bnwat06 water use in new and existing buildings
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BNWAT06: Domestic water use in new and existing buildings Supplementary briefing note
Version 1.0
This Briefing Note and referenced information is a public consultation document and will be used to inform Government decisions. The information and analysis forms part of the Evidence Base created by Defra’s Market Transformation Programme.
1 Introduction
This briefing note summarises how water is used in new and existing households and non-
households. This note does not examine in detail product-specific issues. These are
addressed in separate briefing notes that are referred to in this document.
1.1 Purpose of the briefing note
The purpose of this Briefing Note is to:
Define domestic water use, in household and non-household buildings;
Present an overview of the total volume of water put into supply per day in England
and Wales to understand the relative importance of household demand;
Present a framework for estimating domestic consumption in non-households;
Examine/quantify the relative importance of households’ outdoor use (i.e. this does not
include external use in non-households).
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1.2 Content of the briefing note
This briefing note contains the following information:
Section Information
1: Introduction
2: Key facts Water put into supply, definitions of building types
3:Domestic water use
in households
Existing households, new households, external use, impact of behaviour
4: Domestic water
use in non-
households
Existing non-households, new non-households
2 Key facts
2.1 Water put into supply
The following facts and statistics are for England and Wales only (2009/10).
Total water supplied per day: 14,449 Ml/d1
Approximately half of this was supplied to households: 7,599 Ml/d2;
Approximately a quarter of this was supplied to non-households: 2,857 Ml/d;
Just under a quarter (3,280Ml/d) leaked from the distribution system3; and
The remaining small amounts are used operationally, provided unbilled, taken illegally
or supplied to customers requiring untreated water.
Water companies report annually how much water they supply to metered and un-metered
households and non-households. However, it is not possible to determine from this reported
data how much of the water supplied to non-households is for domestic use, as opposed to
commercial or process use. However, the data shows that, in 2009/10, 72 per cent of the
high quality potable water put into supply was for household and non-household demand.
1 Water UK Water Supply and Infrastructure Data http://www.water.org.uk/home/resources-and-
links/waterfacts/waterindustry/data 2 Sum of data in June Returns 2010 http://www.ofwat.gov.uk/regulating/junereturn/jrlatestdata/
3 Ofwat (2010). Service and delivery – performance of the water companies in England and Wales
2009-10. http://www.ofwat.gov.uk/regulating/reporting/rpt_los_2009-10.pdf
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2.2 Building definitions
Table 1 defines the types of buildings and water use considered within the scope of this
Briefing Note.
Table 1.1 Types of water use and building types
Element Definition
Households Properties used as single domestic dwellings (normally occupied), receiving water for domestic purposes which are not factories, offices or commercial premises
4.
This does not include residential non-household properties such as prisons, hospitals, student halls, boarding schools etc.
Metered households
Households who pay for their water services based on their consumption, as measured by a water meter.
Un-metered households
Households who pay for their water services based on a charge related to the rateable value of the property or estimated consumption. The latter includes households that have requested a meter but cannot have one installed for technical reasons.
Non-households Properties receiving water for domestic purposes but which are not occupied as domestic premises, or where domestic dwellings are combined with other properties, or where properties are in multiple occupation but only have one standing charge
4.
Domestic-type use
Water uses such as toilet and urinal flushing, basin taps, kitchen taps (excluding commercial catering facilities), showering, bathing, domestic clothes and dishwashing, basic cleaning. This type of water use occurs in both household and non-household situations. It includes domestic supplies to factories, offices and commercial premises
4.
Domestic outdoor use
Any potable water that is consumed outside of households after being drawn from the mains distribution system. This can include personal garden watering, car washing, window cleaning etc. External use of rainwater or greywater is not included because this does not require any further water to be drawn from the distribution system.
Process use This includes industrial processes, launderettes, commercial car washers, industrial cleaning/cooling etc, large scale landscape watering (golf courses etc).
Ml/d Megalitres per day (1Ml/d = 1,000,000 litres, 1,000m3)
4Ofwat (2007) June return reporting requirements and definitions manual 2011
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3 Domestic water use in households
3.1.1 Existing households
Domestic water use can be broken down into its constituent parts, commonly referred to as
the micro-components of water use. The components of household water use are shown in
Figure 3.1, along with average use quantities. This shows that the greatest use of water in
households is for toilet flushing (around 26 per cent). Water use associated with personal
hygiene including showering and bathing accounts for 19 per cent and 12 per cent
respectively. Water used in washbasins, for clothes and dishwashing and for outdoor use
each account for between 5 and 10 per cent of daily household water use.
Figure 3.1 Average micro-component water use in existing households*
Toilet f lushing, 26%
Bath use, 14%
Show er use, 19%
Hand basin, 9%
Clothes w ashing,
10%
Dish w ashing, 7%
Garden use, 8%
Miscellaneous use,
6%
Car w ashing, 1%
*Water use in an average existing household. Based on water company submissions data5.
Although the data presented in Figure 3.1 are for an average existing household, it is
important to recognise that actual water use can vary considerably. The amount of water
used for each micro-component is determined by three parameters:
Ownership
5Data based on customer surveys, not 2004 MTP documents. Results are very similar to the micro
component data provided by the majority of water companies.
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All homes will have at least one toilet, washbasin and kitchen sink. However, homes may or
may not have a bath, shower, washing machine, dishwasher or outdoor tap.
Frequency of use
How often water consuming appliances, fixtures and fittings are used determines water use.
For example, some people may choose to shower more than once a day.
Volume per use
The volume of water used by a fixture or fitting each time it is used may vary. For example,
modern toilets are required to have a flush volume not exceeding 6 litres per flush. The flush
volumes of older cisterns are typically 7 to 9 litres but can be even greater.
All three of the above parameters are affected by user behaviour. Householders may select
products based on their performance, for example power showers. Such choices will
increase the volume per use.
3.2 New households
The population of England and Wales is forecast to increase from 55,260,000 in 2010, to
63.0 million in 2030, an increase of 9.15 million6. Housing data from the Department for
Communities and Local Government (CLG) shows that the number of households in
England and Wales has increased from 17,025,000 in 1971 to 23,992,500 in 2010. Housing
levels are forecast to continue increasing in response to the increasing population and the
increasing number of low occupancy/single person households. DCLG data suggests that
by 2030 the number of households in England and Wales could reach 29,168,600.
6 http://www.statistics.gov.uk/pdfdir/pproj1009.pdf
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Figure 3.2 Housing and population forecast (England and Wales)
Forecast housing and population growth
20,000,000
21,000,000
22,000,000
23,000,000
24,000,000
25,000,000
26,000,000
27,000,000
28,000,000
29,000,000
30,000,000
2010
2011
2012
2013
2014
2015
2016
2017
2018
2019
2020
2021
2022
2023
2024
2025
2026
2027
2028
2029
2030
50,000,000
52,000,000
54,000,000
56,000,000
58,000,000
60,000,000
62,000,000
64,000,000
Households in England and Wales Population
Improvements in the water efficiency of new homes are being driven by statutory
requirements such as Part G of the Building Regulations, which requires that “the estimated
consumption of wholesome water of a new dwelling should not be more than 125 litres per
head per day (l/h/d)”7, including a fixed allowance of 5 l/h/d for outdoor use. The non-
statutory Code for Sustainable Homes (CSH) has introduced three performance standards
for water efficiency:
Code Level 1 and 2 (120 l/h/d)
Code Level 3 and 4 (105 l/h/d)
Code Level 5 and 6 (80 l/h/d)
Local planning authorities can stipulate the performance standards for new developments
using tools such as the Code for Sustainable Homes to drive improvements in the efficiency
of new homes. The Building Regulations state that water use for a new home should be
estimated using the Water Efficiency Calculator for New Dwellings8. The same calculator is
used to estimate water use of homes complying with the Code for Sustainable Homes. The
calculator is shown in Table 3.1.
7 HM Government (2010). The Building Regulations 2000. Part G: Sanitation, hot water safety and
water efficiency. 2010 Edition. 8 Communities and Local Government (2009) The water efficiency calculator for new dwellings.
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Table 3.1 The water calculator for new dwellings
Installation type Unit of measure Capacity/flo
w rate
(1)
Use Factor
(2)
Fixed use
(l/h/d)
(3)
Water use (l/h/d)
(4) = [(1)x(2)]+(3)
WC (single flush) Flush volume (litres) 4.42 0.00
WC (dual flush) Full flush volume (litres)
1.46 0.00
Part flush volume (litres)
2.96 0.00
WC (multiple fittings)
Average effective flushing volume (litres)
4.42 0.00
Taps (excluding kitchen/utility room taps)
Flow rate (litres/minute)
1.58 1.58
Bath (where shower also present)
Capacity to overflow (litres)
0.11
Shower (where bath also present)
Flow rate (litres/minute)
0.11 0.00
Bath only Capacity to overflow (litres)
0.50 0.00
Shower only Flow rate (litres/minute)
5.60 0.00
Kitchen/utility room sink taps
Flow rate (litres/minute)
0.44 10.36
Washing machine Litres/kg dry load 2.1 0.00
Dishwasher Litres/place setting 3.6 0.00
Waste disposal unit Litres/use If present = 1
If absent = 0 3.08 0.00
Water Softener Litres/person/day 1.00 0.00
(5) Total calculated use (l/h/d)
(6) Contribution from greywater (l/h/d)
(7) Contribution from rainwater (l/h/d)
(8) Normalisation factor 0.91
(9)
Total water consumption (for
comparison with CSH)
= [ (5) – (6) – (7) ] x (8)
(l/h/d)
(10) External water use 5.00
(11)
Total water consumption (for
comparison with Building Regulations
standard)
= [ (9) + (10)
(l/h/d)
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Figure 3.3 shows the estimated micro-component use for a new household built to comply
with the water efficiency standard set out in the Part G of the Building Regulations. This can
be compared to Figure 3.1 that shows average micro-component values from water
company data. The comparison shows that average demand per person in a new build
home is approximately 14 litres less than in existing homes (note, the data supporting Figure
3.1 includes homes built in recent years that also have some element of water efficiency built
in). The reduction in water use is driven by improvements to the efficiency of WCs. This
results in showering becoming the dominant water use within the home (increasing to
around 33 per cent of water use). As WC flush volumes are further reduced and much more
efficient washing machines and dishwashers are installed, personal washing (showering and
bathing) will become increasingly dominant. The interplay between showering and bathing
(ownership and frequency) will influence consumption patterns and the direction that the
market takes in terms of shower type (efficient versus power shower) will be critical.
Figure 3.3 Daily micro-component water use in new households (CSH level 3)*
Toilet f lushing,
14.7%
Bath use, 16.6%
Show er use,
31.0%
Hand basin, 5.5%
Clothes w ashing,
10.4%
Dish w ashing,
2.6%
Garden use, 9.4%
Miscellaneous use,
9.8%
Car w ashing, 0.0%
*as estimated by the water calculator for new dwellings
It is important to recognise that the proportion of domestic water use attributed to each
micro-component by the water efficiency calculator is dependant on the volume of use of
each fixture and fitting. Component trade-offs are possible: for example, more efficient taps
may help to offset the demand of a shower with a greater flow rate. It is also important to
recognise that the use factors presented in Table 4.1 represent an estimate of average water
use. They do not account for the possible ranges of human behaviour.
Improvements to the performance of water consuming fixtures and fittings will contribute to
new homes becoming more water efficient. This will primarily be through reductions in the
volume of use of individual fixtures and fittings. Previous studies have highlighted that user
acceptability is key to successful improvements in water efficiency. For example,
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showerheads with lower flow rates must be perceived by the householder as offering a
similar or improved showering experience.
3.3 External water use (households)
External water use in households refers to any potable water that is consumed outside of the
domestic dwelling after being drawn from the mains distribution system. External use may
be sourced from an internal tap (e.g. the kitchen cold tap) but generally an external tap is
used. External taps are outside of the MTP remit. However, this section highlights the main
issues of external use that are relevant.
External water use depends on season, peak days9, socio-economic group10 and time of
day. The proportion and total volume of domestic water consumption that is used externally
is heavily influenced by these factors. The influence of seasonal and climatic factors upon
external water use means that there is a likelihood of high external water demand occurring
during periods of drought. Reducing the quantity of water consumed externally could help to
reduce the impact of drought and decrease the normal level of domestic water consumption.
Outdoor use activities:
Garden watering. Hoses can use upwards of 540 litres of water per hour depending
on the pressure and hose size. Sprinklers typically use 540 to 1000 litres per hour (9
to 16 litres per minute). Watering cans come in a variety of volumes, typically between
7 and 13 litres11.
Vehicle washing.
Filling and/or topping-up of ponds and water features. Pre-formed ponds vary in
volume, with typical examples ranging from 150 to 4500 litres12.
Pressure washers (for outdoor cleaning). Pressure washers connect to a water
source, such as an external tap, and deliver the water from a nozzle at high pressure.
This high pressure increases the cleaning power of the washer and therefore reduces
the time taken to perform the cleaning task.
Recreational water use (swimming pools, hot tubs, paddling pools).
The British Swimming Pool Federation (BSPF) states that the average volume of an in-
ground pool is around 75,000 litres13. This is a significant quantity of water in the household
setting. Once filled, swimming pools lose water through evaporation, splashing and
9 a day when the maximum temperature equals or exceeds 18°C and the daily rainfall is less than
2mm on the day and the two previous days 10
ACORN classification system 11
B&Q www.diy.com Accessed 12 Jan 2011 12
www.worldofwater.com Accessed 12 Jan 2011 13
BSPF response to Defra’s Consultation on proposed changes to powers to restrict non-essential uses of water
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backwashing of filters. Pools do not need refilling (except when repairs are necessary) but
do require regular topping-up.
The BSPF claims that an average sized covered pool consumes an average of 66 litres of
water per day. This is based upon a 30 litres loss through evaporation and a fortnightly
backwashing of the filter using 500 litres (averaged over the fortnight to about 36 litres per
day).
BSPF states in the same response that an average hot tub has a volume of 1,500 litres and
needs completely refilling every three months. This is an equivalent usage of about 16 litres
per day. These figures reflect averages and hot tub volumes can range from 400 to 2,500
litres14. Manufacturers recommend that hot tub filters should be cleaned every two to four
weeks. This is performed using a garden hose or tap and will add to the water consumption
attributable to hot tubs15.
3.4 Impact of behaviour on water consumption
Behaviour is a major factor affecting how much water people use. Whilst products can be
restricted in terms of the volume of water they use, individual’s behaviour, particularly
frequency and duration of use, is much more variable. As well as frequency of use,
behaviour also includes the choices that people make such as choosing to take a short or a
long shower, or choosing to water the garden with a watering can, hose or sprinkler.
Behaviour is influenced by external factors. For example showering and outdoor water use
increases during periods of hot weather. There is a lot of uncertainty around the behavioural
aspects of water use and about how climate change will affect water using behaviour.
Whilst water using behaviour cannot be controlled, it can be influenced. One of the barriers
to water efficiency in England and Wales is the perception held by many people that, unless
there is a drought, there is no problem. In 2009 Defra commissioned research16 to uncover
the wide range of factors that influence people’s water using habits: their underlying
assumptions, beliefs and aspirations, and water use expectations. The report concluded
that people need to be engaged in order to modify their behaviour. They need to witness
examples and be actively encouraged. Finally, they need to be enabled; they need to know
what they can actually do and how to do it.
An additional factor that can influence behaviour is domestic water metering. In England
and Wales, 37 per cent of households currently are charged on the basis of their metered
consumption17. Charging for water use in this way is widely acknowledged to influence
water use, particularly discretional uses such as garden watering. As a result, the total
14
MTP hot tubs scoping study (unpublished) 15
www.splashspas.co.uk. Accessed 12 Jan 2011 16
Defra (2009). Public Understanding of Sustainable Water Use in the Home
A research report completed for the Department for Environment, Food and Rural Affairs by Synovate. http://randd.defra.gov.uk/Document.aspx?Document=EV0503_8291_FRP.pdf
17 Data from Ofwat website. http://www.ofwat.gov.uk/regulating/reporting/rpt_tar_2010-
11hhwatcust.xls. Accessed 11-01-11
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volume of water used in a metered household is generally around 10 per cent lower than un-
metered household water use18.
18
Defra (2008). Future Water: The Governments Water Strategy for England.
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4 Domestic water use in non-households
4.1 Water use in existing non-households
Less research has been undertaken on domestic-type water use in non domestic buildings,
compared to that completed for households. A literature review completed for the
Department for Communities and Local Government19 found that although there is a
considerable body of information in the public domain concerning water consumption in non-
household buildings, there is very little information specifically on the domestic-type uses of
water. The same study found that there is also a lack of published information on the
frequency of water consuming activities (e.g. number of toilet flushes per person per day) in
non-household building types.
A 2006 CIRIA report, Water key performance indicators and benchmarks for offices and
hotels20, set benchmarks for water use per bedspace (hotels) or employee (offices) per
annum and per day. However, this report did not disaggregate water use into micro-
components.
Unlike in households, it is much more difficult to identify and quantify generic micro-
components of domestic use in non-households. This is because of the wide range of non-
household building types and the ways in which they are used21.
Framework methodology
This section sets out a framework methodology to estimate non-household domestic
demand in England and Wales. This is based on the MTP method proposed in 2007.
Identify building types
The first step is to identify the relevant building types and the types of domestic water use
activity within them. Information on property types is available within the British Standard BS
6465 Sanitary installations. Code of practice for the design of sanitary facilities and scales of
provision of sanitary and associated appliances.
Table 4.1 lists examples of non-household building types used to estimate domestic water
use22.
19
Entec (2009) Research to Assess the Costs and Benefits of Improvements to the Water Efficiency of New Non-household Buildings. Research report completed for the Department of Communities and Local Government, currently unpublished.
20 http://www.ciria.org/service/Web_Site/AM/ContentManagerNet/ContentDisplay.aspx?Section=Web_Site&ContentID=8988
21 Entec (2009) Research to Assess the Costs and Benefits of Improvements to the Water Efficiency of New Non-household Buildings. Research report completed for the Department of Communities and Local Government, currently unpublished.
22 MTP (2006) BNWAT22: Domestic water consumption in domestic and non-domestic properties Version 1.1
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In general, non-household buildings are:
Used for commercial, industrial or institutional purposes;
Often occupied on a transient basis; and
Generally not used for residential purposes (although there are some clear exceptions
to this such as university halls of residence, prisons and nursing homes).
Domestic-type uses are defined in Table 1.1. Water consumption from commercial fittings
(e.g. commercial dishwashers, washing machines, glass washing machines, etc.) is not
included in domestic use calculations. A key difference between domestic water use in
households and non-households is the additional water used for urinal flushing.
Table 4.1 Categories and sub-categories on non-household building types
Category Sub category
Accommodation for elderly, Sheltered accommodation
NHS psychiatric; NHS other; Local Authority children’s home; Local Authority other; housing association sheltered accommodation; other children’s homes.
Residential and nursing homes Nursing homes; other residential care homes; other establishments; medical and care establishments; other establishments.
Staff in offices, shops, factories and other non domestic premises
Manufacturing; electricity, gas and water supply;
wholesale and retail trades, repairs; hotels and restaurants; transport; storage and communications.
Financial intermediation Real estate, renting and business activities; public administration and defence; social security; education; health and social work; other.
Facilities in shops and shopping malls
-
Schools Special schools; primary schools; secondary schools; nursery schools; boarding schools; other schools.
Buildings used for public entertainment
Cinemas; theatres; town halls; libraries; leisure centres (excluding swimming pools).
Hotels Hotels; guest-houses; farmhouses; bed and breakfast accommodation; flats/apartments; self catering; hostels; universities/schools; self-catering holiday camps; catered holiday camps; camping; caravans.
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Restaurants, cafés, canteens and fast food outlets
-
Pubs and licensed bars -
Swimming pools
Estimate population
The next step is to estimate the population (workers, visitors, residents etc) in the non-
households that will be using the facilities. Table 4.2 lists key sources of information for
estimating occupancy in different types of non-households.
Detailed water consumption and water efficiency analyses may also require information on
the number of products installed. For example, the most efficient flush mechanism for a
suite of urinals is dependent on the intensity of use; a waterless or 1.5 litre push button flush
may be more efficient where there are a small number of infrequently used urinals; whereas
a timer-based system may be more efficient to auto-flush urinals which are used more
frequently. BS 6465 sets out the legal (minimum) requirements for sanitary provision (i.e.
the number of WCs, urinals, washbasins) relevant to the number of people expected to
occupy the building.
Table 4.2 Sources of population data by property type
Property type Sub-type Population data source
Accommodation for elderly,
sheltered accommodation.
Residential and nursing homes
All www.statistics.gov.uk Table KS23
Population 'all communal establishment residents'
Staff in offices, shops, factories
and other non domestic
premises.
All www.statistics.gov.uk Table S039
Occupation by industry
Facilities in shops and
shopping malls.
All www.brc.org.uk British Retail Consortium
Schools. All www.education.gov.uk
Buildings used for public
entertainment.
Cinemas
Theatres & libraries
Town halls
Leisure centres
www.esrc.ac.uk
www.statistics.gov.uk
www.statistics.gov.uk and www.prospects.ac.uk
www.prospects.ac.uk
Hotels. All www.tourismtrade.org.uk/marketintelligenceresearch
Restaurants, cafés, canteens
and fast food outlets
All Kearney, J., et al (2001). Eating patterns -temporal
distribution, converging and diverging foods, meals
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eaten inside and outside of the home – implications
for developing FBGD. Public Health and Nutrition:
4(2B) 693-698.
Pubs and licensed bars All www.statistics.gov.uk
Kearney, J., et al (2001). Commercial and Industrial
Floorspace and Rateable Value Statistics 2005
(2005 Revaluation).
Swimming pools All www.nationalwatersafety.org.uk
Estimate ownership and frequency of use
The next step is to estimate ownership and frequency of use in non-households. Table 4.3
sets out a range of assumptions that may be applied by analysts. These are based on
assumptions within the 2007 MTP briefing note BNWAT22: Domestic water consumption in
domestic and non domestic properties. Further work is needed to review and update these
assumptions.
The 2007 MTP briefing note BNWAT22 presented a method where property SIC codes were
applied to SIC code consumption data taken from a report produced in 1999. There has
been no up to date research on water consumption per SIC code since this report and this is
a major gap in information.
The REWARD report23 presented the water consumption for various industrial and
commercial sectors by SIC code. The 2007 MTP note matched the SIC codes from
REWARD and the property types in BS 6465 as closely as possible to produce the following
list of industries for which domestic consumption was estimated using the assumptions in
Table 4.3. The results are presented in Table 4.4.
Food and drink industry (SIC code 15);
Retail industry (SIC code 52);
Hotels (SIC code 55);
Education (SIC code 80);
Health and social work (SIC code 85);
Recreation, culture and sport (SIC code 92);
Public administration and defence (SIC code 75); and
All other (all other SIC codes).
23
Cambridge Econometrics/Environment Agency (2004). REWARD (Regional and Welsh Appraisal of Resource Productivity and Development) Key Industrial Environmental Pressures - Water Use
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Table 4.3 Assumptions on ownership and frequency of use
Property type WC Urinal Basin/bath use Shower Other
Accommodation for the elderly, sheltered
accommodation.
As per household
use.
n/a As per household
use.
As per household use.
Residential and nursing homes.
As per household
use + 2 uses
n/a As per household
use.
As per household use. 4 litres/day drinking.
Staff in offices, shops, factories etc. Male to
female 1:1. 220 working days. Average office
size is 66 persons*
Female = 4 x WC
Male = 1 x WC, 3 x urinal
Timed flush (1.5l x 30mins)
4 x 0.5 litres per person per day
Facilities in shops and shopping malls.
Only shops with an area of over 1,000 m2 are
required to provide toilets. The majority of
facilities are covered by the 2,150 major outlets.
1 visit to WC/urinal
per visit.
1 WC use:6 urinal uses.
Schools. Male to female 1:1
195 schools days (day pupils).
252 school days (boarders).
3 uses per day of facilities. (7 uses for
boarding pupils).
2 WC use:1 urinal uses
Zero bathing for day pupils (no data).
One bathing event per day for boarders (0.25 x
bath: 0.75 shower). Average 42 litres per use.
2 litres/day drinking (day pupil)
4 litres/day (boarder).
Buildings used for public entertainment.
Male to female 1:1
1 visit to WC/urinal per visit.
Libraries: 1 use per 100 visitors
1WC use:6 urinal uses
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Hotels. 2 persons/room. Hotels are all ensuite.
B&Bs, hostels, university accommodation have
shared facilities
4 WC uses per
person per night
n/a One bathing event per night. Washbasin tap
used as per households.
Kitchen tap use in B&B is half of household use.
Self catering. 2 persons As per household
use.
n/a Normal use Normal use No domestic kitchen tap.
Half household washing
machine use.
Restaurants, cafés, canteens and fast food
outlets. Male to female 1:1. 57 meals per
person per year
1 use per visit 1 WC use:6 urinal uses No data on domestic tap use in
cafes. Many premises have
domestic taps behind the bar.
public house/bar 2 uses per visit 1 WC use:6 urinal uses
Swimming pools
Male to female 1:1
1 use per visit 1 WC use:5 urinal uses 8 litre/min. 2 uses per
visit: 30 second pre-swim.
60 second post swim.
* www.communities.gov.uk
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Table 4.4 Measured and estimated domestic consumption in non-household
buildings
Source: MTP (2007) BNWAT22: Domestic water consumption in domestic and non domestic
properties.
4.2 Water use in new non-households
Part G of the Building Regulations does not include a water consumption performance
standard for new non-households . However, improvements in the water efficiency of new
non-household buildings are being driven through assessment against sustainability
measures such as the Building Research Establishment Environmental Assessment
Methodology (BREEAM).
BREEAM is a package of assessment methods and tools designed to help construction
professionals understand and mitigate the environmental impacts of the developments they
design and build. It comprises a set of assessment criteria that include both quantitative and
qualitative assessments and a credit scoring system that is then used to define the buildings
BREEAM standard. BREEAM Buildings can be used to assess the environmental
performance of any type of building (new and existing).
BREEAM has produced construction standards for a wide range of specific commercial and
domestic buildings including:
Courts;
Ecohomes (new homes, apartments/flats, and houses);
Multi residential;
Healthcare buildings;
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Industrial buildings (storage & distribution, light industrial units, factories and
workshops);
Offices;
Retails;
Education;
Prisons; and
Other buildings (including leisure complexes, laboratories, community buildings and
hotels).
Through BREEAM, credits are awarded for water performance as part of the overall
assessment of the building. Local planning authorities and organisations and businesses
can request builders and developers to build new non-household buildings to meet specific
BREEAM performance standards.
A simple fittings based water efficiency standard has been published by AECB24. This
standard can be equally applied to households and non-households, old and new.
Transforming the market towards more water efficient products will reduce demand within
new non-household buildings. Many of the product types that can be installed to address
domestic water use in the home will also be appropriate for use in certain non-household
buildings. For example, basin taps and showerheads that are used in the home are also
appropriate for use in hotels. Conversely, there are water consuming products that are only
suitable for application in non-household situations. These include urinals (which are very
uncommon in households), and types of tap aimed to rigorously prevent water from being
wasted during hand washing (e.g. automatic or percussion taps). The performance
achievable from these fixtures and fittings is discussed in more detail in the product-specific
briefing notes.
Within the non-household setting, users may be willing to accept different levels of
performance from water fittings to what they expect at home. For example, people who use
showers at work are likely to do so as a result of cycling or running to work, or through
activities undertaken during work hours. In these circumstances, showers with lower flow
rates may be more acceptable as the shower is used for personal hygiene rather than for the
showering ‘experience’ that might be expected in the home.
24
http://www.aecb.net/standards_and_guidance.php
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Related MTP information
BNWAT07: Water and energy use
Changes from earlier versions
This briefing note replaces the following previous briefing notes:
BNWAT22: Domestic water consumption in domestic and non domestic
properties
BNWAT28: Water consumption in new and existing homes
BNWAT27: Domestic external water use – an overview
Consultation and further information
Readers are encouraged to review this document and provide suggestions that may
improve the quality of information provided. Email [email protected] quoting the
document reference, or call the MTP enquiry line on +44 (0) 845 600 8951.
For further information on related issues visit http://efficient-products.defra.gov.uk