3. The Site And The Dwelling
When taken together, site, resources, energy and health are inseparable aspects of design consideration with each affecting the other. As a result, each aspect should always be considered in relation to the others. For the sake of convenience, however, it is useful to refer to these headings individually. The following four chapters deal with these four different aspects of dwelling design and cover all types of housing activity. Chapter Seven summarises aspects that are :
Box 3.1 The Principles of sustainable design for dwellings
- HOLISTIC APPROACH — An integrated design approach is preferable to a fragmented one; everything is connected to everything else
- SITE — The specific nature of a place controls sustainable design
- ENERGY USE — Reducing energy use is more cost effective than producing or reclaiming it
- RESOURCE USE — Aiming for durability and re-use is more efficient than recycling products and materials
- HEALTH — A sustainable environment is a healthy one for people
- SIMPLICITY — Simple solutions are better than those which are complicated, over-designed or rely on “technical fixes”
- EFFICIENCY — Good sustainable design produces multiple benefits from one feature
- PARTICIPATION — Sustainable design involves the user at all stages
Figure 3.1 The standard house still allows resources to be used up and thrown away; very little is recycled.
Figure 3.1a “The whole house” acts as a recycling system in carefully re-using all of the elements wherever possible. This helps maximise the efficiency of resource use (after GAIA architects).
3.1 Climate And Orientation
Did you Know?
It rains 3500mm a year on the West Coast of Scotland, and on average only 700mm on the East?
Climate is a key factor in sustainable design and its variation (Figures 3.2 - 3.3) has great influence on the effectiveness of housing in terms of social activity, human comfort, health, physical resource use and energy use. The correct orientation of housing layouts and the plan of the individual dwelling will ensure an optimal response to the climate (see Section 3.1.1 and Box 3.2). Even in existing housing or tight urban locations where orientation is restricted, it is still possible to significantly improve the response of the dwelling to the climate (see Section 3.1.2).
The four key site variables in the Scottish climate for optimising sustainable design are:
- Solar Energy
- Wind
- Precipitation
- Temperature
3.1.1 Solar Energy: maximising passive solar gain
Scotland has ample sunshine to make its use worthwhile in a variety of ways in housing for heating purposes. The heating season in Scotland is longer than in England which makes the use of solar energy more cost effective in Scotland than in England in terms of reducing heating bills1. Even on cloudy days approximately 30% of solar radiation can be usefully harnessed for lighting and energy use.
The following benefits can be obtained from using solar energy:
the building form itself can capture solar energy for heating and save around 10-15% on annual heating costs
mechanical systems which capture solar energy for the heating of hot water can save up to 50% on annual hot water costs (see Table 4.3)
both passive and active modes of solar heating can be retrofitted to old stock
active solar water heating using solar water panels has an average financial payback of 10 years, well within the life of the panel itself (see Table 4.3)
retro-fitted sunspaces (Figures 3.4 - 3.10) can save energy and offer an additional low cost amenity space for three seasons of the year.
Did you Know?
In one monitored retrofitted solar scheme in Scotland heating bills were reduced from £15-£23 a week to an average of £3-£6 a week
Passive solar gain is the use of solar energy for heating by using the dwelling layout and form to capture and store the sun’s heat for use both in the day and evening2. Ideally, housing should lie roughly on an east/west axis with habitable rooms to the south (Figure 3.4). This layout is not always possible due to planning constraints, but should be adopted wherever practical.
Figure 3.4A This chart demonstrates the relative amount of energy used each year by different house types. Source: GLC (Greater London Council)
The main method of capturing and storing solar energy is through large south facing windows situated in a highly insulated dwelling but an additional means is through using sunspaces. These are highly glazed south facing amenity areas or porches which are either added or incorporated in to the dwelling layout to enhance passive solar gain and reduce heat loss. There are four ways in which sunspaces save energy:
- Thermal Buffering
- Pre-heated Ventilation
- Draught lobby
- Evening heating
Figure 3.5 Thermal Buffering: by acting as an intermediate heating zone, sunspaces provide an additional insulation layer to walls and windows. (After Borer and Harris, 1998).
Figure 3.6 Pre-heated Ventilation: fresh air can be pre-warmed by sunspaces before it enters the house via windows, doors and ventilators. (After Borer and Harris, 1998).
Figure 3.7 Draught lobby: by acting as an air-lock when external doors are opened, sunspaces used as porches reduce ventilation heat loss. (After Borer and Harris, 1998).
Figure 3.8 Evening heat: by storing and re-radiating heat stored in solid walling solar sunspaces can continue to provide warmth in the evenings once outside temperatures have cooled. (After Borer and Harris, 1998).
Energy gathered during the day will be lost in the evening, if sunspaces are not effectively insulated from the outside. It is a matter of training the occupier to ensure that any shutters or insulated blinds in sunspaces are closed at night to prevent heat loss. Airways through doors, windows or ventilators between the sunspace and living area should also be closed off once it is apparent that the sunspace is cooler than the living area.
Did you Know?
Passive solar energy can provide up to 25% of the heating requirements for an ordinary family house.
Passive solar gain methods must also be established in tandem with daylighting design in order to ensure optimum performance (see Section 4.2.2). There are a number of methods and tools available to help carry out these calculations. One of the best known is BREDEM3. Method 50004 is a simpler version. There are also numerous “shareware” solar gain tools on the internet5.
Careful siting of deciduous trees can stop overheating of south facing rooms and conservatories in the summer with full leaf shade, while allowing more light to penetrate in the winter due to less foliage. Care must be taken not to over shade with trees as even in winter deciduous trees can take away up to 50% of daylight when densely planted (Figure 3.11).
Figure 3.10 James Nisbet Street after retrofit to introduce sun spaces to the block using existing balcony structure.
Figure 3.11 Siting of trees relative to the house is critical to ensure that sun can still penetrate into the building. If trees are too close overshadowing will occur (After Borer and Harris, 1998).
Box 3.2 Passive solar gain: pointers for good practice
Site layout should provide access to sunshine for as many dwellings as possible and avoid overshading (See figure 3.12)
housing layouts should be orientated within 30 degrees of due south wherever possible in order for the solar gain to be useful
plan cooler service spaces on the north side and habitable rooms needing warmth on the south side
make sure the building is well insulated and relatively airtight
allow for adequate and controllable ventilation to avoid overheating in summer
incorporate draught lobbies to minimise heat loss
glazing should be optimised with a 70:30 ratio of glazing from south to north elevations to maximise passive solar gain
provide thermal mass where possible to absorb solar gain (up to 100mm blockwork is effective) and avoid overheating
the use of conservatories or sunspaces purely for energy reasons is not effective unless they are a cheap, unheated, preferably single glazed (which uses considerably less material resources than double glazing and doesn’t rely on vulnerable sealants), three season amenity space
narrow width sunspaces (under 1500 mm wide) are preferable to room sized ones or conservatories to prevent them from being treated as an additional room and being heated
provide full separation and insulation between sunspaces and the main dwelling
provide structural overhangs, external shutters and internal blinds to prevent both overheating in summer and heat loss at night
cover as much of the south facing wall as practical with a sunspace to act as a thermal buffer
use deciduous trees and planting to provide partial shade to sunspaces in the summer
Figure 3.12 Plan of solar layout showing shadows cast by housing which define space to be left between houses.
Figure 3.13 The house which presents the narrow end to prevailing winds also maximises the opportunity for passive solar gain (After Borer and Harris, 1998).
3.1.2 Wind: Design With Form, Layout And Land Cover
Did you Know?
A careful assessment of the local climatic conditions combined with design strategies that optimise the microclimate can reduce energy costs by 5%.
Even if an urban development site does not offer much opportunity for passive solar gain, all housing can benefit from design for shelter as wind chill contributes significantly to energy loss. Generally, the best orientation for solar gain is also the best for preventing heat loss due to prevailing wind chill from the southwest and north east (Figure 3.13). Regional wind data can be obtained from the Meterological Office6 but site measurements and analysis will give a more accurate picture for design purposes7.
Figure 3.14 A detached house is the least energy efficient form in that heat loss can occur from all sides. For the same floor area a property within a tenement block is protected on at least one side and often top and bottom by surrounding properties minimising heat loss through the fabric of the building.
Figure 3.15 Vegetation, as third skin, on a building can offer protection from the elements and reduce pollution.
Housing form can reduce the effect of windchill and heat loss. The ideal form for housing will minimise surface area for heat loss but retain surface variation and texture to increase wind drag. One of the most energy efficient forms of housing is the tenement block. Terraced two storey housing is also very effective. The least effective are the semi-detached and detached house (Figure 3.14 and Figure 3.4A). Providing external structures such as porches, trellising and fencing can all help to reduce wind speeds without increasing heat loss from the building. Vegetation, carefully planned, can act as a “third skin” on appropriate walls of buildings by providing wind drag and an additional thermal buffer. In effect it becomes “free” and renewable insulation material with minimal manufacturing costs8 (Figure 3.15).
Figure 3.16 Layout of traditional Scottish village to shelter from harsh elements and take full advantage of sun.
Housing layouts should be self-sheltering wherever possible. The traditional Scottish village (Figure 3.16) provides a good rural example of this with the tight layout of buildings creating a milder micro-climate and helping to shelter the inner faces and entrances of the buildings. The traditional Victorian tenement block provides an urban example of the same principle.
The use of trees combined with planting and fencing in garden areas also provides some degree of wind shelter through landcover. The most effective height for trees is the height of the dwelling and placed 1-3 heights away, or 3-4 heights where solar access is required9(Figure 3.17). Larger shelterbelts of trees can provide the same effect over a whole housing development. There may be a conflict with the need for visibility and observation when providing planting. This can be overcome by planning lines of vision along public routes from the housing.
Figure 3.17 Shelter belts of trees should be planted at a distance of 1 to 3 x house height from the building to maximise wind drag. In addition fences in front of the building can assist this further (After Borer and Harris 1998).
Box 3.3 Reducing wind chill and heat loss: pointers for good practice
Figure 3.18 Site layout to improve local climate showing optimum positioning for shelterbelt in relation to housing.
avoid exposed, windy sites and take advantage of any shelter offered by a site
visit site to establish local wind conditions and design for these
orientate housing to minimise wind chill by presenting narrow ends to the prevailing wind
minimise surface to volume area of buildings by maximising use of terrace or tenement layouts and using compact forms
use shared party walls to reduce heat loss through the building envelope
increase shelter and wind drag through use of planting and external structures
design housing to be self-sheltering
avoid housing layouts and forms that accelerate the wind
use evergreen planting to increase effectiveness of shelterbelts in winter but avoid overshading
Figure 3.18A. A correctly curved shelter belt will help to deflect wind, depending on tree type, density, height, etc.
3.1.3 Precipitation: Design For The Effects Of Climate Change
Housing developments should be “future proofed” against increased precipitation and storm frequency10 with suitably robust layout and detailing. Consultants should be asked if they have taken the predicted effects of global climate change, such as increased storms and precipitation, into account11(see Box 3.4).
Box 3.4 Taking account of global climate change: pointers for good practice
check existing water table and natural patterns of drainage
calculate rainwater guttering and pipework on the basis of up to 30% increase in precipitation
use soft landscaping to reduce storm water runoff and help the rain to percolate naturally back into the water table12 (Figure 3.19)
use porous paving schemes to allow water to flow down through hard landscaping directly into the water table to minimise drainage requirements and relieve pressure on existing drainage (Figure 3.20)
retain robust roofing details including sarking in preference to battens
ensure all details take account of increased intensity and number of storms
preserve and increase planting of trees to absorb CO2 to help reduce global climate change
3.1.4 Temperature: Using Landcover To Modify Extremes
Large urban areas in Scotland create particular local climates which trap pollution, have less solar radiation, and are generally warmer than the surrounding countryside by several degrees. Planting modifies heat difference by trapping solar heat and providing cool air through transpiration. Hard landscaping in the immediate vicinity of the dwelling can also capture solar heat during the day and re-radiate it in the evening which helps to even out daily temperature swings (see Case Study No.5).
Figure 3.20 The use of porous paving and blocks can help rainwater drain away naturally saving significantly on underground pipework.
To replenish the oxygen we use up, each human needs 30 m2 of planting, either in housing schemes or elsewhere. Trees are effectively the “lungs” of the Earth. They not only clean air by removing 75% of dust particles, they oxygenate it, and remove carbon dioxide as well as sulphur monoxide13. Meanwhile their roots break down the soil, take up nutrients and provide the soil with nutrients in return through dead leaf mould. Scotland’s major cities have some of the highest concentrations of air pollutants in Europe, principally arising from traffic. In inner city areas the use of trees and other planting can act as a pollution filter between housing and busy, congested roads.
Trees are also of high amenity value and can form a focus for community involvement by combining community woodland development with housing14. Many of our housing estates have few trees because landscaping is traditionally the first cost saving to be made. This is shortsighted given the environmental benefits that trees and planting in generally can generate.
Box 3.5 Soft and hard landscaping : pointers for good practice
require contractors to preserve biodiversity
minimise hard landscaping and encourage the use of deciduous trees to enhance microclimate
preserve existing mature trees and wildflower areas as much as possible
increase planting generally to increase opportunities for local wildlife to proliferate
set aside wild areas using native plants and trees with minimal cultivation to encourage local biodiversity
provide corridors of linked planting to allow cross-pollination and provide routes for wildlife
establish which parts of the site are optimum for growing vegetation and allow re-development to take place on the least ecologically promising part of the site
replace soil sterilised by additional housing with soil and plant cover on the roofs of the housing (Figure 3.21) where suitable
use planting as pollution filters and sound barriers between busy, congested roads and housing developments
use hard landscaping on south side of building as thermal mass to modify climate
3.2 Site Contamination
Figure 3.21 Soil and plant cover on roofs replace planting sterilized on the ground by new buildings.
The increasing use of brownfield sites often means dealing with contaminated sites. Consultants should establish an accurate site history using local records and carry out a contamination survey where necessary.
Site de-contamination can be carried out in a number of ways:
- scrape clean and removal of toxic soil
- capping the contaminated soil
- chemical de-contamination
- biological de-contamination
The most benign method involving least energy is biological de-contamination using toxin-neutralising plants such as willow saplings and reeds(Figures 3.22 - 3.23).
Figure 3.22 - 2.23 Planting of willows and reeds can naturally assist with de-contamination of site.
This takes time, however, and requires careful pre-planning. Intensive treatment for on site de-contamination using enhanced chemical compositions can be quicker but uses a more energy intensive product. Capping the contamination does not get rid of the problem but may be a cost effective solution if contamination is not severe. Scraping the site clean is a last resort but may be required if contamination is particularly severe. Consultants should balance the cost of de-contamination process against the environmental impact of the de-contamination process itself.15
3.3 A Sense Of Place
The final ingredient when designing sustainably for a given site is to understand the existing nature of the locality. Physical, historical, cultural and archeological features all inform a sense of place and should also be taken into consideration when applying a holistic approach to site development. Sustainable design is as much about sustaining our history as it is about sustaining our environment.
Site Checklist-Key Areas
- Climate
- Land cover
- protect and enhance existing vegetation (see Box 3.5)
- make provision for contaminated site remediation
- Sense of place
- note historical, cultural or archeological features on the site
- identify physical influences on local building style
Footnotes
^ 1. Bartholomew, DML. (1984)
^ 2. There are a number of publications on passive solar which give guidance on passive solar design in housing : BRECSU has published several free reports BRECSU (1997), BRECSU GPG79, BRECSU (1994b). More technical detail is offered by Energy Research Group (1994), Lowe, R, et al (1996). A good introductory and highly illustrated book is Energy Research Group (1996).
^ 3. BREDEM (Building Research Establishment Domestic Energy Model) is available from BRE and is designed to calculate heating demands on the basis of gains and losses, using computer software. BRE (1995)
^ 4. Method 5000 is a manual tool and is found in Energy Research Group (1994)
^ 5. e.g. http://ourworld.compuserve.com/homepages/dacPc/solacalc.htm
^ 6. HMSO, The Climate of Scotland: some facts and figures, Edinburgh
^ 7. BRE (1990a )
^ 8. Johnston and Newton (1993)
^ 9. BRECSU (1995b) p7
^ 10. Climatic Research Unit (1998)
^ 11. BRE Scottish Laboratory (1998)
^ 12. SEPA (1998)
^ 13. Giradet (1992)
^ 14. The CD-ROM Quality Green Space for Residential Areas produced by Scottish Homes, COSLA, Scottish House Builders Association and Scottish Natural Heritage (1999) provides practical guidance and best practice on community greenspace by working with local communities. The CD-ROM is freely available from SNH with supporting documentation.
^ 15. For comparison of treatments for contaminated land see CIRIA (1995 onwards) also CIRIA (1991)