COPSE: Coincident probabilistic
climate change weather data
for a sustainable built environment
Deriving and using future weather data
for building design from UK climate change
projections – an overview of the
COPSE Project
COPSE: Coincident probabilistic
climate change weather data
for a sustainable built environment
COPSE Project:
Manchester University
Prof Geoff Levermore, Dr Richard Watkins (now at the University of Kent), Dr Henry Cheung,
Dr John Parkinson, Prof Patrick Laycock, Prof Roger Courtney;
University of Bath
Dr Sukumar Natarajan, Prof Marialena Nikolopoulou (now at the University of Kent),
Dr Charles McGilligan;
Napier University
Prof Tariq Muneer, Dr Yieng Wei Tham;
Northumbria University
Prof Chris Underwood, Dr Jerry Edge, Dr Hu Du;
Sheffield University
Prof Steve Sharples (now at the University of Liverpool), Prof Jian Kang, Dr Michael Barclay;
Met Office
Dr Michael Sanderson.
July 2012
This report should be referenced as:
Levermore, G.J., Courtney, R., Watkins, R., Cheung, H., Parkinson, J.B., Laycock, P., Natarajan,
S., Nikolopoulou, M., McGilligan, C., Muneer, T., Tham, Y., Underwood, C.P., Edge, J.S., Du, H.,
Sharples, S., Kang, J., Barclay, M. and Sanderson, M. 2012. Deriving and using future weather
data for building design from UK climate change projections – an overview of the COPSE
Project. Manchester University, UK.
COPSE: Coincident probabilistic
climate change weather data
for a sustainable built environment
Contents
Foreword
2
Executive summary
3
1 Introduction
7
2 Projecting future weather
9
3 Building performance in future climates
20
4 Thermal comfort standards and implications for energy use for cooling
32
5 Urban heat islands and canyons
36
6 Implications of climate change for energy consumption
in the national building stock
40
7 Concluding observations
43
Outputs from COPSE
44
Datasets and other outputs
Matlab scripts forming the weather data generators developed at Northumbria University
are available for Matlab users. Contact Professor Chris Underwood: chris.underwood@
northumbria.ac.uk.
Test Reference Years and other building design weather data for future climates derived
from UKCP09 data may be provided by the University of Manchester. Contact: Professor
Geoff Levermore: geoff.levermore@manchester.ac.uk.
Foreword
Climate change has increasing implications for the economic and social life of the UK, as
the reports of the UKCIP1 and the UK Climate Change Risk Assessment 20122 make clear.
In particular, it will impact on the performance of our built environment – our buildings
and the civil infrastructure that supports our urban communities and our communications
networks. Recognising this, the Engineering and Physical Sciences Research Council
has funded successive programmes of research aimed at improving understanding of
the impact of climate change on the built environment and into means of improving its
adaptability and resilience. A recent phase of this research brought together a number of
research projects, including COPSE, under the umbrella of the Adaptation and Resilience to
Climate Change (ARCC) Co-ordination Network (CN)3.
The ARCC CN has sought to develop close links between those directly involved in the
research, who are principally in universities, and prospective users of the outputs, such as
policy-makers, architects and engineering consultants. To that end, it has held conferences
and technical events, published summaries of the research programmes and issued regular
newsletters, with the aim of promoting the outputs of the research and facilitating their
application. This publication further contributes to that overall aim.
Academic research is, rightly, first published in peer-reviewed journals where it can
be subject to the scrutiny of other researchers, and the findings compared with those
of similar studies. Journal publications are often, though, not easily accessible for
practitioners who will be principally concerned with the findings and their implications
rather than the methods through which they were obtained. By contrast, short
non-technical summaries do not provide a suitable basis for application of the findings.
This publication seeks to fill that gap, in that it offers an overview of the COPSE project
which, while summarising the research undertaken, gives most attention to the outputs
and their relevance for practitioners. By also providing full details of the publications from
COPSE research, it facilitates further investigation by those who wish to take advantage of
latest research findings.
I hope that this booklet will be both useful and relevant to all those engaged in ensuring
that our buildings meet their occupants’ comfort requirements without excessive energy
use, both now and in the future.
Roger Street
Technical Director for Adaptation Science, UKCIP
arcc cn
ARCC CN – Enhancing resilience across the urban environment
The Adaptation and Resilience to a Changing Climate Coordination Network brings
together a range of research projects funded by the Engineering and Physical Sciences
Research Council. These look at the impacts of climate change and possible adaptation
options in the built environment and its infrastructure including water resources, transport
systems, telecommunications, energy and waste.
1 www.ukcip.org.uk
2 www.defra.gov.uk/publications/2012/01/26/pb13698-climatechange-riskassessment/
3 www.arcc-cn.org.uk
COPSE: Coincident probabilistic
climate change weather data
for a sustainable built environment
Executive summary
The COPSE (COincident Probabilistic climate change weather data for a Sustainable
built Environment) research project was undertaken between 2008 and 2011. Led
by Manchester University, with eventually six academic research partners and the
Meteorological Office contributing to the overall programme, the core aim of the project,
addressed by the Manchester research team, was to develop robust methodologies for
producing weather data files for assessing building designs in future climates, considering
the period up to 2080, with particular reference to comfort and energy use. But the scope
of the project was much wider; topics studied (and the universities involved) included:
• a critical analysis of future projections of solar radiation and its characteristics (Napier)
• the impact of future climates on the internal temperatures experienced in typical
buildings, particularly examining the proportion of time for which these would exceed
conventional comfort temperatures and the additional energy required for mechanical
cooling systems (Northumbria);
• the interaction between internal temperatures and the external noise environment,
now and in the future, since the noise environment influences the ability of building
occupants to achieve comfort conditions by opening windows and increasing
ventilation rates (Sheffield/Liverpool);
• the implications for future energy use of the adoption of ‘adaptive comfort’ criteria
in the design of buildings, since this approach would reduce demand for mechanical
cooling (Bath/Kent);
• the Urban Heat Island in the Greater Manchester conurbation, with new modelling tools
being developed (Manchester);
• the potential change in national demand for energy for space heating and cooling in
the building stock (Bath).
Chapter 1 provides an introduction to the project, outlining its background and some
principal findings.
Chapter 2 describes the research related to the production of future weather files for use
in modelling building performance. Conventionally, two sets of weather data are used in
building design. The first is a Test Reference Year (TRY); this consists of hourly values of key
weather variables (dry-bulb temperature, solar irradiance and relative humidity) which,
as judged by a defined statistical process, best represent average conditions for the year.
This set is used for assessing annual energy use. The second is a Design Summer Year,
produced by a different process, which presents hourly data for the same variables that are
representative of more extreme summer conditions. These data are used when modelling
the performance of the building during periods of hot weather to assess the likelihood of
over-heating.
The Weather Generator associated with the UKCP09 Climate Projections produces 3000
years of synthetic hourly data for any UK location and future time period up to 2080, under
three different climate change scenarios: Low, Medium and High emissions. However,
some variables that are important for building design (e.g. wind speed) are not included.
These were deduced from the other data and from the augmented data set 21 TRYs were
produced for each of three locations: London, Manchester and Edinburgh. These TRYs
related to seven future dates (2020 to 2080) and three emissions scenarios. One finding
was that while average winter temperatures are projected to increase, average summer
temperatures will increase faster.
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COPSE: Coincident probabilistic
climate change weather data
for a sustainable built environment
The standard process for deriving the Design Summer Year is known to produce anomalous
results for some locations. Hence an improved method for deriving data sets representative
of more extreme conditions was developed, the resulting data files being termed the
Design Reference Year (DRY). The internal environmental conditions in a building are
determined not by a single weather variable but by the combination of the three key
weather variables (hence the reference to ‘coincident’ in the title of COPSE). For an
individual building, the relative importance of each varies with the building characteristics,
its orientation and across seasons. Thus, for example, a building with extensive west-facing
glazing may be less likely to overheat during summer months than during spring and
autumn, because of the higher solar angle during the summer. A key feature of the new
method for providing data representative of more extreme conditions is that DRYs may be
derived using different weightings of the weather variables, thus enabling designers to test
the building performance with a DRY that is suited to the characteristics of the individual
building.
As with TRYs, a DRY may be produced from the synthetic weather data for any location,
future time period and emissions scenario. In addition, designers have the option of
specifying the probability associated with the DRY; thus modelling performance using a
DRY that is representative of conditions that on average occur only once in 100 years is a
more demanding assessment than if the DRY represents conditions that occur on average
every 20 years.
The derivation of future TRYs and DRYs fulfilled the aim of providing robust methodologies
for deriving future weather data files for building design which reflected both the
probabilistic nature of weather data and the need to test designs with data representative
of more extreme combinations of the key weather variables.
As part of the process of preparing the synthetic weather data from which the TRYs and
DRYs were derived, the solar variables produced by the UKCP09 Weather Generator were
subject to close analysis. This showed that both the hours of sunshine and the proportion
of direct to diffuse radiation were projected to increase in the future, although the
physical basis for these changes was not evident. Subsequent interactions with the team
responsible for the Weather Generator resulted in a revised generator being published in
2011.
Chapter 3 covers the work undertaken, using the future weather data files, to explore
how buildings would perform in future climates. Four contrasting buildings – an office
building, a primary school, a hospital and a residential care home – were modelled in
different locations, using not only the future weather files from COPSE research but also
those available from other sources (although the conclusions from each were broadly
similar). These studies showed a steady rise in the proportion of time for which the internal
temperatures exceeded the conventional upper limit for comfort of 28°C; for the office
building in Manchester, for example, this rose by 2050 to more than 15% of occupied
hours. The rate of increase varied – thus for example the hospital showed a relatively slow
increase because of the high proportion of deep-plan spaces which are not as influenced
by future increases in solar radiation. Clearly, though, the need to minimise over-heating
will become an increasing factor in design, and the ability of an existing building to
maintain acceptable internal temperatures will be a factor in decisions on whether to
demolish or refurbish.
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COPSE: Coincident probabilistic
climate change weather data
for a sustainable built environment
The modelling studies also produced estimates of the cooling capacity and associated
energy consumption required in these buildings. Again, a steady increase was observed,
with a doubling of cooling energy consumption by 2050 under some emission scenarios.
Because of its warmer climate, demand in London is significantly higher than in the
other cities. However, the increase in cooling energy use has to be set against a projected
decline in energy use for heating in winter. This was also estimated through the modelling
studies, with the conclusion that the reduction in winter energy demand would exceed
the increase in the summer. Because future winters would continue to have periods of low
temperatures, though, there would be little impact on the capacity required in heating
plant.
A separate study examined the relationship between the external noise environment
and the ability of occupants to increase ventilation rates through opening windows. As
ambient temperatures rise, occupants have greater need to open windows, but this may
mean that they are exposed to external noise for an unacceptable length of time. By
combining ‘noise mapping’, through which the external noise level on different parts of a
building could be calculated, and thermal modelling, the impact of rising temperatures
on comfort and cooling energy requirements could be studied. This research showed that,
unless noise levels could be reduced, cooling energy requirements would rise significantly.
Hence avoiding the need to install mechanical cooling in buildings that currently rely
on natural ventilation may require a combination of measures, not only to improve the
thermal performance of the building but also to reduce external noise levels.
The studies outlined above were based on the conventional design approach of taking
28°C to be the upper limit of the comfort band for most building occupants. However,
previous research has shown that people adapt to warmer periods, for example by
changing their clothing, and can be comfortable at higher temperatures. This observation
underpins the theory of Adaptive Comfort, which predicts the upper comfort temperature
from of the external temperatures experienced in the immediately preceding few days.
Chapter 4 summarises research carried out to determine the extent to which adoption of
that approach to comfort could reduce the need for mechanical cooling of buildings and
the associated energy use. The research demonstrated that the maximum cooling energy
saving in a building over the summer could be related to a novel metric, the number of
Adaptive Comfort Degree Days, and this in turn could be derived simply from the weather
data for the location of the building.
Further, there are two methodologies for predicting the maximum comfort temperature
using Adaptive Comfort principles, one set out in a European standard and the other in
a US standard. The research modelled the performance of a building in future climates
and showed that if the comfort temperature were calculated using the US standard, the
building would require mechanical cooling much earlier than if the European standard
were used. Hence the latter maximised the potential energy savings.
Temperatures in urban areas are generally higher than those in surrounding rural areas,
the effect being known as the Urban Heat Island (UHI). The UHI, which can be up to 8°C
in Manchester, needs to be taken into account when assessing a building’s propensity to
over-heat. Studies of the UHI in Manchester, outlined in Chapter 5, particularly focussed on
the way that ‘street canyons’ influence the temperature, by reducing the rate at which heat
may be lost through radiated to the atmosphere. This research resulted in a new model for
estimating the UHI at an urban location which takes into account the ‘Sky View Factor’, i.e.
the proportion of the sky that can be seen from street level.
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COPSE: Coincident probabilistic
climate change weather data
for a sustainable built environment
Complementing the studies of future energy consumption in individuals buildings,
described in Chapter 3, a top-down assessment of the impact of climate change on energy
use in the national building stock was undertaken and is summarised in
Chapter 6. The study was based on data on gas consumption published by the National
Grid. The relationship between gas consumption and the average daily temperature was
determined for 13 regions. The effect of warmer winters could then be explored, using the
future weather data files. The research showed that, depending on the emissions scenario
chosen, energy use for space heating (currently, about one sixth of national energy use)
would fall by 16–18% by the 2030s and by around twice that proportion by the 2080s. Thus
climate change will itself bring about a significant reduction in national energy demand
(and there will be additional reductions because of changes in the stock, with newer
buildings being thermally more efficient than those in the present stock).
The findings from this broad range of research illuminate different aspects of future
building performance, while the weather data files will be available to support future
research and design studies. The report includes full details of the publications resulting
from COPSE, and contacts through whom the future weather data files may be accessed.
The current revision of a key document for the design of building services, Guide A of the
Chartered Institution of Building Services Engineers, is drawing on COPSE outputs. Further
studies will build upon the work reported here.
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COPSE: Coincident probabilistic
climate change weather data
for a sustainable built environment
1 Introduction
This report summarises the research undertaken and the findings of the COPSE (Coincident
Probabilistic climate change weather data for a Sustainable built Environment) project,
funded by the Engineering and Physical Sciences Research Council between 2008 and
2011. The project was led by Manchester University, the other academic research partners
being Bath University (and after a staff move, the University of Kent), Napier University,
Northumbria University and Sheffield University (with, following another staff move,
Liverpool University). The Meteorological Office was also research partner. The research
was informed by a Stakeholder Group on which were representatives of key potential users
of COPSE findings – building owners, architects, engineering consultants, suppliers of
design software etc. This Group met on five occasions during the course of the project.
COPSE developed and applied tools for examining the performance of buildings in
climates which the UK may experience in the course of this century. Buildings have long
operational lives; most are expected to be in use for 50–100 years and some for even
longer. In previous eras, designers could assume an unchanging climate, and buildings
which provided acceptable internal conditions when first occupied could reasonably be
expected to do so until the end of their useful lives. This assumption is no longer valid;
the global climate is changing, as evidenced by the reports of the International Panel on
Climate Change4. Hence designers need to be able to model the performance of buildings
under future climatic conditions in order to give prospective investors and occupiers
assurance that they will continue to provide acceptable conditions, perhaps with some
modifications during their service life. Reflecting the general trend towards a warmer
climate, a particular need is to be able to assess a building’s propensity to over-heat during
a prolonged period of hot weather.
The core aim of the COPSE project was to develop robust methodologies for producing
weather data files for assessing building designs in future climates, with particular
reference to comfort and energy use. These data files were based on the probabilistic
outputs of the Weather Generator associated with the UKCP09 Climate Projections5,
published in 2009. At the same time, however, the opportunity was taken to improve upon
standard procedures for producing weather data for assessing over-heating, in particularly
by enabling designers to select data by reference to a combination of key variables:
external temperature, solar irradiance and relative humidity. This new methodology
therefore incorporated the characteristics of coincidence and probability that featured in
the project’s title.
However, the research undertaken within the COPSE project covered a much larger range
of topics. In addition to taking lead responsibility for the development of the new weather
data files, Manchester University recorded hourly temperatures at 59 locations throughout
Greater Manchester in order to characterise the Urban Heat Island in the conurbation. From
these data, new models were developed to assist designers to estimate more accurately
the actual external temperature to which buildings in urban areas will be exposed, thus
improving the prediction of internal temperatures in those buildings.
4 Intergovernmental Panel on Climate Change (IPCC) Fourth Assessment Report of the IPCC. (2007)
Cambridge: Cambridge University Press. Available at www.ipcc.ch
5 Available at http://ukclimateprojections.defra.gov.uk
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COPSE: Coincident probabilistic
climate change weather data
for a sustainable built environment
Napier University undertook a critical analysis of future projections of solar weather data,
notably projections of hours of sunshine and the relationship between direct and diffuse
radiation, as part of the process of developing new weather data files. This analysis showed
up anomalies in the output from the original UKCP09 Weather Generator and led to the
publication of an amended generator.
The impact of future weather patterns on both the thermal performance and the energy
consumption of typical buildings was studied by Northumbria University. Using future
weather files developed by COPSE and other projects, this research showed the extent
to which internal temperatures would exceed the conventional comfort criterion of
28°C, under different climate scenarios. It also enabled the cooling energy required to
maintain comfort conditions to be estimated. Winter performance was also studied,
with the conclusion that the reduction in space-heating energy demand consequent on
warmer winters would more than compensate for the increase in summer cooling energy
requirement. However, there would be little impact on the plant capacity required.
Complementing this work on individual buildings, the University of Bath examined
the impact of possible future climates on energy consumption for space heating in the
national building stock, drawing on gas consumption data published by National Grid. This
showed that energy use was likely to decline by around 17% by the 2030s, with further
reductions in later decades.
The team at Bath also explored the way in which adopting ‘adaptive comfort’ principles
in building design could affect assessments of over-heating. This term relates to the
ability of people to adapt to warmer external conditions, which means that they can feel
comfortable when the internal temperature in a building is higher than the conventional
upper limit for comfort. As a consequence, there is reduced need for mechanical cooling
and with its associated energy demand. Bath developed a novel metric, the Adaptive
Comfort Degree Day (ACDD), for exploring this effect.
Finally, Sheffield University examined the relationship between internal temperatures
in naturally ventilated buildings (i.e. those which rely on opening windows to produce
comfortable internal temperatures in warm conditions) and the external noise
environment, under present and future climates. Clearly, the ability of occupants to open
windows is influenced by the external noise level and as external temperatures increase,
it becomes more likely that the building will need to be equipped with some form of
mechanical cooling. The level of external noise could be a factor in determining whether
an existing building can continue to be used.
Hence the COPSE research programme illuminated a number of aspects of the impact
of climate change on buildings in the UK and provided tools relevant to the assessment
of both existing and future buildings. The following chapters present in more detail the
research undertaken and the findings, and draw out the implications for building design
and performance assessment. A full list of COPSE published outputs is also provided.
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COPSE: Coincident probabilistic
climate change weather data
for a sustainable built environment
2 Projecting future weather
2a Test Reference Years and Design Reference Years
Building designers model the thermal performance of proposed designs: first to
estimate annual energy consumption and secondly to provide information on internal
environmental conditions (temperature, air change rates etc) during periods of hot
weather. The latter process leads either to an assessment of the adequacy of natural
ventilation for maintaining acceptable internal conditions or to an estimate of the cooling
capacity that will need to be provided by mechanical plant to maintain environmental
conditions appropriate for the activities within the building.
For these assessments, designers turn increasingly to computer-based modelling
techniques, although manual methods may also be used. Whichever approach is used,
there is a need for sets of weather data for the proposed location which suitably represent
the conditions to be assessed. In the case of annual energy estimates, the data will be
representative of an average or typical year. For assessments of performance in hot
weather, data representative of more extreme conditions will be used.
These data are derived from weather observations stretching back over a period of 20–30
years. There are different methods for converting observational data to weather files for
building design but those most widely used in the UK are set out in ISO and European
Standards6 and the resulting data appear in CIBSE Guide A7. The final data for annual
assessment of performance are assembled into a Test Reference Year (TRY) while the data
for summer-time assessment are presented as a Design Summer Year (DSY). Each takes the
form of files of hourly data relating to weather parameters such as external temperature,
solar irradiance and relative humidity. In principle, different DSYs may be derived, each
based on a particular interpretation of extreme conditions; the data in the standard DSY
represent conditions that have a 12.5% probability of being exceeded.
A core element within the COPSE project concerned the development of such weather
data files based not on historic data but on future weather patterns as generated by the
Weather Generator associated with the UKCP09 climate projections. These files provide
designers with the ability to model the performance of designs under defined future
conditions, thus providing greater assurance that buildings designed now will continue to
provide acceptable environmental conditions in future decades.
But COPSE went further, by developing a different way of assembling data for summertime assessments, the Design Reference Year (DRY). The DRY addresses some well-known
shortcomings of the Design Summer Year and gives designers an alternative approach
to modelling designs in future climates. The advantages of the DRY over the DSY are
discussed more fully later.
6 BS EN ISO 15927-4: 2005 Hydrothermal performance of buildings – calculation and presentation of
climatic data, Part 4: Hourly data for assessing the annual use for heating and cooling.
7 Chartered Institution of Building Services Engineers. Guide A: Environmental Design (2006).
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COPSE: Coincident probabilistic
climate change weather data
for a sustainable built environment
UKCP09 Weather Generator Output
The Weather Generator8 associated with the UKCP09 Climate Projections produces files
of simulated hourly weather data based on the climate projections that result from the
application of Low, Medium and High Emission scenarios to the UK Climate Model. The
projections relate to 10 year intervals starting at 2020 and finishing at 2080. For each future
date, e.g. 2050, the Generator provides 3000 years of simulated weather data, each year
being based on a random starting point. Hence 3000 years of simulated weather data are
available for 21 combinations of emission scenario and future date. Furthermore, the data
can be obtained relating to any defined location, since the underlying UK climate model is
based on a grid of the UK and takes into account factors such as elevation, exposure to the
sea, degree of urbanisation etc.
However, the output from the Weather Generator does not include all the weather
variables required for assessments of building performance. In particular, wind speed and
direction and cloud cover are not included. Hence before any derivation of weather files
could commence, methods for filling these gaps had to be devised (see Box 1).
Box 1 Additions and corrections to UKCP09 data
Wind speed
Building simulation models require wind speed data for modelling natural ventilation
performance. These data are produced in the course of generating the UKCP09
datasets and are used, in conjunction with temperature and humidity data, to
calculate the rate of Potential Evapotranspiration (PET) which is important for
some (e.g. agricultural) applications of the dataset. However, they are not reported
separately owing to the values having low statistical confidence levels. Fortunately,
it is a relatively simple task to compute the wind speed from the PET values provided
in UKCP09, the other weather parameters also provided and the particular algorithm
used to calculate the PET. The calculated wind speeds were compared with output
from a similar weather generator and found to agree very well. Current climate
models cannot model wind speed with sufficient accuracy to be able to give
meaningful predictions of future wind speeds. Hence the distribution of wind speeds
derived from the UKCP09 data essentially matches the current distribution of wind
speeds.
Wind direction
The procedure adopted provided typical data taken from historical weather files.
For a given location, a frequency analysis of hourly wind direction data (0–360° in
10° steps) was carried out for each calendar month over the 10 years 1996–2005,
as well as for each month taking all years together. 12 months were then chosen
whose hourly data were closest to the average pattern for that month in the 10-year
frequency distribution. These 12 selected months provided the wind direction data
required. While these data represented typical wind direction time series data for
a site, there was no linkage with the other weather parameters derived from the
CP09 datasets, e.g. wind speed, temperature or solar radiation. Moreover, these data
inherently assumed that historical patterns of wind direction would continue into the
future, there being no basis for assuming otherwise.
8 Jones, P.D., Kilsby, C.G., Harpham, C., Glenis, V. and Burton, A. (2009). UK Climate Projections science
report: Projections of future daily climate for the UK from the Weather Generator. University of
Newcastle, UK. University of Newcastle, UK http://ukclimateprojections.defra.gov.uk/22588
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COPSE: Coincident probabilistic
climate change weather data
for a sustainable built environment
Cloud cover
The radiation balance for a building depends partly on whether the sky is clear or
cloudy. Cloud cover was derived from the UKCP09 data by taking the data on the
proportion of each hour for which there was sunshine (S), and calculating oktas from
the formula 8(1-S). (An okta is a unit of cloud cover, 8 oktas being total cover.) No
cloud cover data could be directly derived at night time and so this was estimated by
linear interpolation between the values at dawn and dusk.
Box 1 Additions and corrections to UKCP09 data (continued)
Solar radiation
UKCP09 data provide values for diffuse and direct solar irradiation on the horizontal
plane. It was found that at low sun angles these gave rise to unrealistically high
values of direct normal beam irradiation. These low angle errors in the UKCP09 data
were corrected by setting the direct radiation to zero for the first and last two hours
each day, the diffuse radiation being left unchanged. (For a further account of the
solar correction, see page 19).
Barometric pressure
UKCP09 data do not include an air pressure variable and therefore a standard, fixed
value of 101 350 Pa was assumed. This was a less significant approximation than the
others because barometric air pressure, in contrast to wind pressure, has a very small
impact on building performance.
Test Reference Year
A Test Reference Year (TRY) takes the form of an hourly data file for a single year whose
weather patterns are close to the average weather pattern over a 20-30 year period. The
TRY used in the CIBSE Guide consists of 12 months of observed hourly data. Each month
is selected separately and is the month with cumulative distribution profile for daily
data (average daily dry-bulb temperature, humidity and solar radiation) closest to the
cumulative profile for that month for the whole 20–30 year period. ‘Closeness’ is defined by
the Finkelstein–Schaffer (FS) statistic for the distribution9; this provides a measure of the
difference between two cumulative distributions of data – for example, the distribution
of daily average temperatures for a particular month (e.g. August) with the distribution of
daily temperatures over the complete set of Augusts. The lower the FS-statistic, the closer is
a particular August’s distribution of temperature to the overall distribution for August.
This process was applied to the augmented and corrected UKCP09 data, using the 3000
years of generated weather data available for any defined location, climate scenario
and future period. The FS statistic was calculated for each month by comparing the
distribution of average daily values for that month with the distribution over the whole set
of 3000 months. This was repeated for each of the three weather variables of dry-bulb air
temperature, humidity and solar radiation, producing 9000 FS statistics. For each month, a
combined FS statistic was then calculated by taking the means of the FS-statistics for the
three parameters (dry-bulb air temperature, humidity and solar radiation).
9 Finkelstein JM and Schafer RE (1971) Improved Goodness-of-Fit Tests. Biometrika 58(3), 641-645.
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for a sustainable built environment
The January with the lowest combined FS statistic was then selected as the January for
inclusion in the TRY, and so on for the 12 months. Hourly data for these months were
then extracted and concatenated to form a complete TRY of 8760 hourly sets of data. The
inconsistencies in the data at the beginning and end of each month were left unsmoothed
as there are already large discontinuities in the generated hourly data at the daily joins (at
each midnight).
The final form of the TRY was an Excel file of weather data whose monthly distributions of
daily averages for air temperature, relative humidity and solar irradiation are closest to the
average distribution of these variables over the whole set of data for the 3000 synthetic
years. Data in this form are suitable for testing the future energy performance of a building
using building simulation software. The file could be read by, for example, IES building
simulation programs, or through a conversion macro, by Designbuilder. (The latter requires
the weather file first to be converted to CIBSE TRY format – which is automatic within
the COPSE software – and then processed by the program CCweathergen to produce an
Energy Plus Weather file for Designbuilder to read.)
In principle, it is possible to produce a range of TRYs, each based on a different
combination of the three weather variables; however, it was thought that designers would
prefer to operate with a single TRY which is a common, practical future weather year for
assessing the average performance of proposed designs. In COPSE, this TRY was derived,
for any location, for each of the 21 combinations of emissions (high, medium and low) and
time period (one of seven up to 2080–2099) for which covered by the UKCP09 projections.
Figure 2.1 illustrates the projected impact of climate change. It shows, for Heathrow, the
average daily temperature for each month of the current TRY and also for TRYs derived
for future years under the UKCP09 High emissions scenario. Under this scenario, the
mean January temperature in the 2080s is projected to be some 4°C higher than in the
1970s while the projected increase in the mean July temperature is around 6.5°C. Thus
summers are expected to become warmer at a faster rate than in winters. This increase in
summertime temperatures will increase the risk of overheating in buildings.
Figure 2.1: Monthly mean temperatures for the TRYs for Heathrow under the high emission
scenario.
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Design Reference Year
As noted above, the performance of a proposed building design during a period of hot
weather is currently assessed using a file of weather data known as a Design Summer Year.
This is an actual year of hourly weather data, although in practice only the data in the
period April-September are used in the assessment. The selected year is the third warmest
over that six-month period out of a total period of 20 years (i.e. the 87.5 percentile), as
determined from daily average dry-bulb temperatures. Thus since the selection is based on
the six-month average, there is no guarantee that the resulting DSY will contain a period
when temperatures tend towards the extreme.
Moreover, the internal environmental conditions within a building during a period of
hot weather depend not only on the external temperature, but also on solar radiation,
humidity and wind speed. The selection process for the DSY does not take these other
factors into account and it can, therefore, result in a year of actual data which does not
incorporate the most testing conditions for the building. In some locations, the DSY as
constructed by this procedure has a summer period which is cloudier than the typical
conditions of the TRY.
Indeed, for some buildings, the most testing conditions occur when external temperatures
are unlikely to be at a maximum. The perimeter zones of buildings with a high proportion
of glazing will be particularly responsive to solar radiation at lower angles, and so the most
testing conditions may occur during a warm period in April or May, rather than during
a period of higher temperatures in June or July. Recognising this, the CIBSE method for
manual assessment of building thermal performance (In Guide A, referenced previously)
provides separate tables of weather data, one incorporating near-extreme solar radiation
and the other near-extreme dry-bulb temperatures These rarely coincide, as shown in
Figure 2.2. To create this figure, the average daily temperature for the same day in the
year – 1st June, 2nd June etc. – was calculated for each year of a 30-year period centred
on 2050, using weather data generated from the UKCP09 projections, and the 10 highest
averages selected. The same process was carried out using data on solar irradiance. The
result is an ‘L’ with only a small overlap in the two plots where periods of high average
temperature coincide with periods of high irradiance. One explanation is that periods of
high irradiance have low cloud cover, and with the clear skies the night-time temperature
drops significantly, thus reducing the daily average.
Figure 2.2: Coincidence of warm and sunny days in June. DRY data for Turnhouse, Edinburgh
(2050, High emissions scenario).
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To overcome the shortcomings of the DSY, COPSE developed an alternative method of
selecting data for summer-time testing, and brought these together in a Design Reference
Year (DRY). As with the DSY, the data are selected using a percentile, but for the DRY each
month is selected separately, and on the basis of more than one weather parameter – not
just temperature. The process also differs from that of the DSY by having two stages, the
first of which selects a band of candidate months on the basis of one parameter, and the
second then selects from those months using all three parameters.
The procedure for constructing the DRY based on external temperatures, using weather
data generated from the UKCP09 projections, is described in Box 2. It is designed to
produce weather data representative of the more extreme end of the weather spectrum,
and with a realistic coincidence between high values of the different weather variables.
However, it should not result in weather conditions that would rarely be experienced in
practice.
One important difference between the DRY and the DSY is that the first stage of section
for a DRY can alternatively be based on humidity or irradiance data, so giving emphasis to
aspects of the weather that may be more significant for a particular building. Hence, for
any particular choice of initial risk factor – 87.5% in the example in Box 2 – and for each
combination of emissions scenario and future date, three DRYs may be constructed: based
respectively on daily mean temperature (DRY-1), on relative humidity (DRY-2) and on total
solar irradiance (DRY-3).
Box 2 Construction of the Design Reference Year
Each DRY relates to a specified emissions scenario and a specified future date and
for a selected combination of emissions and future date, 3000 years of simulated
hourly weather data are available. The mean monthly air temperature was computed
for each calendar month and, for each January, February etc, the 3000 mean
monthly temperatures were sorted into ascending order. The point on the monthly
distribution corresponding to a chosen percentile, e.g. 87.5%, was then selected. The
years corresponding to the band of 20 points centred on that point were identified
and the data from that month from those 20 years were extracted from the 3000
years in the original weather file. Thus 20 Januaries, Februaries etc were selected.
From the set of Januaries, a specific January was selected for the DRY using the same
statistical process as was used for the TRY with the added refinement that the three
years with the lowest combined rank sum (taking into account dry-bulb temperature,
humidity and irradiance) were selected and the year within this group which had the
closest mean monthly wind speed to the mean of all 20 years was chosen. The 12
months of the DRY were thus selected.
Once all twelve months had been chosen, the relevant data were extracted from
the UKCP09 weather file, the months were concatenated and the month boundaries
smoothed (linearly interpolated between the last eight hours of one month and the
first eight hours of the next month). The end of December was also smoothed to join
smoothly to the January month. These final data form a DRY based on the original
selection of the 87.5% level of monthly external air temperature. As with the TRY,
the data are held in an Excel file which is readable by proprietary software used for
modelling building thermal performance.
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Figure 2.3 compares an example of DRY-3 with the corresponding DSY, for the three
principal weather parameters used in the selection process. Each plot shows mean
monthly values calculated from UKCP09 data for a 5km square at Manchester’s Ringway
Airport using the High Emissions scenario for the year 2080. For the comparison, only
the months of April to September are relevant since the DSY is not intended to be used
outside this period (by contrast, all 12 months of the DRY are potentially useable – see
below). The figure shows that when the near-extreme data are selected primarily on solar
irradiance, the DRY has a higher level of irradiance than the DSY, by up to 60 W/m², or about
25%, in June, July and August. By contrast, air temperatures for DRY-3 are lower in the main
summer months (by 5–7°C) than for the DSY. Relative humidity over the summer is similar
on average but with up to a 15% difference in individual monthly means. This DRY may,
therefore, be more relevant for testing buildings or parts of buildings sensitive to the level
of solar irradiance.
Figure 2.3: DRY-3, selected primarily on solar irradiance. Comparison of key parameters with the
DSY (2080 High emissions) monthly averages for Manchester Ringway.
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Use of the DRY
The ability to derive a DRY based on different weather parameters gives designers more
scope for identifying the critical conditions for over-heating in a proposed building. The
building is first modelled using the complete DRY as the weather file; from this, the month
with the highest risk of overheating is identified. The effect of varying the design is then
explored using that month’s data. Only one month is selected since the concatenation of
extreme months that forms the DRY produces a weather year that is extremely unlikely
to ever occur in its entirety. However, in a multi-zone building, it may be advisable to
investigate the performance in each zone separately, and the critical month may vary
between zones. This may have implications for the total cooling plant capacity required.
As noted above, different buildings will be more or less sensitive to solar gain. Deep
plan, heavily over-shadowed, or windowless buildings will have least sensitivity, and so
DRY-1 and DRY-2 would be more appropriate for testing their performance. Conversely, in
shallow-plan, highly glazed buildings, solar gain will be very important, and performance
would need to be tested using DRY-1 and DRY-3.
The initial choice of risk factor will change the severity of the test applied to the building
design. This can be changed by the designer, but if the DRY were to become a formally
endorsed weather data concept, it would be helpful for CIBSE to give guidance on the
percentile to be used in different circumstances.
Finally, although all the previous discussion has been in the context of performance
testing for periods of hot weather in the summer, the DRY can also be used to examine
building performance during the winter; by choosing, for example, the 12.5 percentile, the
performance may be assessed in cooler, drier and cloudier periods.
Summing up
COPSE has provided a new way of assembling weather data for the purposes of assessing
the performance of a proposed building during the summer10. By comparison with the
present DSY, the DRY provides much greater consistency between months, and much
greater assurance that the weather data file will contain periods where the coincident
values for temperature, solar radiation and humidity are representative of testing external
conditions that need to be taken into account in the design, but are not at the extreme end
of the spectrum of variability.
The DRY for a given location, timeframe and scenario is not a single dataset since it will
vary according to how extreme a user wishes the weather to be in the design assessment;
this will influence the choice of percentile in the distribution. Moreover, the critical month
will vary according to the particular building or zone, orientation, function, etc. Hence the
DRY is, rather, a methodology that provides a consistent way of selecting weather data for
assessing building performance according to the parameters of interest: solar irradiance,
air temperature or humidity.
10 Watkins R, Levermore GJ, Parkinson JB, The Design Reference Year – a new approach to testing a
building in more extreme weather using UKCP09 projections, Building Services Engineering Research and
Technology – on line March 2012 at: http://bse.sagepub.com/content/early/2012/03/26/014362441143
1170.abstract
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At present, use of the DRY would be a decision for an individual designer. However, should
it become accepted as the way of assembling weather data for assessing summer-time
performance, there would be a need for an organisation – presumably CIBSE – to provide
guidelines for its use and the way that data from UKCP09 were used, so that designers were
all working under the same “rules” and, in particular, were using the same weather data –
whether based on observations or simulation – for a given location.
2b: Solar data
Examination of the characteristics of future solar radiation data produced by the Weather
Generator that accompanied the UKCP09 projections showed that the generated data
differed markedly in some respects from current solar data. It was not clear that these
differences could be accounted for by physical changes in the atmosphere. The results
pointed to a need for some modification of the weather generator and COPSE research
informed subsequent changes in the procedure for modelling future solar radiation.
These were incorporated in a revised Weather Generator issued in January 2011, when
the contribution of COPSE researchers at Napier University to these changes was
acknowledged11.
Figure 2.4: Comparisons of sunshine duration hours corresponding to the 89.5th percentile of
daily total radiation for Heathrow. Note: old ss= UKCP09 data set, new ss= new UKCP09 data set.
11 UKCIP. About the Weather Generator version 2.0. UK Climate Impacts Programme (2011) Available from:
http://ukclimateprojections.defra.gov.uk/22580
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The changes principally related to the hours of sunshine and the diffuse radiation
component of the total solar radiation. The first is illustrated by Figure 2.4 which shows the
hours of sunshine through the day at Heathrow at 89.5% probability level in January and
June. The effect of the changes is overall to reduce model-generated hours of sunshine,
particularly at the beginning and end of the day, which produces a closer match with
observations.
The second change is illustrated by Figure 2.5 which shows the proportion of diffuse
radiation in the total radiation for two sites – Bracknell and Edinburgh – under different
climate scenarios, and compares this with observational data. In all cases, the data refer
to the 89.5% level of probability and to 13.00 hours in June. It can be seen that the earlier
version of the Weather Generator projected a much lower proportion of diffuse radiation in
future, i.e. on average much clearer skies, and that the revised version produces projections
that correspond more closely to observed data.
Both original and revised Weather Generators project an overall increase in Global Solar
Radiation by comparison with current levels. Figure 2.6 illustrates this for Bracknell during
June, using generated data for a recent period (Control) and for 2030 Low Emission and
2080 High Emission scenarios. A note of caution is needed, however, concerning the very
high increases at both ends of the day which stem from aspects of the model assumptions
and process. This caveat, though, does not detract from the overall conclusion that future
weather patterns are likely to be favourable for PV and other solar technologies.
Figure 2.5: Ratio of diffuse to global irradiation (DRG) for June at 1300 hrs at 89.5th percentile;
(a) Bracknell and (b) Edinburgh. Note: MetD= Meteorological Office data set, old= old WG
control data sets, v2= WG version 2.0 data sets, LE= Low Emissions, HE= High Emissions.
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Figure 2.6: Global solar radiation (GSR) comparison for Bracknell.
Note: MetD= Meteorological Office data set, old= old WG control data sets, v2= WG version 2.0
data sets, LE= Low Emissions, HE= High Emissions.
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3 Building performance in future climates
This Chapter provides an account of the research carried out under COPSE on the
performance of existing buildings in future climates, using the files of future weather data
described in Chapter 2. Since most of the building stock that will be in use in the second
half of this century is already constructed, it is important to ascertain whether these
buildings will continue to provide acceptable internal conditions, or whether extensive
modifications will be required. The COPSE research covered the propensity of buildings
to overheat in periods of hot weather, the impact of generally warmer climates on annual
energy consumption, and the relationship between the external noise environment and
the ability to cool a building through natural ventilation. The significance of the third study
for future building performance is explained in Section 3c.
3a Overheating
Only a selection of the studies will be described here; the references 9 and 10 provide a
fuller account of the research12,13.
Four contrasting existing buildings – an office building, a primary school, a hospital and
a residential care home for the elderly – were modelled using EnergyPlus 6 software14.
Thumbnail diagrams of the buildings are shown in Figure 3.1 while key physical details
are in Table 3.1. With the exception of the office building (constructed in 1994), all were
constructed recently. The buildings differed considerably in their patterns of occupation
and the modelling took into account likely hours of occupancy, the number of people likely
to be in the building, and the internal energy gains from lighting and electrical equipment,
using widely accepted data15.
All the buildings were naturally ventilated, the ventilation rate being set during the
summer period at 4 air changes per hour – a typical value that might be expected for
spaces mainly ventilated from one side with windows open on still, or virtually still, warm
summer days. This rate was assumed to occur when the internal temperature exceeded
25ºC and in addition was higher than the external air temperature. An additional
infiltration allowance of 0.5 air changes per hour was assumed for the whole period of the
simulation.
12 Du, H., Underwood, C.P. & Edge, J.S. (2012a). Generating design reference years from the UKCP09
projections and their application to future air conditioning loads.Building Services Engineering Research
and Technology 33(1).
13 Du, H., Underwood, C.P. & Edge, J.S. (2012b) Generating test reference years from the UKCP09
projections and their application in building energy simulations. Building Services Engineering Research
and Technology. Doi: 10.1177/0143624411418132, 20pp.
14 National Calculation Method Modelling Guide. Available at: www.ncm.bre.co.uk
15 Energy Analysis and Tools – EnergyPlus Software. US Department of Energy – National Renewable Energy
Laboratory. Available at: www.nrel.gov/buildings/energy-analysis.html
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Figure 3.1: Thumbnails of case study buildings.
Table 3.1: Details of case study buildings
Building
Zones
Gross floor
area (m2)
Treated floor
area (m2)
Effective
thermal
capacity
(kJm-2K-1)
Office
36
4269
2977
466
School
25
4870
2844
285
145
21,897
12,786
259
51
5683
5345
425
Hospital
Care Home
Each of the buildings was simulated using weather data taken to be representative of
present conditions (the ’Control’) and with weather data generated for a range of future
emissions scenarios and for time periods centred on 2030, 2050 and 208016. In addition,
these simulations were repeated for three locations: London, Manchester and Edinburgh
– thus the same building was modelled with weather data relevant for each of these
locations. Only results for Manchester are presented here; Table 3.2 lists the symbols used
in displaying these results.
16 The Control dataset is based on weather data recorded in the period 1961–1990. Hence the time interval
between the middle year of this band and the middle year of the 2030 band is 55 years, which is larger
than the interval between the middle years of the other bands used in the analysis. This accounts for the
significant difference between ‘Control’ and other data points in Figures 3.2 to 3.6.
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Table 3.2: Symbols for time periods and carbon emissions
for a sustainable built environment
Symbol
Meaning
C
Control data
3L
2030s Low carbon emission scenario
3M
2030s Medium carbon emission scenario
3H
2030s High carbon emission scenario
5L
2050s Low carbon emission scenario
5M
2050s Medium carbon emission scenario
5H
2050s High carbon emission scenario
8L
2080s Low carbon emission scenario
8M
2080s Medium carbon emission scenario
8H
2080s High carbon emission scenario
The risk of overheating was examined using two different percentiles in the distribution of
external temperatures (see discussion of selection of weather data in Chapter 2). The first
was 87.5%17 because this is the risk level used by CIBSE in its tables of data for summertime design assessment. The second was 99% in order to examine the impact of rising
temperatures in situations where there is a need to minimise the risk of overheating. Some
results from the four buildings are shown in Figures 3.2 and 3.3.
Figure 3.2 presents the percentage of occupied hours for which the internal temperatures
exceed 28°C. It shows a rising trend throughout this century. Even at the 87.5 percentile
level of risk, the office building exhibits sharp increases in the percentages of time during
which discomfort might be expected, rising by 2050 to more than 15% of occupied hours
under all carbon emission scenarios. Although the rise is not quite as marked for the
primary school, there is still a clear increase in the proportion of time when high internal
temperatures may inhibit learning. The traditional construction methods used in the care
home, which give it a relatively high mass and a relatively small proportion of glazing,
mean that temperatures exceed 28°C for less than 5% of occupied hours under the low
emission projection, using the 87.5 percentile level of weather data. Although this level
may still be too high for its elderly occupiers, the result does illustrate the difference that
can be made through choice of construction measures. Similar conclusions apply to the
hospital, partly because of its traditional high-mass construction and partly because of the
high proportion of deep-plan spaces in this building which are not as influenced by future
increases in solar radiation. The school example demonstrates that a sharp increase in the
percentage of overheating hours ( Figure 3.2) does not necessarily imply a high demand
for cooling ( Figure 3.3), because the school has spaces with low occupancy rates during
periods when hot weather is most likely.
17 Figures 3.2, 3.3 and 3.6 refer to the 85th percentile but in CIBSE nomenclature this is the 87.5 percentile.
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Figure 3.3 shows the cooling capacity per unit of floor area required to maintain each
building at a conventional design maximum internal temperature of 28°C. These cooling
design loads also show a steady rising trend through this century. The office building and
care home show a near-tripling in average zone cooling design loads from the present
to 2080 under the high emission scenario (85th percentile risk level). The trend for the
hospital shows a lower rate of increase, although from a much higher base level; this is
because internal heat gains attributable to equipment account for a larger proportion
of the current cooling load than in the case of the other buildings. The school shows
lower overall average design cooling loads and a much flatter rate of increase over time.
This suggests that the high rate of increase in summer-time overheating in the school is
attributable to a small number of spaces where the temperature is strongly influenced by
external temperatures and solar radiation.
Figure 3.2: Summer-time overheating (Manchester) – a) Office b) School c) Hospital
d) Care home.
Figure 3.3: Cooling design loads (Manchester) – a) Office b) School c) Hospital
d) Care home.
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In another study18 undertaken within the COPSE programme, the cooling capacity required
to maintain comfort conditions in a room with typical thermal properties was calculated
for future time periods, under different emissions scenarios. This study took into account
the decline in performance of cooling systems as external temperatures increase, and
also the additional power consumed by fan systems when more heat has to be removed
through existing ductwork. It concluded that a building designed to provide comfort
conditions for 95% of occupied hours would need around 40% additional cooling capacity
by the 2080s, and that up to five times the fan power would be required in the system to
move air through the same ducting.
The outputs of COPSE research, some of which have been illustrated here, confirm that
many buildings will require either substantial modification or the introduction of cooling
systems (or both) if they are to continue to provide acceptable internal conditions in the
future. Where cooling plant is already installed, it is likely to be replaced several times
during the life of a building and at that time extra capacity and more efficient systems
can be introduced, although increasing the size of air distribution systems may be more
problematic. Where buildings rely at present on natural ventilation, the ability to install
cooling plant may be restricted and this could prejudice the future use of the building.
(Chapter 4 considers how the adoption of Adaptive Comfort principles may help to address
this issue.)
The results also underline the importance of the choices made at design stage in new
buildings, if these are to provide acceptable internal conditions over the whole of their
service life. The choice of construction materials, massing, orientation and shading design,
and the provision of space for possible future mechanical services all take on greater
relevance as these cannot easily be modified during later refurbishments to combat the
impacts of a warming climate.
3b Annual energy use
The energy required for cooling the four buildings in a typical year, under different climate
scenarios, was estimated through the modelling process. The results (in terms of cooling
energy consumption per unit area) are shown in Figure 3.4, for Manchester and also for
London and Edinburgh. In each case, cooling energy shows a rising trend but the impact
varies according to the type of building and the location. Under the high emissions
scenario, cooling energy use in the office, care home and hospital buildings is predicted
by the 2080s to be at least twice the present level. The school building shows the lowest
annual rate of cooling energy increase owing to a large number of its spaces being within
deeper-plan core areas and low internal casual heat gains due to equipment.
For each building type, the annual cooling energy use is higher (in some cases much
higher) in London than in the northern cities of Manchester and Edinburgh. This reflects
not only the difference in latitude but also the impact of the London ‘Urban Heat Island’
(see Section 2b) which raises the summer-time temperature in central London above that
of surrounding areas.
Figure 3.5 shows results from a similar study of heating energy requirements. By contrast
with cooling, however, this demonstrates a declining trend over the century. Annual
energy use for each building is predicted to be lower in London than in the northern
cities though the differences between locations are not as pronounced as is the case with
cooling.
18 Watkins, R. and Levermore, G.J. (2011). Quantifying the effects of climate change and risk level on peak
load design in buildings. Building Services Engineering Research and Technology, 32(1), 9-20.
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Figure 3.4: Annual cooling energy – a) Office b) School c) Hospital d) Care home.
Figure 3.5: Annual heating energy – a) Office b) School c) Hospital d) Care home.
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Although, the warming trend over the next decades will reduce annual energy use for
heating of buildings, it makes little difference to the heating plant capacity that is required.
This is illustrated in Figure 3.6, which shows the heating design load per unit of floor area
for the four buildings under the same future climate scenarios as previously. The reason
is that the weather data generated from the UKCP09 projections shows that winters will
still have ‘cold snaps’ of the same intensity as at present even though average winter
temperatures are higher. Thus decisions on plant sizing, which are based on the ability
to maintain internal temperatures during such cold periods, are not greatly affected by
future changes in the climate. However, they will of course be affected by measures taken
to improve the thermal efficiency of both new and existing buildings, with consequent
reduction both in the heating capacity required and in annual heating energy use.
Figure 3.6: Heating design loads – a) Office b) School c) Hospital d) Care home.
The substantial increases in cooling energy use due to climate change are, however,
unlikely to benefit from measures taken to reduce heating energy consumption and in
some cases these may actually exacerbate the need for cooling. This reinforces the need
for enhanced attention to the potential for over-heating during the design, and possibly to
make provision for future cooling systems, so that building service lives are not shortened
by the inability to combat over-heating.
COPSE research on the implications for national energy consumption of possible trends in
energy use for heating and cooling of buildings is summarised in Chapter 6.
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3c Ventilation and noise
Most buildings in the UK rely on natural ventilation to maintain comfortable internal
conditions during period of lot weather, i.e. they have windows that can be opened.
The internal conditions in such buildings depend upon the ability of occupants to
open windows, the wind speed, wind direction and the external temperature. Building
users are inhibited from opening windows if the external environment is noisy but may
accept a degree of external noise for a small portion of the year if that reduces internal
temperatures. Warmer conditions will tend to increase the proportion of time that
windows need to be open. Thus some naturally ventilated buildings which on balance
provide acceptable conditions because windows need to be opened for only a small
portion of the year may become unacceptable for their occupants. These buildings will
need either modification, perhaps with the installation of mechanical ventilation and
cooling systems or, in the extreme, demolition and re-build.
The research carried out in COPSE included studies of how the need for window opening
might change in future climates, and the relationship with the external noise environment.
These studies showed that use of energy for cooling in buildings that are currently
naturally ventilated for much of the year could increase significantly.
The future effectiveness of natural ventilation
Future wind speeds needed first to be estimated. The derivation of future wind speeds
from the weather data generated from the UKCP09 climate projections was described
in Section 2a. This method was used, but other estimates were also employed including
alternative weather generators and accessing wind speeds obtained from the Regional
Climate Model on which UKCP09 was partly based19. The results showed considerable
variability in change factors from month to month, but were consistent with upper and
lower bounds of the range indicated by the Regional Climate Model.
Dynamic thermal modelling using DesignBuilder was then employed to explore how these
different estimates of future wind speeds affected the predicted ventilation rate of a typical
office building (shown in Figure 3.7). It was found20 that the estimates resulting from the
dataset of the PROMETHEUS project21 gave consistently higher ventilation rates than those
from the COPSE dataset; this would be beneficial for avoiding the need for mechanical
ventilation but at present it is not possible to say which estimate is likely to be more
reliable as a predictor of future wind speeds.
19 UK Met Office Hadley Centre. HadRM3-PPE-UK Model Data. (2009) Available from: http://badc.nerc.
ac.uk/data/hadrm3-ppe-uk/
20 Barclay, M., Sharples, S., Kang, J. and Watkins, R. (2011). The natural ventilation performance of
buildings under alternative future weather projections. Building Services Engineering Research and
Technology, 33(1): 35–50.
21 Eames, M., Kershaw, T. and Coley, D. (2011). The creation of wind speed and direction data for the use in
probabilistic future weather file. Building Services Engineering Research and Technology, 32(2): 143–158.
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Using these two weather datasets, the thermal performance of a small naturally ventilated
office building equipped with passive cooling measures (shown in Figure 3.8) was
investigated. The measure of comfort chosen was the percentage of occupied hours
for which the internal temperature was above a defined comfort level – either a fixed
28°C as found in CIBSE guidance22 or the ‘adaptive comfort’ temperature defined by CEN
and British Standards.23 Figure 3.9 shows the results from models using weather data
representative of the present day, in 2050 and in 2080 under the UKCP09 High Emissions
scenario. In all cases, the proportion of time for which internal temperatures exceeded
the comfort threshold increased very significantly by 2080, calling into question whether
natural ventilation would continue to provide overall acceptable environmental conditions
without assistance from mechanical cooling systems during some part of the year, i.e. a
‘mixed mode’ approach to cooling.
Figure 3.7: Sketch representation of the office building used to explore ventilation rates.
Figure 3.8: Sketch of small office building with passive cooling measures, such as solar shading,
used to explore impact of window opening on internal temperatures.
22 Chartered Institution of Building Services Engineers. CIBSE Guide A: Environmental design (2007)
23 The concept of adaptive comfort is discussed in Chapter 4.
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Figure 3.9: Percentage of occupied hours above thermal comfort threshold against mean
summer temperature legend for two 50 and 90th percentiles of the PROMETHEUS DSY and the
COPSE DSY.
The influence of external noise on ventilation rates
The combination of acoustic and ventilation performance in mixed mode buildings
was explored through the use of noise maps which provide a guide to the external
noise environment in any location24. From noise mapping, the external noise level at
different points on the façade of a building may be calculated. Figure 3.10 shows a typical
output from such a calculation; it illustrates that the exposure to external noise can vary
considerably over the different faces of the building.
The thermal performance of this building was modelled in two contrasted locations in
Manchester, in order to determine the energy that would be required for cooling in future
climates. The degree of window opening was adjusted so that internal noise levels were
close to a chosen tolerance level; this required modelling of the noise transmission through
a window aperture25. Figure 3.11 shows that the average rate of use of energy for cooling
increases markedly as the noise tolerance level decreases, with the two plots showing the
influence of location. The figure also enables the impact of acoustic control measures to
be estimated, since a measure that, for example, will reduce internal noise by 10dB(A) will
reduce the rate of cooling required by the same amount as if the external environment
were that much quieter.
The impact of future climates was also examined. Figure 3.12 shows how the average
cooling energy rate increases in future for the same noise environment. In the model
example, the increase between the present rate and that required in 2050 under the high
emissions scenario was some 11kw. To maintain the cooling energy consumption at its
present level would require a reduction in internal noise in excess of 10dB(A) through a
combination of mitigation measures at the building and measures to reduce the noise
generated by external sources (e.g. the introduction of quiet road surfaces).
24 Barclay, M., Kang, J. and Sharples, S. (2012). Combining air borne noise mapping and ventilation
performance for non-domestic buildings in an urban area. Building and Environment. 52: 68–76.
25 Kang, J. and Li, Z. (2007).Numerical Simulation of an Acoustic Window System Using Finite Element
Method. Acta Acustica united with Acustica. 93(1):152–163(12).
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Figure 3.10: Noise mapping noise exposure pattern (Building 1, Manchester, high external noise
level).
Figure 3.11: Relationship between cooling energy use in mixed mode building and the level of
tolerance of noise in different noise locations (Red: quiet location; Blue: noisy location).
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Figure 3.12: Relationship between cooling energy use in mixed mode building and the level of
tolerance of noise, present and future climates (Control weather data and 2050 high emissions
scenario).
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4 Thermal comfort standards and implications
for energy use for cooling
The concept of adaptive comfort
Adaptive Comfort is a the term used to describe the ability of building occupants to adapt
to different environmental conditions, so that people feel comfortable after a change in
their local environment after being exposed to the changed environment for a period. In
the context of building design, this means that during a period of hot weather building
occupants may feel comfortable with internal temperatures that are considerably higher
than conventional ‘comfort’ conditions (e.g. the temperature to which buildings are often
cooled in summer) after a day or two. In part, this is because they will open windows and
adapt their clothing to the external conditions.
As with all measures of comfort, measures of Adaptive Comfort relate to conditions that
will be considered comfortable by most building occupants, but because of the variability
of individual responses to their environment, some building occupants will consider the
conditions unsatisfactory.
It should also be stressed that Adaptive Comfort criteria relate only to buildings that
are ‘free-floating’, i.e. there is no reliance on mechanical systems to maintain comfort
conditions in summer. Occupants open windows, draw blinds and adjust clothing to
maintain comfort conditions.
Because Adaptive Comfort criteria lead to ‘comfort’ temperatures that can be higher than
those conventionally adopted as fixed control points in air-conditioning systems, they
reduce the need for such systems to be installed. In particular, some existing buildings
which otherwise would need to be refurbished with mechanical cooling systems can
continue to rely on natural methods of ventilation. COPSE research26 explored the
impact, now and in the future, of changing to Adaptive Comfort criteria for design, using
alternative approaches to the definition of Adaptive Comfort.
The adaptive comfort degree day
Two ways of arriving at a band of comfort temperatures using the principles of Adaptive
Comfort have been incorporated into Standards27,28. However, these produce different
upper and lower limits to the band and little guidance is available to policymakers,
designers and energy managers to help them make an informed choice when choosing
between standards. In order to address this, the COPSE research developed a novel metric,
the Adaptive Comfort Degree-Day, which was then used to compare the potential energy
savings from each approach.
26 McGilligan, C., Natarajan, S. and Nikolopoulou, M. (2011). Adaptive Comfort Degree-Days: A metric
to compare adaptive comfort standards and estimate changes in energy consumption for future UK
climates. Energy and Buildings, 43(10): 2767–2778.
27 Indoor environmental input parameters for design and assessment of energy performance of buildings
addressing indoor air quality, thermal environment, lighting and acoustics – BS EN 15251:2007, CEN,
Brussels, 2007/BSI, London, 2008.
28 Thermal Environmental Conditions for Human Occupancy – ANSI/ASHRAE standard 55-2004, ASHRAE,
Atlanta, 2004.
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The degree-day is a familiar concept to building services engineers. It is the sum of the
mean daily internal-external temperature differences over the period of operation of the
heating or cooling system, the internal temperature having been calculated taking into
account the effect of internal thermal gains and solar heating29. Although these heat
inputs fluctuate over the course of a day, they can be taken to have a constant average
value and so raise the internal temperature by a constant amount. The resulting figure for
degree days relates directly to the energy required by mechanical systems to maintain a
defined, normally fixed, temperature which will result in a high proportion of the building
occupants feeling comfortable.
Each degree rise in outdoor temperature, if maintained for a period which depends on the
individual building, results in the same rise in internal temperature in the absence of any
mechanical cooling system and so internal temperatures may be calculated directly from
weather data. Figure 4.1(a) illustrates how average daily external temperatures rise and
fall over the course of a summer. The shaded area is a measure of the cooling degree-days
in a building where the internal temperature rises above a fixed upper bound for comfort
temperature; alternatively, it is a metric for the cooling energy required over that period
to maintain the building at the (fixed) comfort temperature. Since in the absence of a
mechanical cooling system there is a direct relationship between the internal temperature
of the building and the external temperature, the same curve (Figure 4.1(b)) also describes
the internal temperature that would be achieved and the resulting shaded area shows
what might be termed quasi- cooling degree-days.
However, the upper bound of the comfort band, as defined by Adaptive Comfort criteria,
often exceeds the internal temperature in periods of hot weather, since it reflects the
occupants’ experience of progressively higher external temperatures. It follows a curve
shown in Figure 4.1(c). The shaded area here represents the number of Adaptive Comfort
Degree-Days (ACDDs). Studies undertaken as part of the COPSE project showed that this
metric is a reliable indicator of the maximum saving in cooling energy use to be obtained
from adoption of Adaptive Comfort criteria for determining the comfort temperature.
Figure 4.1: Derivation of the ACCD concept from the conventional cooling degree-day.
29 Chartered Institution of Building Services Engineers. (2006) Technical Memorandum 41: Degree-days:
theory and application.
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In these studies, the cooling energy requirement and the number of Adaptive Comfort
Degree Days were calculated for a mechanically-cooled, single storey office building
(illustrated in Figure 4.2) of dimensions 15 x 25 x 3.5 m using five different construction
types and five levels of glazing (10, 30, 50, 70 and 90%) in 22 different European locations.
These ranged from Aberdeen (summer mean temperature 13.3ºC, annual direct normal
solar radiation level 483 kWh/m2) to Marseille (summer mean temperature 23.3ºC, annual
direct normal solar radiation level 1504 kWh/m2). Thus in total 550 annual simulations of
energy use and internal temperatures were undertaken. The weather files used provided
hourly data for the principal weather parameters (temperature, solar irradiance etc) while
the modeling was carried out in DesignBuilder using EnergyPlus software30.
Figure 4.2: An example of a building used in the modelling experiments – medium weight,
pitched roof, 30% of wall surface glazed.
For each location, the comfort temperature through the year was recorded and the
number of ACDDs returned by each location was calculated by two methods, first
using category II of the European adaptive standard (EAS) and secondly using the 80%
acceptability level of the ASHRAE adaptive standard (AAS)31. These two classes of standard
are comparable since they both predict that 10% of occupants will be dissatisfied with
the general internal temperature. Figure 4.3 shows, for one example of the 25 buildings,
the very close relationship between the annual total cooling energy consumption and the
number of ACCDs in each location. This figure was derived using the European standard
but similar results were obtained with the ASHRAE standard. The correlation coefficient
was in each case between 0.89 and 0.99, with an average of 0.97.
This research therefore showed that the ACDD was a good metric for annual cooling
energy consumption for this building, and that by extension was a good metric for the
potential energy savings to be made by relying on passive cooling measures and natural
ventilation and using the adaptive comfort concept to judge the acceptability of internal
temperatures instead of introducing air conditioning.
30 US Department of Energy, Building Energy software Tools Directory – IWEC.
31 An allowance was made for an average of a further 10% dissatisfaction that might occur because of
local thermal discomfort, in addition to the general whole body 10% dissatisfaction. See G. Schiller
Brager and R. de Dear, A Standard for Natural Ventilation. (2000) ASHRAE Journal 42 (10), pp21-28.
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Figure 4.3: Correlation between annual number of cooling EAS ACDDs and total annual cooling
energy consumption for the medium-weight building with 30% glazing.
Energy savings from the application of the ACDD concept in future climates
The way in which adoption of adaptive comfort criteria could result in reductions in cooling
energy use in the future was explored through calculating the ACDDs under both the EAS
and AAS standards using simulated future weather data derived from UKCIP09 data. These
calculations were performed for three locations (London, Manchester, Edinburgh) and
three future time periods (2020s, 2050s, 2080s). In addition, calculations were performed
with future Test Reference Years as described in Section 2a.
The results are shown in Figure 4.4. They showed that, for each city, the potential
savings achieved by an EAS-compliant building (bold line) would not be matched by its
counterpart AAS-compliant building (dotted line) until decades later Indeed, in most
cases savings derived from use of the EAS standard in the 2020s would not be matched by
savings derived from the AAS standard until the 2080s or later. These findings reflect the
higher upper limit of the thermal comfort zone in the EAS, which enables a greater number
of buildings to use natural ventilation.
This research therefore produced a novel method for assessing the energy savings that
could be made through the adoption of Adaptive Comfort criteria, if these showed that
buildings could function satisfactorily without mechanical cooling systems. Further, it
demonstrated that the use of the European standard for Adaptive Comfort resulted in
potentially greater savings than the ASHRAE standard.
Figure 4.4: Annual number of cooling ACDDs for the AAS and the EAS for (a) High and (b) Low
emissions scenarios for Edinburgh, Manchester and London for the 2020s, 2050s and 2080s.
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5 Urban heat islands and canyons
The air temperature in an urban area is almost always higher than that in the surrounding
rural area; this phenomenon is termed the Urban Heat Island (UHI). It arises for two
principal reasons: first, built-up areas and rural areas gain heat from the sun and lose it to
the atmosphere at different rates, the rural areas being exposed to more of the ‘cold’ sky
while buildings in urban areas are less exposed to the sky and retain more heat in their
structures; secondly, an urban area has many local sources of heat, notably buildings and
vehicles, which raise the temperature of the surrounding air. The relative importance of
these factors varies – in summer, solar radiation is the dominant influence while in winter,
heat losses from buildings and traffic account for most of the effect. There are also diurnal
changes; typically, in summer the UHI reaches a maximum (which can be up to 8°C in
Manchester) during the night, as buildings and roads release heat absorbed during the
day; in winter, this effect is less frequent although it can be more intense32. These variations
are illustrated in Figure 5.1.
Figure 5.1: Distributions showing the magnitude of the Urban Heat Island in Greater Manchester
in summer and winter.
32 Levermore and Cheung, (2012) A low order canyon model to estimate the influence of canyon shape
on the maximum Urban Heat Island effect. BSERT. Published online before print January 18, 2012, doi:
10.1177/0143624411417899
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A feature of the central parts of large urban areas is that they have ‘street canyons’.
Because of the height of the buildings lining the street, the view of the sky from ground
level is restricted (Figure 5.2) and this influences the radiation heat exchanges that take
place between buildings and the atmosphere, and therefore the scale of the UHI. Figure
5.3 illustrates how neighbouring buildings reduce radiation heat loss. A measure of the
depth; width ratio of the street canyon is the Sky View Factor (SVF); this is essentially
the proportion of the sky hemisphere that can be seen from ground level. COPSE
research explored the influence of the SVF on the Urban Heat Island, using data from the
Manchester urban area33.
Figure 5.2: Hemispherical image of John Dalton Street, Manchester, using a Nikon FC-E8 Fisheye
Lens.
Figure 5.3: Illustration of heat exchanges between buildings in a street canyon, as compared
with the heat loss in a rural area.
33 H K W Cheung (2011). An Urban Heat Island study for building and urban design. A thesis submitted to
The University of Manchester for the degree of Doctor of Philosophy in the Faculty of Engineering and
Physical Sciences.
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Monitoring urban temperatures
In order to characterise the Manchester UHI, air temperature sensors incorporating data
loggers were installed at 59 sites in the Greater Manchester area, broadly on eight radial
routes as shown in Figure 5.4. The sensors were mounted on lamp-posts at a height of
4 m (Figure 5.5) and recorded the temperature at 30 minute intervals. Data were collected
from February 2010 to April 2011. The reference rural air temperature data came from the
British Atmospheric Data Centre34.
Figure 5.5: Sensor mounted on
lamp-post.
Figure 5.4: Map showing locations of sensors.
Because of its influence on heat loss through radiation to the sky the effect of the SVF is
most marked on clear, calm nights and so from the complete dataset nights were identified
when cloud cover at Manchester Airport was less than 25% and wind speed was lower than
2.5 m/sec, with the two conditions persisting for at least four hours. These data were then
used in subsequent analyses.
Estimation of the Sky View Factor
The wide availability of high quality digital images enabled the research to utilise a new
approach to estimating the SVF. As Figure 5.2 shows, photographs taken with a fish-eve
lens provide a 360° perspective of the street canyon. This may then be analysed, to identify
the white pixels which form the sky image, in contrast to those of other colours which
relate to buildings. The proportion of white pixels in 37 annular rings which, together,
make up the sky hemisphere is found and from that, the SVF is determined35.
34 British Atmospheric Data Centre, see: http://badc.nerc.ac.uk/home/
35 Cheung, H.K.W. (2011). An Urban Heat Island study for building and urban design. A thesis submitted to
The University of Manchester for the degree of Doctor of Philosophy in the Faculty of Engineering and
Physical Sciences.
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Tests showed that the resulting SVF did not change significantly if the camera was at one
side or the other of the street, unless the building heights differed considerably from one
side to the other. Neither was the SVF significantly affected by whether the camera was at
ground level or head height, and so the height was standardised at 1.4 m.
The relationship between SVF and urban temperatures
Figure 5.6 shows, for the 59 sensor locations, a weak relationship between the SVF and the
average UHI. The charts are based on data for clear and calm summer and winter nights
respectively. As might be expected, UHI tends to increase as the SVF decreases, since the
ability to lose heat through radiation reduces. But the effect is influenced by other factors,
for example, the extent to which the buildings are heated during the day will depend
upon the orientation of the canyon; there will be more extensive shading if it is East-West
as compared with North-South. For deeper canyons (SVF less than 0.65), however, the
relationship is stronger.
The UHI and building design
Designers need to take the UHI into account when assessing whether a building will
be able to provide comfortable conditions in periods of hot weather without resort to
mechanical cooling systems, and when estimating the annual energy use associated with
such systems. Further, the rise in night-time temperatures attributable to the nocturnal
UHI has implications for the comfort, and potentially for the health, of urban residents.
Previous research led by Manchester University36 investigated how the UHI in Manchester
and Sheffield might be influenced by climate change and the measures that could be
taken to mitigate the impact of increased temperatures. The COPSE research added to the
understanding of the factors that influence the UHI. Combined with the future weather
files discussed previously, it provides a better basis for assessing the performance of
buildings in urban areas.
Figure 5.6: Relationship between UHI and Sky View Factor.
36 SCORCHIO: Sustainable Cities: Options for Responding to Climate cHange Impacts and Outcomes (2007
to 2009). EPSRC grant EP/E017398/1. See: http://gow.epsrc.ac.uk/NGBOViewGrant.aspx?GrantRef=EP/
E017398/1
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6 Implications of climate change for energy
consumption in the national building stock
Heating buildings (space heating) accounts currently for some 16% of national energy
consumption37. The research summarised in Section 3b showed that the rise in average
winter temperatures expected as a consequence of climate change will reduce the energy
required for heating, but the scale of reduction differs with the type of building. Other
research undertaken within COPSE aimed to quantify the implications of this reduction
for the national stock of buildings. To do this, it took a top-down view, considering the
influence of temperature changes not on individual buildings but on heating energy
consumption over a region.
Gas demand and space heating
Almost 80% of the energy used for space heating is provided by gas. Thus the relationship
between daily average temperature and daily gas consumption can be used to predict
daily gas demand during warmer winters. National Grid, which owns and operates the
National Transmission System, publishes daily demand data for each of the thirteen
geographic Local Distribution Zones (LDZs) which make up Great Britain (i.e. not including
Northern Ireland). Stripping out the consumption that is not weather-dependent (e.g.
industrial use), the residual daily gas consumption for a specified LDZ correlates strongly
with the daily effective temperature38 recorded at a weather station representative of the
LDZ. This is shown in Figure 6.1; with the exact shape of the characteristic sigmoid curve
being dependent upon a number of factors such as geographical latitude and whether the
population is predominantly urban or rural.
Figure 6.1: Relationship between Space Heating Gas Consumption for the North West LDZ and
the Effective Temperature measured at Woodford for the period 2007–2010.
The principal area of interest is the left-hand section of the plot where consumption is
high, since this represents most of the winter. In order to achieve a better relationship
in that part of the curve, the curve was represented as a set of three lines, each with its
characteristic slope (Figure 6.2). This provided the starting point for estimating regional
heating energy demand in future climates.
37 Department for Energy and Climate Change, London. Energy Consumption in the UK. www.decc.gov.uk/
en/content/cms/statistics/publications/ecuk/ecuk.aspx
38 A weighted “composite temperature” incorporating temperatures recorded on previous days.
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Figure 6.2: Segment Regression Analysis performed on Woodford/North West LDZ data.
Demand for space heating in future climates
Daily mean temperatures for future time periods, under different emission scenarios, and
for a location typical of each of the 13 LDZs, were calculated from multiple runs of the
UKCP09 weather generator. Each run produced 99 years of weather data and each average
temperature was derived from 100 runs, i.e. 9900 years of weather data; in total over one
million years of data were generated. From the resulting daily averages over the winter
heating season, and the relationship between daily mean temperature and gas consumption,
future levels of regional (LDZ) heating energy consumption could be calculated. The national
heating energy consumption was then the sum of the 13 regional figures.
This study showed that, depending on the emissions scenario chosen, space heating energy
demand in the present building stock fell by 16-18% in the 2030s with steady decline for the
next 50 years, so that demand in the 2080s level was 27-43% lower than at present. These
reductions are illustrated in Figure 6.3.
Figure 6.3: Reduction in Annual Space Heating Gas Consumption under Low, Medium and High
Emissions scenarios.
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These estimates assume no change in the building stock. But there will of course be
changes in future decades, of which the most significant for heating energy use will be the
introduction of energy efficiency measures in the present stock, the replacement of some
of the present stock by new, more thermally efficient buildings, and the overall increase
in stock expected over the next decades, in response to population pressures. Estimating
the impact of these changes was outside the scope of the research, but the future daily
averages derived through COPSE may be used in combination with consumption data
revised to reflect stock changes to provide more realistic estimates of future heating
energy consumption.
The research has shown, though, that irrespective of changes in the stock, climate change
is likely to have a significant impact on space heating energy use.
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7 Concluding observations
This report has summarised the coherent programme of research undertaken through the
COPSE project. The core element in the project was the development of weather data files
based on the most recent climate projections for the UK. These were then used to examine
the potential impact of climate change on the design and operation of buildings over the
coming decades. The scope was broad: thermal comfort – its implications for design and
for the continued use of existing buildings, and how greater use of mechanical cooling
system might be avoided; cooling and heating energy consumption both for individual
buildings and over the national building stock; the relationship between ventilation,
cooling requirements and the external noise environment; the characterisation of urban
heat islands. The project was, arguably, unique in tackling such a range of issues.
COPSE research findings will, it is hoped, influence future building design, and policies
towards the built environment, through a number of routes. In the first place, they add to
the body of knowledge that can be drawn upon by designers, building owners and those
responsible for regulatory and energy policies. More specifically, they are contributing to
the current update of CIBSE Guide A, which is a key document for the design of building
services.
The need to take account of potential changes in weather patterns, when these can be
projected only on a probabilistic basis, poses challenges for designers and their clients.
The assessment of risk – e.g. of overheating – becomes much more complex. COPSE has
shown how weather files can be constructed that will assist such assessments and one
consequence may be the development of weather data for the sizing of heating and
air-conditioning plant by simulation rather than by the current method which has its
original in manual calculations.
A complete (to date) list of COPSE publications is included in this report, as well as contact
details of relevant research staff. There will in addition be five PhD theses ((two still to be
examined). Because they relate to specific locations, time periods etc, the future weather
data files are not contained in a database but are produced to order. They have already
been used in relation to actual design exercises; included in the report is a Fact Sheet
from the Technology Strategy Board’s programme Design for Future Climate – Adapting
Buildings illustrating the use of the COPSE weather files by a member of the Stakeholder
Group.
With buildings accounting for a significant proportion of UK carbon emissions, and playing
a key role in the health and welfare of the population, it is essential that they should be
both efficient and comfortable, now and in the future. COPSE research has added to our
understanding of the issues, and improved our ability to design and adapt buildings so
that they will function effectively in future climates.
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Outputs from COPSE
Publications
Temperature data and building design weather datasets
Watkins, R., Levermore, G.J. and Parkinson, J.B. (2012). The Design Reference Year – a
new approach to testing a building in more extreme weather using UKCP09 projections.
Building Services Engineering Research and Technology, online March 2012 at: http://bse.
sagepub.com/content/early/2012/03/26/0143624411431170.abstract
Watkins, R., Levermore, G.J. and Parkinson, J.B. (2011). Constructing a future weather file for
use in building simulation using UKCP09 projections. Building Services Engineering Research
and Technology, Vol 32(3): 293–299.
Levermore, G.J. and Cheung, H. (2012). A low order canyon model to estimate the influence
of canyon shape on the maximum Urban Heat Island effect. BSERT. Published online before
print January 18, 2012, doi: 10.1177/0143624411417899
Cheung, H., Levermore, G.J. and Watkins, R. (2010). A low cost, easily fabricated radiation
shield for temperature measurements to monitor dry bulb air temperature in built up
urban areas. Building Services Engineering Research and Technology, Vol 31(4): 371–380.
Solar data
Tham, Y. and Muneer, T. (2011). Sol-air temperature and daylight illuminance profiles for the
UKCP09 data sets. Building and Environment, 46(6): 1243–1250.
Tham. Y., Muneer. T., Levermore, G.J. and Chow, D. (2011). An examination of UKCIP CP02
and CP09 data sets for the UK climate related to their use in building design. Building
Service Engineering, 32(3): 207–228.
Caliskan, N., Jadraque, E., Tham, Y. and Muneer, T. (2011). Evaluation of the accuracy of
mathematical models through use of multiple metrics. Sustainable Cities and Society, 1(2):
63–66.
Gago, E.J., Etxebarria, S., Tham, Y., Aldali, Y. and Muneer, T. (2011). Inter-relationship between
mean-daily irradiation and temperature, and decomposition models for hourly irradiation
and temperature. International Journal of Low-Carbon Technologies, 6(1): 22–37.
Tham, Y., Muneer, T. and Davison, B. (2010). Estimation of hourly averaged solar irradiation:
evaluation of models. Building Service Engineering, 31(1): 9–25.
Tham, Y., Muneer, T. and Davison, B. (2009). A generalized procedure to generate clear-sky
radiation data for any location. International Journal of Low-Carbon Technologies, 4(4):
205–212.
Tham, Y., Muneer, T. and Davison, B. (2009). Evaluation of simple all-sky models to estimate
solar radiation for the UK. International Journal of Low-Carbon Technologies, 4(4): 258–264.
Building performance in future climates
Barclay, M., Kang, J. and Sharples, S. (2012). Combining noise mapping and ventilation
performance for non-domestic buildings in an urban area. Building and Environment, 52,
68–76.
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Barclay, M., Kang, J., Sharples, S., Wang, B. and Du, H. (2010). Estimating urban natural
ventilation potential by noise mapping and building energy simulation [Internet]. Proceedings
of 20th International Congress on Acoustics. Sydney, Australia. Available from: http://www.
acoustics.asn.au/conference_proceedings/ICA2010/cdrom-ICA2010/papers/p339.pdf
Barclay, M., Kang, J., Sharples, S., Wang, B. and Du, H. (2010). The challenge of balancing the
demands for a comfortable thermal and acoustic built environment in a sustainable future.
Proceedings of the International Symposium on Sustainability in Acoustics. Auckland, New
Zealand.
Barclay, M., Sharples, S., Kang, J. and Watkins, R. (2012). The natural ventilation performance
of buildings under alternative future weather projections. Building Services Engineering
Research and Technology, 33(1): 35–50.
Du, H., Underwood, C.P. and Edge, J.S.(2012). Generating Design Reference Years from the
UKCP09 Projections and their application to future air-conditioning loads. Building Services
Engineering Research and Technology, 33(1): 63–80.
Du, H., Underwood, C.P. and Edge, J.S. (2011). Generating Test Reference Years from the
UKCP09 Projections and their application in building energy simulations. Building Services
Engineering Research and Technology, 418132. Doi: 10.1177/0143624411418132.
Du, H., Edge, J.S. and Underwood, C.P. (2011). Modelling the impact of new future UK weather
data on a school building. Proceedings of the International Building Performance Simulation
Association (IBPSA) Building Simulation 2011, Sydney.
Du, H., Underwood, C.P. and Edge, J.S. (2010). Modelling the impact of a warming climate
on commercial buildings in the UK. Proceedings of the 10th REHVA World Congress, Clima
10, Antalya.
Sharples, S., Barclay, M. and Kang, J. (2012). Controlling urban noise in buildings through
facade design. Proceedings of INTER-NOISE 2012, 19–22 August, New York.
Watkins, R. and Levermore, G.J. (2011). Quantifying the effects of climate change and
risk level on peak load design in buildings. Building Services Engineering Research and
Technology, 32(1): 9-20.
Adaptive comfort
McGilligan, C., Natarajan, S. and Nikolopoulou, M. (2011). Adaptive Comfort DegreeDays: A metric to compare adaptive comfort standards and estimate changes in energy
consumption for future UK climates. Energy and Buildings, 43(10): 2767–2778.
McGilligan, C., Natarajan, S. and Nikolopoulou, M. (2011). Comparison of energy savings
achievable by adaptive comfort standards using the Adaptive Comfort Degree Day. SOLARIS
2011, Proceedings of the 5th International Conference on Solar Radiation and Daylighting,
10–11 August 2011, Brno University of Technology, Brno, Czech Republic.
McGilligan, C., Natarajan, S. and Nikolopoulou, M. (2011). Use of Adaptive Comfort DegreeDays to compare energy savings from adaptive comfort standards for future UK climates. CIBSE
Technical Symposium, 6th and 7th September 2011, De Montfort University, Leicester, UK.
45
COPSE: Coincident probabilistic
climate change weather data
for a sustainable built environment
Urban Heat Island
Cheug, H., Levermore, G.J. and Watkins, R. (2010). A low cost, easily fabricated radiation
shield for temperature measurements to monitor dry-bulb air temperature in built up
urban areas. Building Services Engineering Research and Technology, 31(4): 371–390.
Datasets and other outputs
Matlab scripts forming the weather data generators developed at Northumbria University
are available for Matlab users. Contact Professor Chris Underwood: chris.underwood@
northumbria.ac.uk.
Test Reference Years and other building design weather data for future climates derived
from UKCP09 data may be provided by the University of Manchester. Contact: Professor
Geoff Levermore: geoff.levermore@manchester.ac.uk.
46
University of Greenwich, Stockwell Street
Project description
Contact details
Name:
Eimear Moloney
Company:
Hoare Lea
Email:
eimearmoloney@hoarelea.com
Tel:
01865 339756
The project comprises the relocation of the School of
Architecture and Construction, currently situated at Eltham,
to Greenwich. It also creates a new learning resource centre
on the same site, to improve its facilities and accommodate
a growing numbers of students. The development will
be undertaken on a brownfield site in Stockwell Street,
Greenwich and proposes to provide 17 000m² of new
buildings 10 000m² for the School of Architecture and
Construction and 7000 m² for the learning resources centre
General project information
Name of project:
University of Greenwich, Stockwell
Street
Location of project: London
Project timescales and dates
Type of project:
New build
Cost of project:
£60m
Design and assessment period (pre-planning): project was
submitted for planning in February 2011
Construction period (post-consent): construction is due to
begin in summer 2011 and will take about two years
Project team
Client:
University of Greenwich
Designer:
Heneghan Peng Architects
Contractor:
Unknown
Operation and monitoring period: this will occur for 12
months post-completion
Other organisations involved (and their role): Hoare Lea
(M&E consultant), Alan Baxter (structural engineer),
Fanshawe (cost consultant)
D4FC Factsheet 6
1
Design for future climate: adapting buildings competition – Phase 1
D4FC Factsheet 6:
4 What has the client agreed to implement as a result of
your adaptation work?
1 What approach did you take in assessing risks and
identifying adaptation measures to mitigate the risks?
zz The
adaptation measures were discussed with the client
and it has been agreed to implement the following:
zz we
held several workshops at which each member
of the design team and the client attended. Climate
related design and operational risks were identified and
adaptations options and strategies developed. Each
adaptation measure and its application to the University
of Greenwich project was discussed
data was available further numerical modelling
was undertaken otherwise a “what if” approach was
taken.
{z
permanent flood protection to basement areas
{z
add access control to the standby generator
{z
include adaptable door frames for door dams
{z
connect drainage system to the BMS
{z
build-up above the attenuation tank to avoid
flotation
{z
an increase to the number of bike storage spaces
{z
allow for an increase in plant and riser space
zz where
zz this
equates to a cost uplift of the original cost plant
of £149 000 from £42 570 000 to a new total of
£42 719 000.
2 How have you communicated the risks and
recommendations with your client? What methods
worked well?
zz the
client has been in attendance at each workshop and
as such, is fully aware of all adaptation measures that
will be recommended. The client has been involved in all
areas of the design for the adaptation measures. Some
of the students from the college are also getting involved
outside of the workshops.
5 What were the major challenges so far in doing this
adaptation work?
zz a
large degree of uncertainty remains surrounding
the design basis and the context in which the effects
of climate change can be assessed. The availability
of credible future weather data is fundamental to an
analytical assessment of the impacts. The nonexistence
or unreliability of specific data relating to key risk factors
such as rainfall and wind reduces confidence in the
analysis. As a result, clients and design teams are less
3 What tools have you used to assess overheating and
flood risks?
zz the
University of Manchester were appointed to analyse
the UKCIP09 data and to provide the team with the
following:
{z
design limit data for heating and cooling systems
{z
design summer year (DSY) for overheating analysis
for Greenwich for present, 2020s, 2040s 2080s.
This data was used IES thermal modelling analysis
software
{z
test reference year (TRY) data energy use analysis
for Greenwich for present, 2020s, 2040s 2080s.
{z
peak rainfall data from the University of
Manchester was given, in terms of mm/hr for storm
water flooding risk calculations
zz the
TSB design checklist was developed further to aid
discussion and structure the design analysis at the
workshops.
D4FC Factsheet 6
2
Design for future climate: adapting buildings competition – Phase 1
Further project details
Design for future climate: adapting buildings competition – Phase 1
likely to commit to added expenditure in response to
potential risks
{z
measures that required changes to system or
component capacity were only to be implemented
when required but consequential structural and
space planning issues were implemented (as in the
first point)
zz ultimately
{z
each measure was considered in terms of its
impact on the current design and modifications
immediately introduced to facilitate a future retrofit
zz the
{z
those measures that were identified but for
which the UKCIP09 weather data provided no
firm direction were assessed on their merits and
measures introduced on a risk management basis.
This particularly applied to the risk of flooding
6 What advice would you give others undertaking
adaptation strategies?
{z
adaptation measures for future years were
triggered by the crossing of key thresholds such
as thermal capacities of plant, indoor and external
design criteria temperature criteria.
zz the
UKCIP09 weather data has the potential to provide
high resolution weather data for projects but as yet is
generally unusable by the property sector.
the implementation of adaptation measures
will affect costs and this need to be balanced against
budget
second major challenge was identifying the risks
and briefing the design team. There was a degree of
scepticism and initial defensiveness but gradually this
was overcome.
zz many
of the adaptations and those of most significance
are strategic in nature and affect the space planning
and structure of the building. As such the climate related
risks need to be identified and analysed at an early stage
in the project
zz ultimately
the implementation of adaptation measures
will impact upon costs. A building that is inherently
flexible and “loose fit”, and has good passive design
features, is likely to be easier and less costly to adapt
over its lifetime.
zz based
on the experience of the team the following
design strategy could be adopted for other buildings:
{z
measures that required structural alteration were
recommended to be undertaken immediately
irrespective of their actual required implementation
time
D4FC Factsheet 6
3