design and Detailing for Deconstruction

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3 Building Resource Efficiency

3.1 Ecological principles
3.2 Natural and recycled resources
3.3 Energy
3.4 Waste: closing the loop
3.5 Regionalism


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Key Principles

1. Resource efficiency is an ecological issue – the rates of use of any material must be sustainable and aim to maintain diversity in design and supply.

2. Aim to minimise waste by designing elements for maximum diversity of options when re-used.

3. Know Your Place – nothing can replace intimate “local knowledge” in relation to designing for a particular place. Avoid monocultural deconstruction solutions for different sites – each site is unique in terms of climate and resources.

4. Aim to minimise waste by increasing the number of times a construction element can be
re-used.

5. Minimise transportation by allowing building to be fully adaptable with the minimum use of new resources. Avoid excessive transportation of materials.

6. Prefabrication maybe cost effective, but don’t forget the external pollution costs associated with transportation – aim for local prefabrication wherever possible close to the site.



3.1 Local knowledge

Reducing waste is the main aim of this guide. There is little point in advocating DfD to reduce waste, however, without full consideration of the sustainable design, wider waste reduction and ecological resource issues relating to place.

Ideally, the designer should be knowledgeable about the local region and ecology relating to the site, as well as understanding where the more remote construction materials are coming from, and what the ecological impacts of design decisions are on both a local and global scale.


3.2 Natural and recycled resources

All resources have an initial natural source, a rate of extraction, and a natural sink, where unusable waste finally rests. A key consideration is to ensure that our rate of extracting materials is not greater than the earth can naturally assimilate in any one place at any given time.

DfD should aim to reduce the rate of extraction of the construction materials by maximising the re-use of construction elements. This means “future-proofing” against waste and pollution as far as possible by considering future scenarios for building use. As DfD matures material cycles will be become more closed with waste products playing more and more of a role in the overall resourcing of construction materials.

Energy requirements for manufacturing and/or producing selected building materials

Material

kWh/tonne

kWh/m³

1. Fletton bricks

175

300

2. Non-fletton bricks

860

1,462

3. Engineering bricks

1,120

2,016

4. Clay tiles

800

1,520

5. Concrete tiles

300

630

6. Local stone tiles

200

450

7. Local slates

200

540

8. Single layer roof membrane

45,000

47,000

9. Concrete 1:3:6

275

600

10. Concrete 1:2:4

360

800

11. Lightweight blocks

500

600

12. Autoclaved blocks

1,300

800

13. Natural sand/aggregate

30

45

14. Crushed granite aggregate

100

150

15. Lightweight aggregate

500

300

16. Cement

2,200

2,860

17. Sand/cement render

277

400

18. Plaster/plasterboard

890

900

19. Steel

13,200

103,000

20. Copper

15,000

133,000

21. Aluminium

27,000

75,600

22. Timber (imported softwood)

1,450

754

23. Timber (local airdried)

200

110

24. Timber (local greenoak)

200

220

25. Glass

9,200

23,000

26. Plastics

45,000

47,000

27. Plastic insulation

 

1,125

28. Mineral wool

 

230

29. Cellulose insulation

 

133

30. Woodwool (loose)

 

900

Source: Pat Borer, Centre for Alternative Technology


Ideally the designer
should be
knowledgeable about
the local region -
each one is unique
Source: F. Stevenso
n


3.3 Energy

Embodied energy costs are a rough indicator of how much energy materials are using in DfD. Generally, the less energy used in the production of construction elements, the less impact there is on the environment.

It is often assumed that recycling construction products is just as energy efficient as re-using them, when this is in fact seldom the case. Recycling invariably involves re-processing, which in turn involves transport and manufacturing energy costs. A re-used element usually has virtually no embodied energy costs associated with re-processing, although transport needs careful consideration.

DfD can minimise energy costs by aiming to increase the number of times a construction element can be re-used without serious depreciation, loss of strength, rigidity and other factors associated with wear and tear. Durability has to be balanced against initial energy costs in manufacture and transport. Given that the re-use of building elements is highly unpredictable, it is still wise to always aim for low initial energy costs by using renewable materials where possible.

3.4 Waste –closing the loop

An industrial ecosystem mimics a natural ecosystem through an interacting web of inputs, processes and wastes which “close the loop” by turning wastes back into resources. DfD can close the waste loop in two ways; firstly by re-using existing construction elements where practical and secondly by encouraging the designed elements to be re-used easily and locally. Ideally DfD should be contained as far as possible within a given regional area, to minimise transportation and maximise the local economy.

In Scotland, the landfill situation is now critical, with local authorities having to resort to transporting waste further and further afield or else burning it and releasing pollution into the air. There are a number of construction product reclamation sites in Scotland and the North of England15 which should be scoured during the DfD process, if the design site is in Scotland.

3.5 Regionalism

Resources, energy, waste, transport and community are all interacting aspects of a regional approach to DfD. No aspect can be considered without thinking of the consequences for the other aspects on a local level. Bioregionalism takes this one step further by insisting on the inclusion of ecological aspects as well and recognising the differences between ecological systems in different regions.

Scotland can basically be divided into four broad regions, the North West, the North East, the South West and the South East, with the Central Belt region straddling between the North and South regions. Each region has its own unique “soft palette” of renewable, re-used, recycled and by-product construction materials which can be developed by working with other industries in the region. DfD can build on this by selecting from this palette. Visible re-use of certain locally made construction elements in appropriate locations within the building fabric can also preserve a deeper historic understanding of regional building construction practice.

DfD can help support communities in Scotland economically by keeping resource use and re-use as local as possible, thus retaining economic value within the region. For this purpose SEDA have helped to produce an information guide on local construction products and materials which are produced in Scotland [16].

Minimising transportation is key part of a successful DfD, given that we spend as much energy transporting our construction materials around the country as we do making them in the first place (see diagram over page).

There are clear differences between reclamation and DfD practice in different parts of Scotland, which is a relatively unpopulated country. The majority of industry and population is concentrated in the Central Belt region from Glasgow through to Edinburgh. This region is well resourced for a locally derived DfD approach, with numerous salvage yards and manufacturers. It makes sense for design projects in the Central Belt to source and reclaim their construction products from within the region. Rurally, DfD may operate on a more hybrid basis with local renewable and reclaimed construction elements forming part of the “soft palette” complimented by elements obtained more remotely that can then be re-circulated within the region. For these more remote regions, transportation impacts will have to be carefully weighed against the advantages of importing re-used construction elements to the region.

Energy consumption of building materials industry as a proportion of total UK industry energy consuption (1996)

Source: BRE

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Footnotes:

16 See www.sust.org and highlight the “Green Directory” or “Ecological Design Gateway” title to obtain an interactive database of indigenous Scottish construction materials and products.

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DfD can minimise waste
by increasing the
number of times an
element can be re-used
Source: N. Verow

Recycling is often not
as energy efficient
as re-using materials
Source: F. Stevenson

Sheeps wool is highly
renewable, re-usable,
and has low energy
costs
Source: F. Stevenson

This natural wool
product is
biodegradable, healthy
and as good as mineral
wool for insulation
Source: F. Stevenson

Dundee Contemporary
Arts Centre. Visible
re-use of existing local
building fabric
preserves historic
understanding and
maintaining a link
with the past
Source: N. Verow

Map showing 4 regions
and sub bio-regions of
Scotland based on rivers
Source: Doug Aberlay

   
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