WOODCOTE VALLEY ROAD, PURLEY, CROYDON Mantle
Transcription
WOODCOTE VALLEY ROAD, PURLEY, CROYDON Mantle
WOODCOTE VALLEY ROAD, PURLEY, CROYDON 10% RENEWABLE ENERGY REPORT for Mantle Developments UK Ltd December 2011 Project no. 587 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport WOODCOTE VALLEY ROAD, PURLEY, CROYDON 10% RENEWABLE ENERGY REPORT Mantle Developments UK Ltd DATE REVISION DATE PREPARED BY REVIEWED BY COMMENTS 0 14/12/2011 Max Campbell Mark Heptonstall For Comment 1 20/12/2011 Max Campbell Mark Heptonstall PV modules moved to flat roof 2 21/12/2011 Max Campbell Mark Heptonstall PV modules mounted flat The current report provides a brief overview of the wide range of opportunities for renewable energy and is not intended as detailed design advice. As such data and information should only be treated as INDICATIVE at this stage of the process. Further investigation can be undertaken when more accurate and detailed information is required on specific measures. No part of this document may be reproduced or transmitted in any form or by any means, in whole or in part, without the written permission of C80 Solutions. Whilst C80 Solutions has endeavoured to ensure that all information contained within this document is correct, it cannot be held responsible for any inaccuracies within or problems arising out of the use of this document. C80 Solutions Suite 2 Enterprise House 249 Low Lane Horsforth Leeds LS18 5NY 1 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport E: [email protected] W: www.c80solutions.co.uk Contents Page 1.0 Introduction ......................................................................................................... 4 1.1 About C80 Solutions ......................................................................................................... 4 1.2 Introduction to Development ............................................................................................. 4 1.3 Planning Policy ................................................................................................................. 5 1.4 Methodology..................................................................................................................... 6 2.0 Total Predicted Annual Energy Demand of the Development......................... 7 3.0 Baseline Carbon Emissions of the Development............................................. 9 4.0 Overview of Renewable Technologies ............................................................ 10 4.1 Wind Turbines ................................................................................................................ 10 4.2 Solar Photovoltaics (PV) ................................................................................................. 14 4.3 Solar Thermal ................................................................................................................. 17 4.4 ASHP (Air Source Heat Pump) ....................................................................................... 20 4.5 GSHP (Ground Source Heat Pump)................................................................................ 22 4.6 Biomass Boiler ............................................................................................................... 25 5.0 Feasibility Study of Renewable Technologies ............................................... 28 6.0 System Size to Provide 10% CO2 Reduction.................................................. 31 2 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport Tables Table Description Page 1 Part L compliant construction specifications 7 2 Baseline Predicated Annual Energy Demand 8 3 Baseline Associated Carbon Emissions of the Development 9 4 Feasibility Study of Renewable Technologies 29 5 SAP Results and Amount of PV per Plot 31 6 Carbon Emissions of the Development with 6.5kWp Solar PV 33 7 Percentage Reduction in Carbon Emissions from 6.5 kWp Solar PV 33 Figures Figure Description Page 1 Proposed Site Plan 5 2 Sectional diagrams of horizontal axis and vertical axis wind turbines 10 3 Example of a mast mounted wind turbine 11 4 Example of a roof mounted wind turbine 11 5 A solar PV Module 14 6 Solar PV array 14 7 Reduction in solar PV panel efficiency with angle and orientation 15 8 Solar irradiation map of the UK 15 9 Simple solar thermal installation diagram 17 10 Flat plate collectors 17 11 Evacuated tube collectors 17 12 ASHP 20 13 ASHP diagram 20 14 A ground source heat pump 22 15 Slinkies (coiled pipes) in a trench 22 16 Biomass boiler 25 17 Wood pellets 25 18 33 20 Proposed South West Elevation showing possible location of 14 PV panels Proposed Roof Plan showing possible location of 12 PV panels mounted at 30 degrees on flat roof Estimation of Solar PV System Performance 21 25 Year Feed-in Tariff Financial Calculation 36 19 34 35 3 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport 1.0 Introduction 1.1 About C80 Solutions C80 Solutions are independent Sustainability and Energy Consultants providing carbon reduction solutions to help the UK achieve its carbon emission reduction target of 80% by 2050 - as set out in the Government's Climate Change Act 2008. Our range of affordable but comprehensive solutions for the residential market are broken down into two sectors; i) Compliance and ii) Consultancy. Compliance: Our Residential Compliance services include; Code for Sustainable Homes Assessments, SAP Calculations, On Construction Energy Performance Certificates, Water Efficiency Calculations and Air Tightness Testing. Consultancy: Our experience and exposure to residential compliance combined with previous employment and IEMA accredited training means we have built up a vast amount of experience and knowledge which enables us to provide our clients with invaluable advice. Our Residential Consultancy services include; Renewable Energy Feasibility Studies, Energy Statements, Code for Sustainable Homes ENE7 Reports, Part L Compliance Reports and Feed-in Tariff reports. 1.2 Introduction to Development C80 Solutions have been instructed by Mantle Developments to prepare a renewable energy report for the proposed residential development on Woodcote Valley Road, Purley, Croydon. The report will demonstrate how the predicted CO2 emissions from the development will be reduced by at least 10% through the use of on-site renewable energy technology. The site is located in south London in the London Borough of Croydon. The site’s existing use class is residential and it has some mature trees located on the site boundaries. The proposed scheme is for 11 new build flats in a single 3 storey block built to achieve code for sustainable homes level 4. The site also contains associated parking, cycle storage and amenity space for the residents. The proposed site plan for the development can be seen below in figure 1. 4 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport Figure 1: Proposed Site Plan 1.3 Planning Policy Policy EP16 of the Croydon Unitary Development Plan states: “The Council will encourage all developments to incorporate renewable energy, but will require proposals for non-residential developments exceeding 1,000 square metres gross floorspace, and new residential developments comprising 10 or more units, whether new build or conversion, to incorporate renewable energy production equipment to off-set at least 10% of predicted carbon emissions, except where: a) the technology would be inappropriate; b) it would have an adverse visual or amenity impact that would clearly outweigh the benefits of the technology; and c) renewable energy cannot be incorporated to achieve the full 10%. Where the 10% requirement cannot be achieved on major developments, a planning obligation will be sought to secure savings through the implementation of other local 5 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport renewable energy schemes.” The reason for this condition is in the interests of sustainability and to minimize the impact of the development on the effects of climate change. 1.4 Methodology The methodology that has been applied in this report is as follows: 1. Prepare baseline SAP 2009 Calculations for the 11 dwellings based on the Part L 2010 compliant construction specification designed for the development. These baseline calculations will not contain any form of renewable technology. 2. From the Part L compliant Baseline SAP calculations, the predicted energy demand for the development in kWh/year can be established. Standard carbon emission factors from SAP 2009 will be applied to this figure to ascertain the predicted CO2 emissions in kgCO2/year for the whole site before any renewable technology is incorporated. 3. Multiplying the site wide predicted CO2 emissions figure by 10% will provide the CO2 reduction target required from renewable technology. This target will be above and beyond what is required to comply with Part L of Building Regulations since the Baseline SAP calculations will already be complaint with Part L. 4. Carry out a renewable energy feasibility study to ascertain which LZC technologies would be suitable for the development. A particular technology will be chosen by the developer after presenting the suitable options. 5. The last stage is to establish the sizing of suitable renewable technologies to meet the 10% CO2 emission reduction target. As the new build properties must achieve code for sustainable homes level 4, a dwelling emission rate of 25% less than Part L 2010 is a mandatory requirement. In this regard, an amount of renewable technology will be entered into the Baseline SAP calculations until the 25% emissions target has been achieved. A check will then be carried out to ensure that this amount of technology provides the 10% CO2 reduction needed to satisfy EP16. 6 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport 2.0 Total Predicted Annual Energy Demand of the Development Baseline SAP 2009 calculations were prepared based on the construction specification shown in table 1 below. Aspect Fabric U-values 2 W/m K Roof 0.13 Walls external 0.26 Ground Floor 0.15 Windows 1.70 Doors 1.80 Party Walls 0.00 Thermal Bridging Ventilation New Build Airtightness m3/(hr.m2) Mechanical Ventilation Boiler Heating Controls Water Heating Renewables / LZC Low energy lighting Table 1: Part L compliant construction specifications 0.04 (ECDs) 5 Mechanical Ventilation with Heat Recovery 90% Efficiency Gas condensing boiler, boiler interlock. Load Compensator Time and temperature zone control 110L cylinder None 100% Based on using the specification outlined in table 1 above, this would create a total predicted energy demand for the development of 54,578 kWh/year. The breakdown of this predicted energy demand can be seen in table 2 below. The figures quoted have been derived from the Design Stage SAP 2009 Calculations for the development. 7 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport Predicted Annual Energy Requirements: Space Heating Water Heating Lighting, Pumps, Fans Total Predicted Energy Requirement (kWh/yr) Plot No. Units Gas Gas Electric Plot 1 Plot 2 Plot 3 Plot 4 Plot 5 Plot 6 Plot 7 Plot 8 Plot 9 Plot 10 Plot 11 1 1 1 1 1 1 1 1 1 1 1 kWh/yr kWh/yr kWh/yr kWh/yr kWh/yr kWh/yr kWh/yr kWh/yr kWh/yr kWh/yr kWh/yr 2,339 2,402 2,167 1,369 1,714 1,499 1,600 862 1,826 2,416 2,050 2,573 2,594 2,514 2,286 2,562 2,483 2,530 2,539 2,398 2,457 2,521 673 720 630 504 655 601 630 641 574 593 659 5,585 5,716 5,310 4,158 4,931 4,583 4,760 4,042 4,797 5,466 5,230 20,243 27,455 6,880 54,579 Site Total 11 Table 2: Baseline Predicated Annual Energy Demand 8 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport 3.0 Baseline Carbon Emissions of the Development Total Energy Demand (kWh/yr) Associated Total CO2 (kgCO2/yr) Space Heating 20,243 4,008 Water Heating 27,455 5,436 Fixed Electrical 6,880 3,556 Site Total 54,579 13,000 Table 3: Baseline Associated Carbon Emissions of the Development Carbon Factors Used (from SAP 2009) Gas = 0.198 kg CO2/kWh Electric = 0.517 kg CO2/kWh In order to satisfy EP16, the development needs to reduce predicted site wide CO2 emissions by 10% from on-site renewable energy sources. Therefore, since the development’s predicted CO2 emissions is 13,000 kgCO2/yr, this would equate to a reduction of 1,300 kgCO2/yr. In other words, providing the total site emissions comes to equal to or less than 11,700 kgCO2/yr (13,000 – 1,300) when renewable technology is added to the SAP calculations, this would prove that the 10% reduction target has been met and policy EP16 has been complied with. 9 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport 4.0 Overview of Renewable Technologies 4.1 Wind Turbines General Description Wind turbines convert the kinetic energy from the wind into mechanical energy which is then used to drive a generator that converts this energy into electricity. When the wind blows the large aerodynamic blades are forced round, driving a turbine which generates the electricity. The stronger the wind, the faster the blades turn and the more electricity is produced. In the UK we have approximately 40% of Europe’s total wind energy resource, but this resource is still largely untapped with only 2.5% (July 2010) of the UK’s electricity production coming from wind energy. Wind turbines can be either horizontal axis or vertical axis turbines. Horizontal axis turbines are the more familiar windmill type where the blades rotate in a vertical plane about a horizontal axis and the turbine is dynamically rotated on its tower to face the wind. Most domestic scale wind turbines are horizontal axis devices. Vertical axis turbines do not need orientation into the wind, although some of the earlier versions required a power source to start rotating due to their high torque. More recent models have helical blades that have low torque and do not require external power to start the blade rotating. Vertical axis turbines are more suited to small scale applications due to their low environmental impact and no noise. Figure 2: Sectional diagrams of horizontal axis and vertical axis wind turbines 10 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport There are two types of domestic sized wind turbine: Mast mounted: these are free standing and are erected in a suitably exposed position. They are often around 2kW to 6kW in size. The masts are usually located close to the building that will be using the generated electricity. Figure 3: Example of a mast mounted wind turbine Roof mounted: these are smaller than mast mounted systems and can be installed on the roof of a home where there is a suitable wind resource. Often these are around 1kW to 2kW in size. Building mounted turbines are relatively new editions to the renewable energy market and some concerns have been expressed about the performance of these types of systems given the lower wind speeds and increased turbulence in built up areas. One study has shown that in some urban environments micro-wind turbines may never payback their embodied carbon emissions. Figure 4: Example of a roof mounted wind turbine 11 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport Wind turbines can be a grid connected system (connected to the national grid) or an off grid system. Both require an inverter to convert the generated direct current (DC) electricity into alternating current (AC) mains electricity. Off grid systems also require a battery to store any unused or excess generated electricity. With a grid connected system any electricity that is not used at the time of generation is exported and sold to the grid. Please see section 8.6 on Feed-in Tariffs. Suitability – Environment & Building Generally speaking the ideal site is a smooth top hill with a flat, clear exposure, free from excessive turbulence and obstructions such as large trees, houses or other buildings. The electricity generated at any one time by a wind turbine is highly dependent on the speed and direction of the wind. The wind speed itself is dependent on a number of factors, such as location within the UK, height of the turbine above ground level and nearby obstructions. It is recommended to undertake a professional assessment of the local wind speed for a full year at the exact location before proceeding. In practice, this may be difficult, expensive and time consuming to undertake. Therefore it is recommended that if you are considering a domestic building mounted installation, then you only consider a wind turbine under the following circumstances: The local annual average wind speed is 6 m/s or more. There are no significant nearby obstacles such as buildings, trees or hills that are likely to reduce the wind speed or increase turbulence. Building mounted wind turbines require caution due to the loads that are imposed on the building’s structure and the transmission of vibration into the structure. Energy Generated Wind turbines are rated by their power output in kW at a given wind speed. A viable 2.5 kW wind turbine installation should generate around 4000 kWh pa, which is equivalent to an average household’s electricity consumption. However, it does not follow that a 2.5kW installation can supply a house with all its electricity because the peak power demand in many houses exceeds 10kW and there can be prolonged periods of calm when the wind speed is below average. Carbon Savings A viable 2.5 kW wind turbine installation should offset around 2,000kg of CO2. Cost Savings If all the electricity generated is consumed in the household the money saved @ 11.5p/kWh is £460. 12 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport Capital Costs Mast mounted wind turbines are often around 2kW to 6kW and cost around £3000 per kW installed. Roof mounted wind turbines are often around 1kW to 2kW in size and cost around £1800 per kW installed. Typical Payback Generally, investment in a wind turbine should be recouped where there is a minimum average wind speed of 5 m/s. A well-sited, 2.5 kW wind turbine could provide payback within a period of about 15 years. Lifespan Turbines can have a lifespan of up to 20 years. For battery storage systems, typical battery life is around 6-10 years, depending on the type, so batteries may have to be replaced at some point in the system's life. Maintenance Turbines require service checks every few years to ensure they work efficiently. Maintenance of small-scale turbines is generally limited to visual assessments and an annual oil check, which in most cases can be incorporated into a site’s annual maintenance schedule and does not require the turbine installer to be present. Noise Turbines make more noise in higher wind speeds, but because the background noise also increases, they are barely audible. Planning Planning issues such as visual impact, noise and conservation issues have to be considered. System installation normally requires planning permission from the local authority, although it is hoped that, in future, small building-mounted turbines may be granted ‘permitted development’ status. Land Use Roof mounted systems have no additional land use. Mast mounted systems will require adequate land for construction and maintenance purposes. Financial Incentives – FIT or RHI Since wind turbines generate electricity they are viable for feed-in tariffs providing the products and installer used are MCS certified. A dwelling with a 2.5kWp installation will generate around £1,068 revenue a year. The tariffs for wind turbines are fixed for 20 years. 13 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport 4.2 Solar Photovoltaics (PV) General Description The energy in sunlight is converted into electricity by photovoltaic (PV) cells, which are semiconductor devices. Each PV cell is made from one or two layers of semiconducting material, usually silicon. When light shines on the cell it creates an electric field across the layers. The stronger the sunshine, the more electricity is produced. Since individual cells only generate a small amount of electricity, they are usually grouped in rectangular modules that comprise transparent cover, a metal mounting frame and a back plate, thus forming a weatherproof enclosure. Modules are often then grouped into arrays. PV cells can also be moulded into solar slates or solar tiles for integration into roofs. Figure 5: A solar PV Module Figure 6: Solar PV array PV installations are not described in terms of their area but are rated according to their peak power output (kWpeak or kWp). The module areas currently required per kWp output for the different technologies are: monocrystalline = 7 m2 polycrystalline = 10 m2 Suitability – Environment & Building The building roof should have good access to solar radiation and be free from shadowing as this has a detrimental effect on the generation ability of the PV panels. Due to the way in which they are electrically connected, even if one small area of a panel is overshadowed, the efficiency of the panel - and even the PV array - will be significantly reduced, meaning that the output is much lower than predicted. It is essential, therefore, that PV products are mounted away from trees, other roof obstacles and shadows cast by surrounding buildings. Rural and suburban sites are likely to have access to more sunlight for longer periods of the day than inner urban locations where other buildings and trees can cast shadows. 14 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport Ideally, PV panels should be sited on south-facing roofs pitched at 30° to 45° from horizontal to maximize solar gain throughout the year. For flat roofs, angled mounting frame kits are available but care should be taken to ensure one row doesn’t overshadow the row behind. Shallow angle mounting reduces energy capture and increases the risk of dirt accumulation. Figure 7: Reduction in solar PV panel efficiency with angle and orientation Energy Generated In most parts of the UK, PV installations will generate around 800 kWh annually per kWp of installed capacity. The highest UK solar irradiation is in south-west England and South Wales; it is lowest in north-east Scotland (see map below). A typical domestic 3 kWp installation should generate an annual yield of around 2400 kWh – which is the equivalent of a small household’s annual electrical consumption. Figure 8: Solar irradiation map of the UK 15 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport Carbon Savings A typical domestic 3 kWp installation will offset approximately 1248 kg per annum of power station CO2 emissions. Cost Savings A typical domestic 3 kWp installation will save a maximum of £276 a year, providing all the electricity generated is consumed in the home. This is based on an electricity price of 11.5p/kWh. Capital Costs Approximately £6000 per kWp installed. Typical Payback Around 10 to 15 years for an optimized system that’s eligible for the feed-in tariffs. Lifespan Manufacturers often give a 25 or 30 year guarantee. Output does degrade slightly over time (rate dependent upon technology). Maintenance Since there are no moving parts the maintenance for PV systems is negligible. The panels may require periodic cleaning, although when at tilt angle, run-off from rain is usually sufficient. Noise Usually the only system noise is from the inverter cooling fans, which, if audible at all, should be no louder than computer cooling fans. The inverter converts the generated DC electricity into mains AC electricity. Planning Solar PV generally comes under the scope of ‘permitted development’ so planning permission is not required – although it is wise to check with the local planning department. Planning permission will usually be needed in conservation areas and national parks, and on listed/heritage buildings. Land Use The solar PV panels would be fitted to the roof structure therefore they would not require any further land use or special provision of land. Financial Incentives – FIT or RHI Since PV panels generate electricity they are viable for feed-in tariffs providing the products and installer used are MCS certified. A new build dwelling with a 3kWp installation will generate around £866 revenue a year. The tariffs for PV are fixed for 25 years so PV panels will provide the owner with a return on their initial investment. 16 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport 4.3 Solar Thermal General Description Solar collectors (panels) absorb solar radiation and convert it to heat which is transferred to a hot water cylinder by circulating fluid through a series of pipes to pre-heat the water in the cylinder. This pre-heated water is then further heated to useable temperature by an auxiliary system (boiler or electric immersion heater). Figure 9: Simple solar thermal installation diagram There are two standard types of collector: flat plate and evacuated tube. Flat plate collectors are simple but effective devices, comprising a dark plate within an insulated box with a glass or durable plastic cover. The plate is usually coated with a ‘selective’ coating to ensure that it has high absorption but low emissivity (heat loss by reradiation). Figure 10: Flat plate collectors Figure 11: Evacuated tube collectors Evacuated tube collectors are more sophisticated, with a series of metal strip collectors inside glass vacuum tubes. Their efficiencies are usually higher and they are more effective in cold weather because of their low heat losses, but they do tend to be more expensive than flat plate collectors, and succumb more easily to vandalism. 17 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport Both collector types can capture heat whether the sky is overcast or clear. Depending on UK location, 900–1100 kWh of solar energy falls on each m2 of unshaded UK roof surface annually. The annual energy captured by the two types is: Flat plates: 380–450 kWh per m2 of collector. Evacuated tubes: 500–550 kWh per m2 of collector. A typical solar domestic system features 4 m2 of flat plate or 3 m2 of evacuated tube, providing 50% to 65% of the energy required annually for water heating. Panels vary in size but are usually around 2 to 3m2 depending on manufacturer and collector type. Most domestic solar systems are known as indirect systems. The pipes connecting the collector to the hot water cylinder connect to a heat exchange coil inside the cylinder. The coil supplied by the solar system can either be in a dedicated solar cylinder that feeds preheated water to an existing domestic hot water cylinder served by a boiler, or it can be the lower coil in a purpose built twin-coil cylinder where the upper coil is connected to the boiler to provide the ‘top-up’ when needed. Suitability – Environment & Building As with PV panels, the collectors must be free from overshadowing. As with solar PV, the optimum orientation for mounting solar thermal collectors is due south with a 30° to 40° pitch. For individual systems, storage space must be available to house hot water tanks within dwellings. Energy Generated A typical domestic-sized installation has an annual yield of 1600–2000 kWh. Carbon Savings A typical installation will reduce CO2 emissions by 400–1000 kg per annum, depending on the fuel/energy displaced and conversion efficiency. Cost Savings Cost savings depend on the system type and orientation, the fuel/energy displaced and the energy conversion efficiency of the existing hot water supply. A typical 4m2 domestic installation that generates 1600 kWh of heat energy a year with an existing 90% efficient gas boiler will save approximately £57 per year based on gas price of 3.2p/kWh. Capital Costs £2000–£4000 installed on a new build property. Installing solar thermal systems on an existing dwelling can cost up to 30% more than for new build due to the additional infrastructure required to support the system being added to existing hot water systems. A flat-plate collector, including a twin-coil unvented cylinder costs in the region of £ 930 per m2 collector installed. An evacuated tube collector, including a twin-coil unvented cylinder costs in the region of £ 945 per m2 collector installed. 18 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport Typical Payback 8 to 20 years generally quoted: depends on fuel displaced, conversion efficiency, and fossil fuel/energy price escalation. Lifespan 30 years. Maintenance Solar water heating systems generally come with a 5-10 year warranty and require little maintenance. A yearly check by the householder and a more detailed check by a professional installer every 3-5 years should be sufficient Noise Solar collectors are considered to be silent in operation. Usually the only system noise is from the small circulation pump which should be no louder than a modern central heating pump. Planning Solar thermal generally comes under the scope of ‘permitted development’ so planning permission is not required – although it is wise to check with the local planning department. Planning permission will usually be needed in conservation areas and national parks, and on listed/heritage buildings. Land Use The solar PV panels would be fitted to the roof structure therefore they would not require any further land use or special provision of land. Financial Incentives – FIT or RHI Since solar panels generate renewable heat they will be viable for the renewable heat incentives when they begin in June 2011. 19 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport 4.4 ASHP (Air Source Heat Pump) General Description Air source heat pumps (ASHPs) use the same principles as ground source heat pumps (GSHPs). The heat pump takes low-grade energy from the surrounding air by means of a fan pulling the outside air over a heat exchanger (evaporator); this energy is then upgraded and the higher temperature refrigerant is released by means of another heat exchanger. In ASHPs this heat exchange can be to the air inside the dwelling or the heat exchange can be to water. Therefore there are two main types of air source heat pump system: An air-to-air system produces warm air which is distributed to the different rooms by ducts and supply grills. These systems are unlikely to provide hot water as well. An air-to-water system distributes heat via a wet central heating system. Heat pumps work much more efficiently at a lower temperature than a standard boiler system would. So they are more suitable for underfloor heating systems or larger oversized radiators, which give out heat at lower temperatures over longer periods of time. Figure 12: ASHP Figure 13: ASHP diagram Unlike GSHPs, where the temperature of the ground is relatively stable throughout the year, in an air source heat pump the source air temperature range can be highly variable. Air source heat pumps operate at their most efficient when the source temperature is as high as possible, but in the UK the mean air temperature for winter is lower than the mean ground temperature. All of these factors have an impact on seasonal efficiency for ASHPs, which is lower compared to GSHPs. Suitability – Environment & Building ASHPs are not particularly suited to cold winters, where coils may need to be defrosted or an alternative source of heating used in particularly severe conditions. 20 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport They are best suited to new build applications as they are most efficient when supplying low temperature distribution systems such as under-floor heating or oversized radiators. Energy Generated The efficiency of air source heat pumps is determined by their Coefficient of Performance (COP), which is the ratio of the units of heat out to units of electricity in. To maximise the efficiency of a heat pump it is important to have a low heating distribution temperature, and in these circumstances typical CoPs are about 2.5, which equates to an efficiency of 250% compared to a typical condensing gas boiler with a 90% efficiency. Capital Costs Costs for installing a typical ASHP system suitable for a detached home range from about £6,000 to £10,000 including installation. Running costs will vary depending on a number of factors including the size of the dwelling and how well insulated it is. Typical Payback ASHPs can have a pay-back of between 8 and 15 years, however this depends on a number of such as; the CoP of the heat pump, the heat distribution system, fuel costs, the type of fuel that they displace, if the system is providing hot water as well as space heating, temperature settings etc. Lifespan Air source heat pumps have a life expectancy between 20-25 years. Maintenance System maintenance is minimal. Noise Air source heat pumps emit noise from the fan and compressor which can cause a nuisance. They should not be sited in close proximity to bedrooms or neighbouring properties. Planning ASHPs are one of the few microgeneration systems that fall outside any permitted development rights and as such planning permission will be required. However, once ongoing legal technicalities have been resolved, it is expected that air source heat pumps will be permitted developments. Financial Incentives – FIT or RHI Since air source heat pumps generate renewable heat they will be viable for the renewable heat incentives when they begin in June 2011. 21 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport 4.5 GSHP (Ground Source Heat Pump) General Description A few metres underground remains at a constant temperature of about 10 to 15 degrees in the UK. It is possible to transfer this latent heat to a dwelling by installing a ground source heat pump. The heat pump draws heat from the ground via a ground collector (slinky) or a ground probe (bore hole) depending on the available area on site. Figure 14: A ground source heat pump Figure 15: Slinkies (coiled pipes) in a trench Heat pumps work in much the same way as a fridge in reverse. In a fridge the heat is transported from inside to outside, whereas a heat pump takes heat stored below the ground and transports it via the heating system to the house interior. In order to upgrade the low temperature heat from the ground into a higher, more useful temperature the system contains a compressor which increases the pressure and therefore the temperature of the systems refrigerant. Heat pumps operate most efficiently when the temperature difference between the heat source and the heat demand is smallest. They are therefore most suited to work with underfloor heating which run at between 35 and 40 degrees as opposed to radiators which typically operate at about 60 degrees. Suitability – Environment & Building GSHPs are well-suited to new build applications as their efficiency is improved when supplying low temperature distribution systems such as under-floor heating. Heat pumps have a typical operating temperature limit of 55°C and are not generally suitable for operation with traditional wet radiator systems. Either a horizontal or vertical ground collector is required; the choice will depend on land area available, local ground conditions and excavation costs. Energy Generated The efficiency of ground source heat pumps is determined by their Coefficient of Performance (COP) of the pump, which is the ratio of the units of heat out to units of electricity in. Ground source heat pumps should have a CoP of 3 or more, in order to gain 22 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport good carbon savings. That means that for every unit of electricity put into the system, 3 units of heat are produced. In other words the GSHP has an efficiency of 300% compared to a condensing gas boiler with 90% efficiency. Capital Costs The cost of a professionally installed GSHP ranges from about £1,200 to £1,700 per kW of peak heat output. This includes the cost of the distribution system. Vertical borehole systems would be at the higher end of this scale, due to greater installation costs. A typical 8kW system would therefore vary between £9,600 and £13,600. Installing a heat pump to replace a gas-fired heating system is less economically favourable than one replacing electrical or oil heating systems. Typical Payback GSHPs can have a pay-back of between 8 and 15 years; actual figures will depend to a great extent on the type of ground collector, ground conditions, the type of fuel that they displace and economies of scale for the installation. Lifespan GSHP technology is low in maintenance as systems have very few moving parts. Systems can have an operating life of over 40 years. Maintenance System maintenance is minimal. The piping infrastructure, like utility piping infrastructures, rarely requires maintenance. Only the pump may require maintenance work and it is easily accessible. Noise Heat pumps can emit constant noise due to the operation of the compressor. Although this is generally low level noise, locating heat pump units in close proximity to bedrooms should be avoided. Planning It is unlikely that planning permission will be required for the installation of a ground source heat pump, since the pipes are buried below ground and the only visible part of the system is the pump itself. However, it is wise to check with the local planning authority if the site is located in a Conservation Area. Land Use If a large enough land area is available, horizontal ground collectors are buried at a depth of approximately 1.2m and spaced 0.75m apart. The land area required is dependent on both the capacity of the heat pump and heat conductance of the soil type in which the pipes are buried. As a space saving alternative to horizontal collectors, slinkies - consisting of coiled pipes buried in a trench can be used. If land space is limited the ground collectors can be installed vertically in a borehole, drilled up to 100m deep in the ground. Multiple boreholes are commonly used in large installations where very high levels of heat extraction are required. 23 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport Financial Incentives – FIT or RHI Since ground source heat pumps generate renewable heat they will be viable for the renewable heat incentives when they begin in June 2011. 24 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport 4.6 Biomass Boiler General Description The term biomass refers to organic matter such as timber and crops grown specifically to be burnt to generate heat and power. Biomass can be sustainable and generally carbon neutral because the carbon released in the combustion process is offset by the carbon trapped in the organic matter during its growth. Biomass technologies have developed greatly over recent years and modern wood-fuel boilers are highly efficient, clean and smokeless. There are two main types of wood fuel which can be used in biomass boilers – wood pellets and wood chips, however smaller systems for domestic buildings may also use logs. The wood chip or wood pellets are fed automatically into the boiler from the fuel store using an auger screw system. The fuel then burns in the combustion chamber, where a regulated flow of oxygen ensures a clean and efficient combustion process. The resulting hot gases then heat water in a heat exchanger which feeds the hot water storage tank and then ultimately the heating circuit - such as radiators. Biomass boilers are as controllable as modern gas condensing systems; heating controls allow the user to adjust all elements for the central heating and domestic hot water. Figure 16: Biomass boiler Figure 17: Wood pellets Suitability – Environment & Building There are several factors that will influence the type of boiler suitable for a particular project. Space – If there is limited space on site then storage of wood fuel could be a restriction. Wood chips will occupy up three times more room than wood pellets for the same weight of wood. Biomass boilers also tend to be larger than conventional fossil fuel boilers, so there will need to be a large enough space to house the unit. 25 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport Size of the building – Typically the larger the building is, the greater requirement for space heating and therefore the larger the boiler needs to be. Larger systems will consume more fuel and therefore tend to be automated systems with minimal manual intervention. Biomass boilers with automatic auger feed mechanisms and fuel stores are generally too large for domestic installations. However, domestic systems allow the user to fill a hopper attached to the boiler. Access – For most systems a fuel delivery vehicle will need to access the site. Fuel can be delivered in a variety ways, however for bulk chips and pellet orders direct access to the fuel store is critical. For small domestic deliveries it is important to have a dry place to stack logs or store bags of pellets. Projects in urban areas will need to be mindful of the number of fuel deliveries (large vehicle movements) necessary throughout the year as this may have planning implications. Fuel supply – Generally if space and access are not a problem larger projects would consider wood chip; however if space is at a premium or the area is sensitive to a greater number of fuel deliveries then pellets are the preferred option. Energy Generated One tonne of wood pellets has an energy content of 5,000kWh and costs in the region of £160 which equates to 3.2p/kWh. One tonne of wood chips has an energy content of around 3,000kWh and costs about £50, which equates to 1.6p/kWh. A tonne of logs has an energy content of 4,200kWh and costs £60, which equates to 1.4p/kWh. Carbon Savings The carbon savings from a biomass boiler depends on what type of fuel is being displaced. In the Government’s 2009 Standard Assessment Procedure (SAP) grid electricity has a carbon emission factor of 0.52 kgCO2/kWh, mains gas has a carbon factor of 0.2 kgCO2/kWh and biomass has a carbon factor of 0.03 kgCO2/kWh. Therefore where the alternative is electric heating, biomass displaces 0.49 kg of CO2 per kWh of delivered heat and where the alternative is mains gas heating, biomass displaces 0.17 kg of CO2 per kWh of delivered heat. So for a standard dwelling heated by a gas boiler that uses around 18,000 kWh per year, a biomass boiler would save 3060 kg CO2. This saving would be significantly more if electricity was being displaced. Cost Savings The cost savings from a biomass boiler depends on what type of fuel is being displaced, the efficiency of the boiler and the type of biomass fuel used. If the biomass boiler was 90% efficient and it ran on wood pellets the energy running costs would be silighty more than a 90% efficient gas boiler since the average mains gas price is 3p/kWh and wood pellets retail at around 3.2p/kWh. Cost savings are more likely when replacing electric heating since the average price for electricity is 11.46p/kWh (according to SAP 2009). Capital Costs As a general guide for domestic installations the price per installed kW (including flue, fuel storage, fuel feed, commissioning and design, exc VAT) is around £450 - £600. So a 15kW pellet boiler would cost approximately £9,000. Wood chip boilers cost 26 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport approximately £250 - £450 per kW installed. Log boilers tend to be cheaper than both wood chip and wood pellet boilers; for example a 20kW system suitable for a 3 or 4 bed property would cost in the region of £150 - £200 per kW installed (£3,000 to £4,000). Typical Payback Depends on fuel displaced and type of system. Payback periods will be reduced when the renewable heat incentives begin in June 2011. Lifespan 25 years. Maintenance Automated feeding and de-ashing systems mean that maintenance requirements are minimised. In addition, the majority of boilers have a built-in modem, which automatically contacts the site engineer if a performance problem is detected. Smaller boilers normally require an annual visit while much larger boilers may need a quarterly visit. Most UK installers offer ongoing maintenance contracts. Noise Some people find the fan noise of certain wood pellet stoves intrusive. Planning Biomass boilers generally fall under permitted development rights (i.e. planning permission is not required) unless the flue exceeds 1m above the roof height or if it is installed on the principal elevation which is visible from a road on buildings in Conservation Areas and World Heritage Sites. Not all biomass equipment is approved for operation in smokeless zones. Land Use A dry, covered fuel store is required with adequate space – wood is bulky, and often bulk discounts depend on logs or pellets being delivered in sizeable quantities, e.g. tonne loads. Financial Incentives – FIT or RHI Since biomass boilers generate renewable heat they will be viable for the renewable heat incentives when they begin in June 2011. 27 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport 5.0 Feasibility Study of Renewable Technologies This section will assess the technical viability of the following renewable energy technologies for the site in order to rule out unfeasible options: - Mast mounted wind turbines Roof mounted wind turbines Solar PV (Photovoltaic) Panels Solar Thermal Panels GSHP (Ground Source Heat Pump) Biomass Micro Combined heat and power (CHP) The following observations have been made with regard to the technical feasibility of integrating renewable energy technologies into this development. Renewable Technology Feasible Mast Mounted Wind Turbine No Roof Mounted Wind Turbine No Reasons Currently the BWEA suggests a large wind turbine to be viable where wind speed is 7m/s or above. According to the NOABL database the average wind speeds for the site postcode (CR8 3AG) are 4.6 m/s at 10m, 5.4 m/s at 25m and 6 m/s at 45m height. Therefore the wind speeds are not sufficient for a Wind turbine to be viable. The surrounding area isn't free from obstructions such as buildings and trees that could cause uneven and turbulent wind patterns. Depending on the exact location of existing and proposed trees there may be sufficient open land for a mast mounted wind turbine to be installed. Surrounding properties aren't far enough away to be unaffected by turbine noise, reflected light and shadow flicker. Currently the BWEA suggests a small scale wind turbine to be viable where wind speed is 6m/s or above. According to the NOABL wind map the average wind speeds for the site postcode (CR8 3AG) are 4.6 m/s at 10m, 5.4 m/s at 25m and 6 m/s at 45m height. Therefore the wind speeds are not sufficient to be viable since the average wind speed isn't greater than 6 m/s at hub height. The surrounding area isn't free from obstructions such as buildings and trees that could cause uneven and turbulent wind patterns. Roof mounted wind turbines are not yet a proven technology and a number of technical problems have been identified by manufacturers which are being investigated to rectify these issues. 28 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport Solar PV (Photovoltaic) Panels/Tiles Yes Solar Thermal Collectors Yes ASHP (Air Source Heat Pump) No GSHP (Ground Source Heat Pump) No Biomass Boiler No Micro CHP No The proposed dwelling has both South East and South West facing areas of roof The roofs should be free from overshadowing for most of the day from other buildings, structures or trees. There is sufficient unshaded roof area. The proposed dwelling has both South East and South West facing areas of roof The roofs should be free from overshadowing for most of the day from other buildings, structures or trees. There is sufficient unshaded roof area. There will be a year round hot water demand. All the proposed housetypes have space for a hot water cylinder close to the solar panels. Solar thermal collectors would be compatible with the planned heating system. There is space inside the dwelling for a hot water cylinder. An external ASHP can’t be located away from the bedrooms to avoid potential noise issues. The proposed dwellings do have a sufficient area of land where horizontal piping could be installed. The proposed dwellings do have a sufficient area of land where vertical piping could be installed, however it is unknown whether the ground is free from obstacles such as sewers, tunnels etc. It is possible to have a low-grade heat distribution system e.g. underfloor heating, oversized radiators. A basic ground study to check if the site is suitable for ground source heat pumps has not been conducted. There is not sufficient space inside all the proposed dwellings for the heat pump. There is an established fuel supply chain for the area. There isn’t sufficient space for a delivery vehicle. (vehicular access to fuel storage, turning circle etc) There isn't sufficient space inside the proposed dwellings for a wood-fuel boiler and associated auxiliary equipment. There isn't sufficient space for fuel storage to allow a reasonable number of deliveries. Micro CHP is gas-fired and therefore is not generally classed as a renewable energy technology Micro CHP is ideal for high-density residential developments as there is a sufficient year round heat and electrical demand. The relatively low-density of the site makes it unsuitable for the application of micro CHP. Table 4: Feasibility Study of Renewable Technologies 29 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport Based on the feasibility study in table 4 above, the following technologies have been identified as being feasible for the proposed development. Solar PV (Photovoltaic) Panels/tiles Solar Thermal Panels Following discussions with the developer of the site it was concluded that their preferred technology from the above list of feasible technologies was Solar PV panels. Therefore this technology will be taken forward for sizing and calculation of the contribution to CO2 reduction. 30 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport 6.0 System Size to Provide 10% CO2 Reduction The developer is proposing to install solar photovoltaic panels to the roof of the new block of flats. Due to the restricted amount of suitable roof area on the plots, because of the dormer windows and balconies, it is suggested that a high efficiency 250w solar pv panel is utilized on this development. Solar PV was added to the sap calculations in increments of 0.25kWp until a 25% improvement in the Dwelling Emission Rate (DER) over the Target Emission Rate (TER) was achieved – to achieve the mandatory requirement in ENE1 for code for sustainable homes level 4. The results of this process can be found in table 5 below. In essence a total of 6.5 kWp (26 No. 250w panels) will need to be installed on the project to ensure that the mandatory 25% improvement of DER over TER needed for code level 4 properties is achieved. It is proposed to split the PV array into 3.5kWp (14 No. 250w panels) on the South-West facing roof of the development and 3kWp (12 No. 250w panels) on the flat roof of the development. A check was then carried out to establish what percentage of site wide CO2 is reduced from the 6.5kWp array of solar pv. According to the SAP software, the 6.5 kWp of pv generates 5,105 kWh/year which provides a CO2 reduction of 2,639 kgCO2/year (based on a carbon factor of Electric = 0.517 kg CO2/kWh) Since the site wide CO2 emissions before renewables are added is 13,000 kgCO2/year, this represents a 20.3% reduction which is more than sufficient to satisfy EP16. Plot 1 2 3 4 5 6 7 8 9 10 11 TER DER % Improvement Code Level (ENE1) 12.87 12.91 13.6 14.93 11.97 12.71 12.17 10.68 14.72 15.12 13.51 18.36 17.7 18.28 19.88 16.05 15.72 15.25 14.56 19.33 19.77 18.43 29.9 27.06 25.6 24.9 25.42 19.15 20.2 26.65 23.85 23.52 26.7 4 4 4 3 4 3 3 4 3 3 4 PV (kWp) Prorata based on floor area (SW Roof 45°) PV (kWp) Prorata based on floor area (Flat Roof) 0.36 0.38 0.33 0.24 0.34 0.30 0.33 0.32 0.28 0.30 0.33 3.50 0.31 0.32 0.28 0.20 0.30 0.26 0.28 0.27 0.24 0.26 0.28 3.00 Table 5: SAP Results and Amount of PV per Plot As can be seen from the above not all of the dwellings achieve code level 4 based on the % improvement of DER over TER and the floor area prorata share of kWp of solar pv. However as stated in the code for sustainable homes 2010 technical guide under category ENE1 Dwelling Emission Rate: 31 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport “Where a building contains multiple dwellings, it is acceptable to asses this issue based on the average energy performance of all the dwellings within the building.” In this case the SAP calculations show the following TER and DER for the site as a whole: This means the overall percentage improvement of DER over TER is as follows: 100 – (( Average DER) x 100) = 100 – (( 13.12 ) x 100) = 25.02% Average TER 17.50 The above calculation shows that the minimum percentage improvement of 25% to achieve code level 4 has been satisfied and therefore all dwellings on the site now reach this level. 32 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport Table 6 below shows the CO2 emissions of the development following the introduction of 6.5kWp of solar PV. Total Energy Demand (kWh/yr) Associated Total CO2 (kgCO2/yr) Space Heating (gas) 20,243 4,008 Water Heating (gas) 27,455 5,436 Fixed Electrical 6,880 3,556 Solar PV -5,105 (generated) -2,639 (reduced) Site Total 49,473 10,361 Table 6: Carbon Emissions of the Development with 6.5kWp Solar PV Associated Total CO2 (kgCO2/yr) Baseline (no PV) (2) 13,000 With PV 10,361 Reduction in CO2 (1) 2,639 % Reduction (1) / (2) x 100 20.3% Table 7: Percentage Reduction in Carbon Emissions from 6.5 kWp Solar PV Table 7 above shows the percentage reduction in CO2 emissions contributed by the solar PV panels. Therefore the installation of 6.5kWp of solar pv will achieve significantly greater than the 10% CO2 reduction required to satisfy EP16. Figure 18: Proposed South West Elevation showing possible location of 14 No. 250w PV panels 33 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport Figure 19: Proposed Roof Plan showing possible location of 12 No. 250w PV panels mounted horizontal on the flat roof 34 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport 35 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport 36 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport 37 Woodc ot e Va l l e y Roa d, Pur l e y, Cr oydon 10% R enew able Ener gy R eport 38