This document describes the data sources, definitions and assumptions incorporated in the IRENES Land Use Tool (ILUT) available within the XMAP platform (https://irenes.xmap.cloud/login). It outlines the resources available for the territory covered by the Greater South East Net Zero Hub (GSENZH) as of June 2024.
Figure 1: Stages in developing an evidence base for
renewable energy potential (SQW Energy, 2010).
Table 1: Assumptions made in the calculation of theoretical energy potentials.
Calculation Steps | Calculation Results | References |
Wind Speed | ||
Example wind speed | 7.5 m/s | |
Power density = (0.5 * Density of Air) * (Wind Speed)3 | (0.5 x 1.3) x (421.9) = 274.2 W/m2 | MacKay (2009) p.264 |
Maximum extractable power (59%) | 0.59 x 274.2 = 161.8 W/m2 | MacKay (2009) p.264 |
Power of turbine 80 m diameter and 100 m hub height | 161.8 x (3.1416 x 402) = 813,297 W | |
Turbine minimum spacing (5 diameters) | MacKay (2009) p.265 | |
Power density (power of turbine / land area of turbine) | 813,297 / (5 x 80)2 = 5.1 W/m2 | |
Theoretical energy (as power density) | 5.1 W/m2 | |
Solar Radiation | ||
Example Global Irradiation at Optimum Tilt (GTI) | 140 W/m2 | |
Assumed panel efficiency (17.5%) | 0.175 x 140 = 24.5 W/m2 | microgen-database.sheffield.ac.uk |
Ratio of panel area to plant area (40%) | 0.4 x 24.5 = 9.8 W/m2 | Solar Trade Association data |
Theoretical energy (as power density) | 9.8 W/m2 | |
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Table 1 includes example calculations based on typical values for the East of England. These results indicate a theoretical power density for solar PV that is approximately double that for onshore wind. Similar contrasts are apparent in the findings presented by Smil (2016, p.203). It is important to note, however, that these are estimates of potential capacity and do not incorporate load factors that will also influence the amount of electricity that can be generated over a year.
The parameters from Table 1 were used in the Land Use Tool to produce estimates of theoretical electricity generation for a mesh of 1 km resolution cells. Figure 1 shows the resulting spatial variations in electricity power density for solar PV and onshore wind.
To assess the exploitable energy it is necessary to identify factors that could prevent the use of land for renewable energy generation. Within England there are planning regulations that restrict developments in the vicinity of certain facilities (e.g. airfields), but currently no national strategic or zoning framework. However, many studies have examined suitability criteria for different renewables (e.g. SQW Energy, 2010; Watson & Hudson, 2015; Gove et al., 2016; Palmer et al., 2019; McKenna et al., 2022). For the purposes of the IRENES Land Use Tool a two-stage approach was adopted. The first of these involved the compilation of a series of spatial data layers on land use characteristics based on criteria discussed in previous studies. Secondly, a data-driven assessment was carried out to examine the influence of these layers on the existing distribution of generation sites. This involved extracting details of grid references and generation capacity for all operational or under construction onshore wind or ground solar PV installations from the Renewable Energy Planning Database (REPD, https://www.gov.uk/government/publications/renewable-energy-planning-database-monthly-extract). The ArcGIS software was then used to overlay these points on the polygons for the different land use factors. This made it possible to assess the extent to which the distributions coincided and therefore the degree to which different factors appeared to exclude current generation facilities. These results were then used to group siting factors into categories of likely development constraint.
Spatial data to represent the different land use factors were obtained from the sources listed in Table 2. These layers were then imported into ArcGIS and combinations of buffer and overlay operations used to identify the extent to which they coincided with the locations of existing generation sites.
Table 2: Data sources used to define the land use factors.
Feature | Source | URL |
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Motorways, A & B Roads | Ordnance Survey VectorMap® District | |
Railways | Ordnance Survey VectorMap® District | |
Rivers, Canals, Lakes & Reservoirs | Ordnance Survey VectorMap® District | |
Populated Areas | Census 2021 LSOA Centroids | |
Airports & Airfields | Civil Aviation Authority, MoD, Ofcom | |
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Ministry of Defence Land | Ordnance Survey OpenMap - Local | |
Airspace Restrictions | Met Office and NATS | |
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Slopes | Ordnance Survey Terrain® 50 | |
Peaty Soils | Natural England | |
Monuments & Heritage Sites | Historic England | https://historicengland.org.uk/listing/the-list/data-downloads/ |
Ancient Woodland | Natural England | |
Managed Woodland | Forestry Commission | |
Designated Nature Reserves | Natural England | |
National Landscapes and Parks | Natural England | |
Green Belt | DLUHC | |
Green Spaces | Ordnance Survey | |
Agricultural Land Classification | Natural England | |
Risk of Flooding from Rivers & Sea | Environment Agency |
Table 3 lists the hectares covered by different land use factors within the GSENZH territory. Several of these had buffer zones defined around them based on suggestions in the literature. For each factor the table also lists the number of solar PV sites (as of January 2024) and their total electricity generation capacity (in MW) that occurred within the polygons. It is clear from this that some factors completely or largely excluded solar sites (e.g. National Parks), whilst in other cases they were quite common (e.g. Grade 1 or 2 agricultural land). Since the sites also varied in capacity an overall measure of likely absence was calculated as the ratio of the percentage of total regional capacity within the factor polygons divided by the percentage of the GSENZH area they occupied. With this measure a low value (e.g. at or close to zero) implies that few existing sites occurred where the factor was present, whilst a higher value (e.g. above 1.0) suggests that it was not an important constraint. From these results it is clear that proximity to infrastructure, populated area, various designations and high flood risk were important siting constraints, whilst higher quality agricultural land and peaty soils had less influence. These capacity/ha ratios were used alongside discussions in policy documents to produce a three-level classification of siting constraint as shown in the right-most column. As a general rule if the ratio was < 0.1 then the classification was ‘Very Unlikely’, if it was between 0.1 and 0.5 it was ‘Unlikely’ and if above 0.5 then ‘Potentially Available’. However, a small number of exceptions to this approach were made, particularly where the number of sites involved was small.
Table 3: Land use siting assessment for solar PV.
Area in Hectares | Solar Sites | Capacity in MW | % Capacity / % Ha Ratio | Classification | |
Main Roads + 15 m Buffer | 58,181 | 0 | 0.0 | 0.00 | Very Unlikely |
Railway Tracks + 15 m Buffer | 14,650 | 0 | 0.0 | 0.00 | Very Unlikely |
Main Water Courses + 150 m Buffer | 306,059 | 18 | 112.9 | 0.39 | Unlikely |
Lakes and Reservoirs + 150 m Buffer | 38,366 | 3 | 14.7 | 0.40 | Unlikely |
Airports/Airfields + 500 m Buffer | 92,044 | 6 | 13.0 | 0.15 | Unlikely |
Military Land | 4,629 | 1 | 1.5 | 0.34 | Very Unlikely |
Designated Nature Reserves | 245,366 | 1 | 13.0 | 0.06 | Very Unlikely |
Ancient Woodland | 166,154 | 1 | 2.8 | 0.02 | Very Unlikely |
Managed Woodland | 470,102 | 6 | 87.8 | 0.20 | Unlikely |
Monuments & Heritage Sites | 17,854 | 0 | 0.0 | 0.00 | Very Unlikely |
Registered Parks & Gardens | 73,413 | 0 | 0.0 | 0.00 | Very Unlikely |
OS Open Greenspace | 120,940 | 4 | 39.4 | 0.34 | Unlikely |
National Parks | 195,829 | 0 | 0.0 | 0.00 | Very Unlikely |
National Landscapes (AONBs) | 585,991 | 7 | 34.8 | 0.06 | Very Unlikely |
Green Belt | 566,453 | 26 | 265.7 | 0.49 | Unlikely |
Slope (>5%) | 788,605 | 21 | 163.5 | 0.22 | Unlikely |
Agricultural Land Grade 1 or 2 | 947,477 | 115 | 1,164.3 | 1.30 | Potentially Available |
High Flood Risk | 163,478 | 2 | 1.0 | 0.01 | Very Unlikely |
Medium Flood Risk | 235,627 | 13 | 91.7 | 0.41 | Unlikely |
Peaty Soils | 231,559 | 20 | 225.9 | 1.03 | Potentially Available |
Census Centroids + 200 m Buffer | 468,152 | 8 | 69.6 | 0.16 | Unlikely |
Census Centroids + 500 m Buffer | 1,090,850 | 48 | 367.0 | 0.36 | Unlikely |
Census Centroids + 1 km Buffer | 2,230,859 | 165 | 1,312.2 | 0.62 | Potentially Available |
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Totals | 4,139,096 | 356 | 3,922.6 | - |
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Table 4: Land use siting assessment for onshore wind.
Solar Siting Factor | Area in Hectares | Solar Sites | Capacity in MW | % Capacity / % Ha Ratio | Classification |
Main Roads + 150 m Buffer | 519,979 | 2 | 3.3 | 0.04 | Very Unlikely |
Railway Tracks + 150 m Buffer | 135,901 | 1 | 9.0 | 0.38 | Unlikely |
Main Water Courses + 150 m Buffer | 306,059 | 1 | 20.7 | 0.38 | Unlikely |
Lakes and Reservoirs + 150 m Buffer | 38,366 | 1 | 1.5 | 0.22 | Unlikely |
Airports/Airfields + 5 km Buffer | 329,192 | 1 | 2.2 | 0.04 | Very Unlikely |
Rader Sites + 5 km Buffer | 25,256 | 0 | 0.0 | 0.00 | Very Unlikely |
Military Land | 4,629 | 0 | 0.0 | 0.00 | Very Unlikely |
Designated Nature Reserves | 245,366 | 0 | 0.0 | 0.00 | Very Unlikely |
Ancient Woodland | 166,154 | 0 | 0.0 | 0.00 | Very Unlikely |
Managed Woodland | 470,102 | 0 | 0.0 | 0.00 | Very Unlikely |
Monuments & Heritage Sites | 17,854 | 0 | 0.0 | 0.00 | Very Unlikely |
Registered Parks & Gardens | 73,413 | 0 | 0.0 | 0.00 | Very Unlikely |
OS Open Greenspace | 120,940 | 2 | 2.5 | 0.12 | Unlikely |
National Parks | 195,829 | 0 | 0.0 | 0.00 | Very Unlikely |
National Landscapes (AONBs) | 585,991 | 0 | 0.0 | 0.00 | Very Unlikely |
Green Belt | 566,453 | 2 | 2.5 | 0.03 | Very Unlikely |
Slope (>15%) | 76,460 | 0 | 0.0 | 0.00 | Very Unlikely |
Agricultural Land Grade 1 or 2 | 947,477 | 27 | 307.4 | 1.84 | Potentially Available |
High Flood Risk | 163,478 | 2 | 11.5 | 0.40 | Very Unlikely |
Medium Flood Risk | 235,627 | 21 | 196.9 | 4.75 | Potentially Available |
Peaty Soils | 231,559 | 9 | 84.1 | 2.07 | Potentially Available |
Census Centroids + 200 m Buffer | 468,152 | 0 | 0.0 | 0.00 | Very Unlikely |
Census Centroids + 500 m Buffer | 1,090,850 | 5 | 18.1 | 0.09 | Unlikely |
Census Centroids + 1 km Buffer | 2,230,859 | 20 | 120.3 | 0.31 | Unlikely |
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Totals | 4,139,096 | 76 | 727.9 |
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Figure 2: Classification results for solar PV and onshore wind.
Further refinements to the classifications were to incorporate variations in power density for solar radiation and wind speed as well as proximity to electricity substations. The power density estimates were such that very little of the region was excluded on the basis of unviable generation potential. An analysis of proximity to electricity substations (primary, bulk or grid supply locations from network operator data portals) indicated that the average distance to solar PV sites was 2.4 km and for onshore wind turbines 2.9 km. A buffer distance of 3 km around existing substations was therefore used to identify areas that would be more suitable for renewable energy developments. No attempt was made to define available connection capacity at individual substations since this is complex to determine and any estimate would be best obtained from the relevant network operator. Using a buffer distance does, however, provide a simple screening regarding the scope for network connection.
Tables 5 and 6 indicate how the values of the % capacity / % ha ratios vary between the different classification categories when proximity to substations is incorporated. This is termed the ‘full’ classification below. As would be anticipated, there is a strong gradient, with the highest ratio in ‘Potential Areas’ closer to a substation and very low ones in a more distant area classed as ‘Very Unlikely’. It is also apparent that the influence of substation proximity is stronger of solar PV sites than onshore wind turbines. Overall the trends are sufficiently strong to help identify where additional capacity might be located based on current experience. The map in Figure 3 shows the spatial distribution of the different categories in the full classification.
Table 5: Capacity / ha ratio results for the full solar PV classification.
< 3 km from Substation | > 3 km from Substation |
Total | |
Potential Area | 4.71 | 1.03 | 2.31 |
Unlikely Area | 0.65 | 0.48 | 0.59 |
Very Unlikely Area | 0.10 | 0.01 | 0.04 |
Total | 1.52 | 0.54 | 1.00 |
Table 6: Capacity / ha ratio results for the full onshore wind classification.
Classification | < 3 km from Substation | > 3 km from Substation |
Total |
Potential Area | 5.73 | 2.81 | 3.69 |
Unlikely Area | 1.26 | 0.76 | 0.99 |
Very Unlikely Area | 0.02 | 0.07 | 0.05 |
Total | 1.04 | 0.96 | 1.00 |
Figure 3: Full classification results for solar PV and
onshore wind.
The approaches and data discussed above are incorporated in the IRENES Land Use Tool in several different ways. Within the tool the following folders of resources are available. Hovering your mouse over a layer name will display a pop-up with more information about how the layer is defi ned and sources.
· Prospecting Sidebar – this allows the
user to define potential areas and then calculates their theoretical
electricity generation using the power densities in Table 1. The total for all sites within a parish can
also be calculated.
· Boundaries Sidebar – shows the GSENZH boundary, plus those of local government units.
· Wind Potential Sidebar – displays the areas covered by the different classification categories, either individually or in combination. The full classification incorporating substation proximity is also available.
· Infrastructure Sidebar – includes individual map players for roads, railways, airfield buffers and military sites.
· Populated Areas Sidebar – includes individual map players for buffer zones of different distances around census centroids.
· Resource Potential Sidebar – includes individual map players for solar radiation, wind speed and derived power densities.
· Soils and Geology Sidebar – includes map layers on peaty soils, subsidence risk (from British Geological Survey analysis) and slope steepness
· Water Sidebar – Includes map layers on rivers, lakes, reservoirs and flooding risks.
In terms of how these resources might be used we envisage that the classifications in the Solar Potential and Wind Potential sidebars would provide a quick way of screening a region of interest for possible development sites. Individual factors from other sidebars could then be added to refine this assessment. Alternatively, the user could build up their own evaluation by combining individual factors as they wished. In either case, if a particular locality was identified then the tools in the Prospecting sidebar could be used to define individual sites and assess their electricity generation potential. Further capabilities may be added in subsequent versions of the tool.
Several spatial data sets used in the analysis are © copyright Ordnance Survey. Others are used under the terms of the Open Government Licence v3.0. Wind speed data were obtained from the New European Wind Atlas, a free, web-based application developed, owned and operated by the NEWA Consortium. For additional information see www.neweuropeanwindatlas.eu. Solar radiation data are © 2019 The World Bank, source: Global Solar Atlas 2.0, solar resource data: Solargis.
The research underpinning the compilation of the data layers and tool creation was funded by a combination of the EU Interreg Europe Programme (IRENES), the UK Energy Research Centre Phase 4, the Greater South East Net Zero Hub, five county councils in eastern England (Cambridgeshire, Essex, Hertfordshire, Norfolk and Suffolk) and UK Power Networks. Chris Mewse (Geoxphere) was responsible for the implementation within the Parish Online platform. We are also grateful to our local government and regional stakeholders for their advice and feedback.
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