Low Carbon Buildings and Sustainability

Low Carbon Buildings and Sustainability
By John Bradley & Dr David Johnston – licensed under the Creative Commons Attribution – Non-Commercial – Share Alike License

ENVIRONMENTAL SCIENCE & SERVICES LEVEL 1
Energy resources and fuels CHP & District Heating John Bradley and Dr David Johnston

Objectives and Content
Understand the difference between renewable and non-renewable energy sources Be aware of the energy and CO2 emissions attributable to domestic buildings Define what is meant by a District Heating system and a Combined Heat and Power (CHP) system Identify a number of different types of these systems Be aware of issues which relate to the integration of CHP into buildings Identify the advantages of district heating and CHP Content Energy supply Domestic energy use Low and zero carbon (LZC) energy generation technologies District Heating

Government targets for CO2 emissions to 2050
Introduction UK has recently adopted an ambitious 80% reduction target in CO2 emissions by 2050 in an effort to combat climate change (HM Government, 2008). Emissions associated with the domestic sector, primarily from electricity use and heat generation in homes, account for 27% of UK emissions (DEFRA, 2008), and will have to be dramatically reduced, to virtually nothing by 2050 Climate Change Act 2008 Government targets for CO2 emissions to 2050 2050 [Source: DECC, 2009]

Introduction Studies (ECI, 2005) suggest extensive refurbishment of the existing housing stock and more thermally efficient building fabric in new-build will not be enough to achieve these targets, and that use of low or zero carbon (LZC) energy is essential. This will require a decarbonised electricity grid, and onsite LZC generation of electricity and heat (microgeneration). Such technologies include: renewable electricity generation from solar photovoltaics or small wind turbines; renewable heat from solar water heating, wood burners and other biomass boilers; and low carbon technologies such as heat pumps and combined heat and power (CHP) generators. District or community heating schemes are one way in which CHP can be used to deliver energy efficiently, and with reduced emissions if using biomass as a fuel. This lecture looks at the different types of energy resources and the way in which energy is supplied to the domestic sector. It then examines the way energy is used in dwellings, LZC technologies and the contribution they can make to reducing carbon emissions from buildings.

ENERGY SUPPLY

Energy resources There are five ultimate sources of useful energy:
1. The sun 2. The motion and gravitational potential of the sun, moon and earth 3. Geothermal energy from cooling, chemical reactions, and radioactive decay in the earth 4. Nuclear reactions on the earth 5. Chemical reactions from mineral resources These five energy sources can be split into two main categories: Non-renewable energy - energy obtained from static stores of energy that remain bound unless released by human interaction, e.g., nuclear fuels, fossil fuels - oil, coal, natural gas. Renewable energy - energy obtained from the continuing or repetitive currents of energy occurring in the natural environment, e.g., solar, wind, tidal, biomass, geothermal.

Fossil fuels: Carbon intensities
The majority of the electricity and heat that we use comes from fossil fuels. Burning these fuels liberates their carbon content and this leads to CO2 emissions. In 2008, UK emissions were 532 MtCOe. Electricity generation is responsible for the production of about a third of the total. The amount of carbon associated with each of the main energy carriers varies widely: Carbon intensity of different fuels kg(CO2)/kWh Where a building relies on conventional forms of energy, total CO2 emissions are likely to be minimised if gas is used to provide the space and water heating. Using electricity is likely to result in substantially higher CO2 emissions. Delivered fuel CO2 emissions factor (kgCO2/kWh) Natural gas 0.194 Oil 0.265 Coal 0.291 Electricity 0.568 [Source: Approved Document L2A]

Electricity generation efficiencies
The efficiency of electricity generation depends on the mix of generating plant used. Plant Efficiency Conventional coal-fired power station 38% 1st generation Combined Cycle Gas Turbine (CCGT) 45% Advanced CCGTs % Average UK efficiency 40% Transport and distribution grid losses account for a further 9% of the energy supplied to the grid. A coal-fired power station will deliver about 35 units of energy to the final consumer for every 100 units of fuel input.

Electricity generation carbon intensity
The carbon intensity of electricity has fallen by 50% since 1970 as a result of decreasing reliance on coal-fired generating stations. [Source: DBERR, 2008] 10

Decarbonisation of electricity generation
A major plank of the Government’s strategy to reduce greenhouse gas emissions by 80% by 2050, set out in The UK Low Carbon Transition Plan, is to decarbonise the supply of electricity by increasing the share of renewables, increasing nuclear capacity and using clean coal technology: Renewables Large scale wind Microgeneration Small scale wind Photovoltaics Nuclear 2008 White Paper on Nuclear Power: nuclear power is low carbon, affordable, dependable, safe and capable of increasing diversity of energy supply Clean coal (CCS) Carbon Capture and Storage (CCS) – has the potential to reduce emissions from fossil fuel power stations by up to 90%

Decarbonisation of electricity generation
According to The UK Low Carbon Transition Plan, by 2020 the carbon intensity of electricity generation will have declined significantly as a result of the higher proportion of renewable energy used in generation. By 2050, it will have reduced even further, as a result of nuclear power stations coming on stream and the use of clean coal technologies.

Renewable energy in electricity generation
Renewable energy accounted for 5.5% of electricity generation in 2008 Increased significantly since 2002 when Government introduced the Renewables Obligation (RO): requires all licensed electricity suppliers to supply a specified and growing proportion of their electricity from renewable sources, and provides financial incentives to do so. Biofuels account for over 80% of renewable energy sources, wind about 10%. [Source: DBERR, 2008] 13

Renewable energy in electricity generation
The UK Renewable Energy Strategy (Cm 7876, 2009) commits the UK to produce 15% of its energy from renewable sources by 2020 (currently 2.3%) and 30% of its electricity from renewable sources by 2020 (currently 5.5%). These are legally binding targets. Wind The growth in renewable electricity generation will come from onshore and offshore wind and from small scale renewable technologies (small scale wind and photovoltaics)

Electricity generation and sector usage
The chart below shows that the domestic sector consumes about a third of all the electricity consumed in the UK Fuels used for electricity generation and sector usage of electricity Mtoe, 2006 [Source DBERR a, 2007]

DOMESTIC ENERGY USE

Domestic energy use by fuel
Electricity accounts for 20% but gas accounts for almost three quarters of the fuel used in the domestic sector.

Energy use in the domestic sector
Energy is delivered to the domestic sector to satisfy 4 categories of demand: Space heating, Water heating, Cooking, Lights and appliances The chart below shows the proportion of energy consumed in each category of demand

Trends in domestic sector energy use
Energy use for heating has continued to grow (because of increased ownership of central heating and higher controlled internal temperatures) Use of hot water has increased significantly (as a result of changing lifestyles) Electrical use for lights and appliances has more than doubled since 1970

Domestic sector carbon emissions
UK produced 542 million tonnes of CO2 emissions (MtC02) in Emissions from the domestic building stock were responsible for 142 MtC02; 27% of the total. Carbon emissions are 9% lower than in 1990. Space and water heating is responsible for 73% of domestic emissions. Over 80% of heating systems in UK are fuelled by gas.

Low and zero carbon (LZC) energy generation technologies

Types of technology Low or zero carbon energy (LZC) is the term which is applied to renewable sources of energy and also to technologies which are either significantly more efficient than traditional solutions or which emit less carbon in providing heating, cooling or power (CIBSE, 2006) A number of factors influence integration of these technologies into buildings: Almost all buildings in UK are connected to the national electricity grid, and the majority of buildings (about 80% of dwellings) have natural gas. Costs associated with providing and maintaining these connections are small, for majority of buildings. Providing renewable energy systems which have a reliability of supply which is equivalent to that of the electricity and gas network would be technically difficult to achieve, and expensive. Providing buildings which rely totally on renewable energy systems requires a re-evaluation of the building envelope, as well as all of the energy-using systems contained within the building, e.g., space and water heating systems, cooking systems, cooling systems, lights and appliances. Therefore, the aim should not be to completely replace non-renewable energy systems with renewable energy systems, but to incorporate renewable energy systems where possible, in order to reduce the consumption of fossil fuels.

LZC energy technologies: policy drivers
In 2003 Merton became the first local authority in the UK to include a policy in its Unitary Development Plan that requires new developments to generate at least 10% of their energy needs from renewable energy. This is the so-called Merton Rule. The Merton Rule has been adopted by many local planning authorities Planning Policy Statement PPS22: Renewable energy requires planning authorities and developers to consider opportunities for including renewable energy in all new developments. The Code for Sustainable Homes will require all new homes to be zero carbon by 2016, which will require on-site renewable energy generation Microgeneration is small-scale production of heat and/or electricity from a low carbon source. Aim of Government’s Microgeneration Strategy, is to ‘create conditions under which microgeneration becomes a realistic alternative or supplementary energy generation source for the householder, the community and small business’ (DTI, 2006). According to a study by the Energy Saving Trust, microgeneration could meet 30–40% of UK’s current electricity demand by 2050

LZC energy technologies: penetration
There are few LZC installations in the UK currently: a total of 107,200 in 2005, including 25,000 households with community-scale CHP. Although the figures are for both the domestic and non-domestic sectors, nearly all of them are installed on homes - ie only four out of every 1000 homes have any LZC energy. The majority (73%) of these are solar water heating systems. Very little electricity is generated from existing LZC installations. Most photovoltaic and micro-wind installations have been grant aided. Advancing from the small handful of zero carbon homes currently being built to 240,000 homes a year within nine years will challenge everyone connected with the industry, including house builders themselves, product manufacturers, energy suppliers, designers, surveyors, planners, insurers, regulators and house buyers themselves. [Calcutt, 2007] The Low Carbon Buildings Programme (LCBP) launched in April 2006, giving grants to a variety of microgeneration installations in homes, public buildings and businesses. The total number of approved applications for installations using LCBP grants in the first two years was 5,595, of which 3,339 were solar thermal.

LZC technology classification
The LZC technologies can be classified according to whether they produce electricity, heat or both heat and electricity. Heat only Heat and electricity Electricity only Low carbon Heat pumps Gas fired Combined Heat and Power (CHP) in community heating Gas fired micro-CHP Zero carbon Solar hot water Biomass stove/boiler Waste/biomass CHP in community heating Biomass in micro-CHP Photovoltaics Wind

LZC (renewable) electricity
There are two main renewable technologies that produce electricity: Wind turbines vary in design, although the most common ones use three blades, mounted on a horizontal axis, which drive an electricity generator. There have been significant technical advances over recent years. One kilowatt units are now available for household installation, while the largest turbines can have a capacity of up to five megawatts. Solar photovoltaics (PV), generates electricity from sunlight using roof-top panels or tiles. The panels usually contain two or more layers of silicon, which produce an electrical charge when exposed to light. Solar photovoltaics are examined in a later lecture, here a brief introduction is given to wind turbines.

Wind turbines Wind power is potentially the UK’s most cost-effective renewable resource. The UK has an abundance of good-quality wind resource and large-scale wind power is the UK’s preferred renewables option. Wind turbines convert the kinetic energy of the wind that passes through the swept area of the rotor into electrical energy by means of a rotor, a mechanical drive train (usually including a gearbox) and an electrical generator, mounted on a tower. The economics of wind power are driven by: Wind speed: an increase in wind speed results in a greater than proportional change in rated power. Rated power is proportional to the cube of the wind speed. Rotor diameter: an increase in rotor diameter results in a greater than proportional change in rated power A 1MW turbine can provide enough power for 640 homes

Wind turbines The economics favour large scale wind generation.
Small 600W wind turbine costs about £388/t of carbon saved Large 2MW wind turbine costs about £54/t of carbon saved However, smaller scale generation (at the level of a housing development, industrial/commercial buildings) could make a marginal contribution where the location is favourable. The following location constraints need to be considered in the impact on the built environment: Grid connection is necessary to cope with peak demands and periods of intermittent supply caused by calm conditions Wind in urban areas or around buildings is often of poor quality: unpredictable with significant disturbance Average wind speeds are likely to be greater in rural and outer suburban areas but obstructions such as trees can reduce wind speeds and cause turbulence Planning consent is required (seldom classed as ‘permitted development’) and issues arise such as noise, vibration and visual intrusion The taller the mast, the better: near the ground, friction effects slow the wind As a result of unfavourable wind quality and occurrence and unfavourable economics it is unlikely that wind turbines installed on individual dwellings will be a realistic and viable option.

Wind turbines The Energy Saving Trust's field trial of domestic wind turbines concluded that: Wind turbines do work but only when installed properly in an appropriate location. There is the potential for delivering nearly 2 million tonnes of CO2 savings from domestic small scale wind turbines in the UK. This is equivalent to the annual emissions of approximately 350,000 homes. There is a potential to generate up to 3,500GWh electricity per annum from domestic small-scale wind turbines in the UK.

Financial incentives for LZC electricity
Earlier this month (Feb 2010) Government launched Feed-in tariffs for small scale low carbon electricity generation This “clean energy cashback” will allow many people to invest in small scale low carbon electricity, in return for a guaranteed payment for the electricity they generate. It is expected that by 2020 the scheme will support over 750,000 small scale low carbon electricity installations and will have saved 7 million tonnes of CO2. The specified maximum capacity for the scheme will be set at 5MW. It will support new anaerobic digestion, hydro, solar photovoltaic (PV) and wind projects up to that 5MW limit (and a number of micro-CHP installations), with differing generation tariffs proposed for different scales of each of those technologies.

Feed-in tariffs: the economics
In this example, the site generates (G) 2,000kWh per annum (using a retrofitted <4kW solar PV panel) . It exports (E) 50% of its generation to the local electricity network when the household does not use it. The other 50% is used on-site (O). The household uses (U) a total of 4,500 kWh pa, therefore will need to import (I) 3,500 kWh from its electricity supplier. The household will receive a payment of £856 pa (generation tariff payment of 2,000 kWh x 41.3 p/kWh = £826, plus export tariff payment of 1,000kWh x 3p/kWh = £30). It also benefits from the 1,000 kWh it generates and uses on-site as that will offset 1,000 kWh it would otherwise have had to buy from the electricity supplier. Assuming an import price of 13 p/kWh this would be a saving of £130 (1,000 kWh x 13 p/kWh).

LZC heat There are three main LZC technologies for producing heat:
Solar water heating systems use flat plate or airtight (evacuated) tubes, mounted on south facing roofs using solar radiation to heat water. Heat pumps capture thermal energy stored in the ground, water or air to supply hot water for heating purposes. Ground source heat pumps (GSHPs) use the heat stored in the ground to heat fluid circulating through pipes in the ground: a heat exchanger extracts the heat and then a compression cycle (similar to that used by refrigerators) raises the temperature to, typically, supply hot water for heating purposes. GSHPs are not carbon neutral as they require electricity for the pump and compressor. However, up to five units of heat can be provided for one unit of electrical energy used Space or water heating can be generated from biomass stoves or boilers, which burn wood or other fuels such as energy crops (eg, willow or miscanthus). Both solar water heating and heat pumps will be covered in later lectures. Biomass stoves/boilers are briefly covered next.

Biomass boiler or stove
An ordinary wet central heating system can be based around a boiler that burns wood chips or pellets. As supplementary heating, or in very energy efficient homes, a single woodstove can be used. Both systems require on-site storage of the biomass, and a boiler requires an automatic-feed mechanism, so this is best if part of a community CHP scheme. The opportunities for the penetration of biomass boilers at individual household level are limited: Most suitable in areas where biomass is readily available, such as for rural or suburban homes. Domestic biomass boilers require more room than standard boilers and are unlikely to fit into small properties. Exhaust gases require a flue vent that rises above the roofline of the building; planning permission may be required Energy density of biomass is low: wood 4kWh/kg whereas biomass is 12kWh/kg, therefore greater mass and storage is needed Boiler capital costs 4-5 times that of gas, operating costs higher Output sensitive to moisture content of fuel Biomass boiler

Renewable Heat Incentive
Government is proposing to introduce, from April 2011, a Renewable Heat Incentive (RHI) to provide financial support to increase significantly the level of renewable heat generation Heating accounts for approximately half of the UK’s CO2 emissions and more than half of average domestic energy bills. Currently, only 1% of our heating comes from renewable sources. The RHI scheme will support a range of technologies, including air, water and ground-source heat pumps (and other geothermal energy), solar thermal, biomass boilers, and renewable combined heat and power Tariff levels are proposed to provide a rate of return of 12% on the additional capital cost of renewables, with a lower rate of return of 6% given to solar thermal.

LZC heat and electricity
Both heat and power can be generated together efficiently using Combined Heat and Power (CHP) systems, also known as cogeneration. CHP involves generating electricity on-site and using the heat that is a by-product of the generation process. For a wide range of buildings, CHP can offer an economical method of providing heat and power which is less environmentally harmful than conventional methods. These systems use either natural gas or biomass as a fuel to provide electricity and heating simultaneously. Whereas conventional large power stations emit heat into the environment as a by-product of electricity generation, CHP systems capture this thermal energy to use locally. Typical efficiency is around 65–85%, which is much greater than typical power stations. Also, because he electricity is generated on-site, the transmission losses associated with centralised generation do not occur. Depending on the size and location of the plant, this may be purely for domestic use, in the case of micro-CHP, or to provide community or district heating through a heat distribution network

Combined Heat and Power (CHP)
Each kWh of electricity supplied from the average fossil fuel power station results in the emission of around half a kg of CO2. Typically, gas-fired boilers emit around one fifth of a kg of CO2 per unit of heat generated. CHP has a lower carbon intensity of heat and power production than these separate sources and this can result in around a 30% reduction in emissions of CO2. The environmental benefits can be seen in the diagrams below. CHP produces far less CO2 emissions with a reduced primary energy input than conventional energy supply systems. Conventional energy supply Energy supply using CHP [Source: CIBSE (2009) ]

CHP technology The basic components of a CHP system are:
An engine to drive the generator Fuel system Generator to produce electricity Heat recovery system to recover useful heat from the engine Cooling system Combustion and ventilation air systems Control system Enclosure Typical small scale CHP system [Source: Carbon Trust, 2004]

CHP applications CHP can be implemented at a wide range of scales:
Large-scale CHP - generally above 1MWe electrical and can range from large diesel engines to gas and steam turbines. Tend to be non-standard, with each site having a tailor made design. Suitable for airports, large hospitals and large district heating systems. Small-scale CHP - most building installations use small-scale packaged units fuelled by natural gas, with electrical outputs of up to 1MWe. All of the components come assembled ready for connection to the building’s central heating and electrical distribution systems. Micro-CHP units - several boiler manufacturers have produced units that are capable of serving a single dwelling, are no bigger than conventional boilers, and if integrated correctly, are capable of replacing existing gas-fired heating boilers The main applications for CHP in buildings are those sites where there is simultaneous demand for heat and electricity for extended periods. Three sectors have proven to be particularly suitable: Hotels Hospitals Leisure facilities with swimming pools Universities

CHP in buildings Number and capacity of CHP schemes installed in buildings, by sector, 2008 [Source: DUKES, 2009]

Examples of small scale CHP units
CHP examples Examples of small scale CHP units

CHP capacity In 2008, just over 7% of the total electricity generated in the UK came from CHP plants, representing 5.5 GWe capacity. In 1999 the Government set a target of 10 GW installed capacity by 2010 and developed a strategy and incentives in order to achieve this. Target not met primarily as a result of unfavourable price differentials for gas and electricity (‘spark spread’). New projection is 6.2 GW installed capacity by 2010, rising to 15.5 GW by 2020. [Source: DBERR, 2007] 41

Integration of CHP into buildings
CHP installations cannot be considered in isolation, but must be correctly integrated with any other energy systems on site. A building’s heat and power requirements will not be exactly mirrored by the output of the CHP plant, and there will generally be a need for ‘top-up’ heat and power unless there is excess capacity that can be exported. CHP does not necessarily replace conventional boilers, although it often replaces boiler capacity. To maximise the benefits, a CHP installation will usually be designed to meet the base heat load. This ensures that the plant operates for as many hours as possible. Additional boiler capacity is required to meet the peak heat demands. Sizing of CHP plant should only be done after consideration of energy efficient measures as these may have a significant effect on the site demand profiles. Future changes in energy requirements should also be anticipated to avoid the unit becoming oversized.

Micro-CHP CHP for small buildings is available as the result of development of small gas (or oil)-fired engines. Two types available: Internal combustion engines: supply electrical output of 5kW+ and heat output of10kW+. Suitable for groups of flats, residential homes, small commercial premises. Need to operate for 10hrs+ a day to be economic. Stirling engines: electrical output of 1kW+ and power to heat ratio of between 1:6 and 1:3, most suitable for larger new houses, older houses with high heat demand and smaller commercial premises. The Whispergen 0.8kWe Stirling engine system is one micro-CHP unit currently marketed in UK domestic sector Whispergen micro-CHP unit in a kitchen

Micro-CHP: carbon savings
Carbon saving depends on Amount of electricity generated Carbon intensity of grid electricity displaced In example below, CHP unit produces same heat output as a conventional boiler, (at a lower efficiency) but the CHP unit also produces 1,780kWh of electricity. The net effect is to save 370kgCO2 pa However, if there is a low heat demand, CHP could produce more, not less carbon, as there would be little electricity generated to offset the lower thermal efficiency of the CHP unit. Example of how a Micro-CHP system can save carbon * To power controller, pump and fan * [Source: Carbon Trust, 2007] A carbon emissions factor of 0.568kgCO2/kWh is assumed for locally generated electricity from Micro-CHP

Micro-CHP: power to heat ratio
The power-to-heat ratio is important when assessing the potential end uses and carbon savings for different units. The higher the power-to-heat ratio the higher the proportion of electrical output and therefore the greater the potential carbon savings for a given energy input. Stirling engine Micro-CHP systems typically have power to heat ratios in the range of 1:10 to 1:4, so they are suited to operating in a ‘heat-led’ fashion in domestic environments, sized to meet the full heat demand. They are also usually sized to generate electricity at a level that ensures that a reasonable proportion is used within the household rather than exported to the grid. Theoretical carbon savings for different power-to-heat ratios [Source: Carbon Trust, 2007]

Micro-CHP: evaluation
Field trials carried out by the Carbon Trust suggest that: Carbon and cost savings from Micro-CHP are higher for buildings where they can operate for long and consistent heating periods In small commercial applications, Micro-CHP systems can provide carbon savings of 15% to 20% Micro-CHP systems have the potential to provide carbon savings of 5% to 10% for older, larger houses with high and consistent heat demands For smaller and newer houses, the typical carbon savings will be less than 5% Range of carbon savings expected for domestic and commercial Micro-CHP* older, larger houses [Source: Carbon Trust, 2007] *relative to a typical A-rated condensing system boiler and based on carbon emissions factor of 0.568kgCO2/kWh for displaced electricity

Micro-CHP: dis/advantages
Combustion efficiencies of up to 95% Relatively low cost and simple installation Could directly replace existing central heating boilers Heating operation coincides with peak demand periods for electricity Ability to export excess electricity to National Grid Disadvantages Inherent carbon emissions Seasonal patterns of electricity generation, restricted to heating season Continuing reliance on grid electricity to make up shortfalls Viability affected by fluctuating price of grid-generated electricity Only viable in dwellings with higher thermal requirements (large or less well insulated)

Renewable energy in buildings: early examples
The Beddington Zero Energy Development (BedZed), Sutton, London A 130kWe wood-fuelled combined heat and power (CHP) unit 777m2 of photovoltaic panels mounted on the south-facing elevations of the buildings are used to power up to 40 electric vehicles. The Hockerton Houses, Southwell, Nottinghamshire The Autonomous Urban House, Southwell, Nottinghamshire Two grid-linked wind turbines (11kW rating) - producing 9000kWh annually. A 7.65kW grid-linked roof-mounted photovoltaic array - producing 5700kWh annually. Building integrated 2.2kW grid-connected PV system sited on a pergola in the garden

District heating Community or district heating, where buildings are collectively served by the same central heating plant, has been widely adopted in Europe. In particular Denmark where it is now the heating technology of the first rather than last choice. In UK, less than 1% of homers are served by Community heating Community heating is not new to UK: Manchester, Glasgow, Dundee and Chesterfield had district heating systems in the early 1900s. Hit a peak in the late 1960s early 1970s in the UK, when over 500 district and group heating systems were installed, serving in excess of 400,000 users. In the 1980s, development virtually ceased due to poor technical performance of earlier schemes. However, some UK cities do possess substantial community heating networks, notably Sheffield, Nottingham, Southampton and Birmingham

District heating However, community heating is now seen as a part of the solution for delivering sustainable communities: Significant carbon savings are available if heat is supplied from renewable energy sources such as biomass or geothermal heat, or using the waste heat from power generation (CHP). Introduction of Code for Sustainable Homes means that low carbon solutions, such as community heating, are a key consideration for new developments. Community/district heating is most appropriate in the following circumstances: Dense housing, flats in particular offer high heat demand density. The role of CHP is particularly important with flats, as these have insufficient roof or garden space for the solar technologies or heat pumps, lack the storage for individual biomass burners and are often not permitted to have individual gas boilers, for safety reasons. Off-gas communities, where oil, solid fuel heating, or electricity is displaced In new and dense build, typically over 50 dwellings per hectare where electrical and gas network infrastructure is not already installed. Cost of heating pipes is about 25% of the full installation, remaining costs being for trenching etc. So economies obtained by installing all services simultaneously.

District heating: scheme elements
Pipes A network of pre-insulated pipes carries the heated water from the plant in the energy centre to each connected building and/or dwelling. Heat losses are minimised by insulating the pipes, operation at low temperature and effective detection and repair of leaks The energy centre The plant room or energy centre typically has an arrangement of in-line boilers. The lead boiler provides for summer base load – generally domestic hot water. Most modern schemes will include a CHP engine acting as the lead boiler. As demand for heat rises, other boilers will come on-line as required. Consumer interface Within the dwelling is an Hydraulic Interface Unit (HIU) which takes the heat from the main heating network and transfers it to the dwelling central heating system and domestic hot water supply through a plate heat exchanger.

Types of district heating system
The term ‘district’ is a general term and covers the following types of systems: Block heating - serving a single building which contains a number of individual units, i.e. flats, shopping centre. Group heating - serving a number of similar buildings, i.e. industrial units, industrial estate, hospital, university. District / community heating - serving a specified district, area or community which contains a number of different buildings with different building usage, i.e. a town or a city. District heating can be implemented at any scale, from a few dozen dwellings to a whole city. A site-wide scheme A city-wide scheme

District heating: sources of heat
District heating systems can be very flexible, because they are based on the distribution of hot water. Almost any source of heat can be used, including: Refuse incineration. Industrial waste heat. Biomass. Solar energy. In UK, an important source of waste heat is from electricity generation. Average efficiency of electricity generation in the UK is around 40%, with the remainder of the energy from the fuel being rejected as waste heat. This waste heat is rejected at too low a temperature (25 to 30OC) to be used for most practical heating purposes, but contains enough energy to heat every home in Britain. If the low pressure section of power stations steam turbines is modified, heat can be rejected at temperatures high enough to heat buildings. Such power stations are referred to as Combined Heat and Power (CHP) stations. The cost of the higher temperature is a modest reduction in the efficiency of electricity generation. For example, London Thames Gateway Heat Network, which will capture heat from Barking Power Station and pump low carbon heat through a district heating network up to 120,000 homes

Comparison with conventional supply system
There are differences for consumers between a dwelling heated conventionally and one heated by community/district heating: Reduced maintenance for the individual heating system: no boiler to safety check and maintain HIU that replaces the boiler is smaller than a traditional wall-hung boiler No hot water storage cylinder and immediately available, unlimited hot water supply (also the case for combi boilers) No gas supply to individual dwellings, thus avoiding the need for external venting as well as potential safety advantages, but cooking requirements would be met by electricity Customer connected to a community heating scheme cannot change supplier in the way that a gas or electricity consumer can switch suppliers Payment made for heat supplied instead of gas consumed. With community heating, an HIU is fitted in each dwelling and the plant itself is located in an energy centre. This means that: Accommodation must be provided onsite for the energy centre: purpose-built or within one of the buildings, eg the basement of a block. If biomass is used then enough space must be allowed for storage/delivery. A chimney stack will be required. A pipe network must be installed in trenches so that a connection can be provided to each building that is to receive the community heating supply. This should be considered alongside the other service connections that will be provided to each dwelling Arrangements must be made for ownership, operation and administration of this local energy supply system.

District heating: benefits
There are benefits nationally: Decarbonising energy supply: heating can be provided using a variety of sources, including low carbon fuels and renewable energy - refuse incineration, industrial waste heat, biomass, solar energy. Less fossil fuel is likely to be used and carbon emissions will therefore be lower Flexibility: changes to the fuel supply can be made without disrupting consumers, to take advantage of new technologies eg fuel cells There are also benefits for the consumer: Heating bills: Customers of modern community heating schemes will generally be paying less for their heat than those with conventional gas boilers, partly because of the use of highly efficient CHP systems and partly because the aggregated demand enables the operator to take advantage of the highly competitive (and hence cheaper) commercial fuel markets in a way the individual householder cannot. Consequently, the heat price can be pitched at a very competitive rate. Safety: As the plant is external, there is no need for external flues from the individual dwellings. Removing the need for gas-fired equipment within dwellings also removes any potential risk of carbon monoxide poisoning or gas explosion. More space: The HIU that interfaces between the primary distribution network and internal central heating systems is smaller than wall-hung boilers. Additionally, there is no need for stored hot water, contributing to space saving within the dwelling.

Advantages of District heating and CHP
The main advantages of District Heating and CHP are: Long term flexibility of energy supply Reduced fossil fuel consumption Reduced carbon emissions Considerable reduction in SO2 emissions if natural gas fired plant is used. Cost savings CHP plant serving Southampton’s district heating scheme

CHP and district heating: examples
The Beddington Zero Energy Development (BedZed), Sutton, London [Source: BedZed, 2002] A 130kWe wood-fuelled CHP unit generates electricity and distributes hot water around the site via a district heating system. Since peak loads have been flattened, the boiler installation normally required by a CHP system for peak backup is avoided. Emergency backup is provided from the electricity grid and by stored hot water from oversized domestic hot water cylinders.

District heating system, Nottingham [Source: BRECSU, 1996] Refurbishment of a district heating system originally installed in 1972. Refurbishment involved improvements to domestic properties on the scheme and improvements to ageing pipework. Heat is obtained from a waste incinerator and a CHP system. Supplies commercial buildings, 3600 council dwellings, around 700 owner occupied dwellings and public sector properties.

Park View, Southampton [Source: BRECSU, 1996] Consists of a 108 1, 2 and 3-bedroomed luxury apartments. It is the first new private housing development of its type in the UK to use district heating. Connected to the Southampton District Energy Scheme, which is linked to a CHP generator. Flats have conventional hot water radiators with thermostats and time controls which are fed direct from the system. Domestic hot water is produced using heat exchangers.

Proposed London Thames Gateway Heat Network Proposal to develop a low-carbon district heating network in Europe’s largest regeneration area. The £150 million project will serve the equivalent of 120,000 homes and other properties, delivering savings of up to 100,000 tonnes of CO2 per year for 40 years. The system will incorporate heat from a number of sources, including waste heat from Barking Power Station and heat generated by Tate & Lyle. Heat will be distributed via an extensive distribution main up to 67km long. The project’s delivery is expected over a three phase period from 2010 to 2019.

LZC technologies: potential
Up to 10 million new homes will be needed by Most built to Zero Carbon standards, requiring LZC technologies as well as highly energy efficient design and construction. The low level of heating required in these new homes means that the focus will be on electricity generation, and hot water. Developers may be forced into uneconomic provision of LZC technologies. For the existing stock, ease of retrofitting will be the key driver. The replacement cycle for boilers and roofs will present opportunities for micro-CHP, solar thermal and photovoltaics (if the economics improve). Appropriateness of LZC technologies New buildings Existing buildings Solar thermal Yes with RHI Photovoltaics Yes, with FITs GSHPs Yes, if heat demand high enough Rarely – too disruptive and need for garden Woodstoves Yes, if space for storing wood Rarely Micro-wind Possibly on a whole development scale Rarely, unless rural and exposed Micro-CHP Yes, but only where heat demand is high enough Yes, particularly in suburban areas CHP (waste/biomass fired) Yes Possibly, in some locations

References BEDZED (2002) Beddington Zero Energy Development. Available from: BOARDMAN, B (2007) HomeTruths: a low-carbon strategy to reduce UK housing emissions by 80% by 2050, Oxford, Environmental Change Institute BRE (2002) Community Heating Serves Luxury Private Apartments - Park View, Southampton. Good Practice Case Study 400, London, The Stationery Office Ltd. BRECSU (1996) Community Heating in Nottingham: An Overview of a Rejuvenated System. Good Practice Case Study 312 London: The Stationery Office Ltd. CALCUTT (2007) The Calcutt Review of Housebuilding Delivery London: Department for Communities and Local Government CHPA (2003) How Does CHP Work? Available from: < CARBON TRUST (2004) GPG 388 Combined Heat and Power for Buildings, London, HMSO CARBON TRUST (2007) Micro-CHP Accelerator London, The Carbon Trust CIBSE (1999) Small-scale Combined Heat and Power for Buildings. CIBSE Applications Manual AM12: 199 London, Chartered Institution of Building Services Engineers. CIBSE (2006) Renewable energy sources for buildings London Chartered Institution of Building Services Engineers. CIBSE (2009) Energy efficient heating London: Chartered Institution of Building Services Engineers. DBERR (2007a) Energy Trends, London, Department for Business, Enterprise and Regulatory Reform

References DBERR (2008) UK Energy in Brief, London, Department for Business, Enterprise and Regulatory Reform DBERR (2008a) Meeting the Energy Challenge: A White Paper on Nuclear Power, London: Department for Business, Enterprise and Regulatory Reform DCLG (2006) Review of Sustainability of Existing Buildings London: DCLG DECC (2009) The UK Low Carbon Transition Plan London: Department of Energy and Climate Change DECC (2009a) Energy Trends London: Department of Energy and Climate Change DECC (2009b) Heat and Energy Saving Strategy Consultation London: Department of Energy and Climate Change DECC (2009c) UK Energy in Brief 2009 London: Department of Energy and Climate Change DECC (2010) Feed-in Tariffs Government’s Response to the Summer 2009 Consultation London: Department of Energy and Climate Change DEFRA (2001) Digest of Environmental Statistics. London: HMSO. DEFRA (2006) Climate Change: The UK Programme 2006 London: HMSO DEFRA (2008) Carbon dioxide emissions by end user:1990–2006 – United Kingdom [Internet] Available from <from (last accessed 24/1/2010) DETR (2000a) Climate Change: The UK Programme - Summary London: HMSO. DTI (2001) Digest of United Kingdom Energy Statistics London: HMSO

References DTI (2006) Microgeneration Strategy London: Department of Trade and Industry ECI (2000) Lower Carbon Futures for European Households. Environmental Change Institute: Oxford, University of Oxford ECI (2005) ECI Research Report 31: the 40% House Environmental Change Institute, Oxford: University of Oxford ECI (2009) Power from the people: Domestic microgeneration and the low carbon buildings programme Environmental Change Institute, Oxford: University of Oxford HM GOVERNMENT(2008) Climate Change Act London: The Stationery Office HM TREASURY (2009) Building a low carbon economy: implementing the Climate Change Act 2008, London, TSO HOCKERTON HOUSING PROJECT (2008) Hockerton Housing Project (HHP). Available from :< NHBC (2009) Community heating and Combined Heat and Power Amersham: NHBC ODPM (2006) Low or Zero Carbon Energy Sources: Strategic Guide, London: RIBA Enterprises The UK Renewable Energy Strategy (CM 7686, 2009) London, TSO Stern, N (2007): ‘The Stern Review: Economics of Climate Change’, Cambridge University Press UTLEY, J.I. and SHORROCK, L. D. (2008) Domestic Energy Fact File. Garston, Watford, Building Research Establishment. VALE, B. and VALE, R. (2000) The New Autonomous House: Design and Planning for Sustainability. London, Thames & Hudson.

Low Carbon Buildings and Sustainability

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Low Carbon Buildings and Sustainability

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