Site suitability report for a wind farm in the UK
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Transcript of Site suitability report for a wind farm in the UK
Site suitability report for a wind farm in the UK
Gonzalo Romero
16/03/2012
GEOG5060 Gonzalo Romero
INDEX
1. INTRODUCTION.....................................................................................................3
2. PHASE 1...................................................................................................................3
2.1. Input data......................................................................................................................3
2.2. Selection of criteria.......................................................................................................4
2.3. Initial modelling assessment.........................................................................................5
3. PHASE 2...................................................................................................................9
3.1. Input data......................................................................................................................9
3.2. Selection and analysis of criteria................................................................................103.2.1. Environmental criteria.........................................................................................................113.2.2. Social criteria.......................................................................................................................113.2.3. Economic criteria.................................................................................................................123.2.4. Technical criteria.................................................................................................................12
3.3. Weighing of criteria....................................................................................................12
3.4. Site selection...............................................................................................................13
4. DATA QUALITY...................................................................................................17
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1. INTRODUCTION.
This report focuses on the site selection phase of a 90MW wind farm in Britain.
Selection of suitable areas to build a wind farm requires a set of considerations that
range from technical to environmental factors. Such considerations are mainly based on
the “Best Practice Guidelines for Wind Energy Development” (BWEA, 1994). Potential
sites for wind farms are identified using a Multi-Criteria Evaluation (MCE) & GIS
approach. The project is carried out under 2 different phases. First phase aims to search
for potential sites using key criteria to do initial modelling. Second phase is developed
on the previous selected sites adding new technical and environmental criteria. Main
aspects mentioned in this report are data source, data quality, weighting criteria and
selected method used to reach the final decision.
2. PHASE 1.
1.1. Input data.
Next table shows initial data used in this project.
SourceFile
FormatDescription Spatial Reference System
BWEA .asc 1 km2 wind speed data from at 10, 25 and 45m above ground level
British National Grid
CIS2000 .asc 1 km2 Digital Terrain Model (DTM) British National GridCIS2000 .asc 1 km2 Dominant Land Cover (DLC) British National GridDigimap .shp county_region 1:50,000 scale British National GridTable 1. Data used in phase 1.
As stated in table 1, some data have unknown spatial reference system (SRS). After
converting ASC files into GRID format it is observed that such layers do not match
when are added into ArcMap. This problem is fixed by opening layer properties using
ArcCatalog. British National Grid is selected as SRS, and linear unit is changed from
meters to kilometer. Finally the visible extent properties (left and bottom) are also
changed for “DTM” and “wspeed” layers.
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Figure 1. Input data for phase 1. Source: ArcMap 10.
1.2. Selection of criteria.
Criteria are mainly related to technical factors as wind speed (orientation) or
topographic site conditions (slope, elevation), and environmental factors as soil type.
Their importance is mentioned briefly.
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1) Orientation: dominant wind direction is a crucial technical factor for a wind
farm.
2) Slope: slope poses a problem of limitations to site access. It must be considered
that during the construction phase moderate or strong slopes are not appropriate
for heavy goods vehicles (BWEA, 1994). On the other hand, faster wind occurs
more often when there is strong variation in threshold slope (EDINA, 2001).
3) Land type: suitability to locate a wind farm varies depending on the land type.
4) Wind speed: probably the most evident technical factor. A wind farm is not
feasible if there is not a certain minimum annual average speed.
1.3. Initial modelling assessment.
Correspondent GRIDs are reclassified according to Boolean criteria where 1 (total
constraint) is not suitable and 0 (no constraint) is suitable.
1) Orientation
“Aspect” layer is derived from “DTM” layer using Spatial Analyst Tools
(Surface_Aspect). According to information from Exmoor National Park, the most
common winds are south-westerlies. This means that our potential sites will have a
westerly orientation.
AspectOld value New valueFlat 0North 1Northeast 1East 1Southeast 1South 1Southwest 0West 0Northwest 0
Table 2. Aspect reclassification.
2) Slope
“Slope” layer is derived from “DTM” layer using Spatial Analyst Tools
(Surface_Slope). Z factor was modified as x,y units and z units are not in the same units
of measure. The problem of slope is that has been derived from a DEM where its spatial
resolution is 1 km. This leads to inaccuracy that must be taken into account during the
analysis. Layer is reclassified considering slope not to be greater than 10% (Baban,
2001).
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SlopeOld value New value0-10% 0>10% 1
Table 3. Slope reclassification.
3) Land type
Dominant land cover is reclassified according to table 4.
Code Class Value1 Broad-leaved / mixed woodland 12 Coniferous Woodland 13 Arable and Horticultural 04 Improved Grassland 05 Semi-natural / rough grass and bracken 06 Montane, Heath and Bog, and inland rock 07 Built-up and Gardens 18 Standing open water and canals, rivers and
streams1
9 Coastal 010 Sea/Estuary and Unclassified 1
Table 4. Land characteristics. Source: Land Cover Map of Great Britain (2000).
4) Wind speed
Although we have layers containing wind speed data from BWEA at 10, 25 and 45m
above ground level, we finally use wind speed data at 45m as hub heights are 45m
above ground level (Siemens, 2012). Such layer is reclassified considering wind speed
should be greater than 6,5m/s to have a wind resource suitable for wind development
(US Department of Energy, 2012)
Wind SpeedOld value New value
>6.5 0<6.5 1
Table 5. Wind speed reclassification.
Sieve Map
The initial map with potential sites is based on Boolean Criteria as it helps to
differentiate areas that are completely unsuitable for a wind farm.
The output “Sieve” layer is the result of using CellStatistics tool in Spatial Analyst.
“Maximum” operator is used to determine the maximum (largest value) of the inputs for
each cell. Maximum operator ensures the “area will be suitable to the extent of its best
quality” (Jiang p. 178, 2000). Hence values equal to 0 are selected for phase 2. All the
analysis process can be observed in Figure 2.
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Figure 3 shows the location of the selected area where there is an important number of
potential sites. Phase 2 is carried out in this selected area where potential sites occupy a
total extent of 2.428 km2.
Figure 2. Flow chart for phase 1. Source: Model Builder.
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Figure 3. Potential sites for a wind farm in UK. Source: ArcMap 10.
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3. PHASE 2.
1.4. Input data.
In this second phase more constraint factors are added. Table 6 shows the additional
input data used in this second phase. Such inputs are shown graphically in figure 4.
SourceFile
FormatDescription Spatial Reference System
Digimap .shp Motorways 1:50,000 scale British National GridDigimap .shp A_roads 1:50,000 scale British National GridDigimap .shp Urban_Region_South 1:250,000 British National Grid
Natural England
.shp
Special Conservation Areas of England (areas which have been identified as best representing the range and variety within the European Union of habitats and (non-bird) species listed on Annexes I and II to the EC Habitats Directive). 1:10,000 scale
British National Grid
Natural England
.shpSite of Special Scientific Interest (SSSI). 1:10,000 scale
British National Grid
Natural England
.shp National Parks. 1:10,000 scale British National Grid
Digimap .shp Woodland region 1:50,000 scale British National GridDigimap .shp Rivers. 1:50,000 scale British National GridNational Grid
.shp Lines (electricity network) British National Grid
Table 6. Additional data used in phase 2.
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Figure 4. Input data for phase 2. Source: ArcMap 10.
1.5. Selection and analysis of criteria.
Multi-Criteria Evaluation used for this second phase, involves environmental, social,
economic and technical considerations (Baban, 2001) for a better assessment of
potentiality, limitations and constraints of a potential wind farm site. Analytic Hierarchy
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Process (AHP) is used “to make a decision in an organized way, generate priorities and
establish the relative importance of the criteria” (Saaty p.85, 2008).
Goal Objectives Attributes
Ecological Area (SCA, SSSI, National Parks) Environmental
Rivers
Social Urban areasSuitability
Road networkEconomic
Electrical network
Technical Woodlands
Figure 5. Hierarchical organization of the criteria.
Prior the analysis start, several environment options were set in the Geoprocessing
toolbar as workspace, cartography (British_National_Grid) and mask in Raster Analysis
(2 areas selected in phase 1).
1.5.1. Environmental criteria.
There are environmental restrictions due to ecological characteristics of some areas. In
this respect no sites are selected within the boundaries of Special Conservation Areas
(SCA) as well as Sites of Special Scientific Interest (SSSI’s) and National Parks
(EDINA, 2001). Analysis is carried out in ArcMap using the tool “Merge” to combine
the different layers. The output “EA” (ecological area) is converted into raster and
reclassified giving highest values (10) to cells included in ecological areas and lowest
value (0) to the rest of cells.
On the other hand, to avoid water pollution, potential sites cannot be located within 200
meters from rivers (EDINA, 2001). Buffer zones are created for “rivers” layer, and the
output is converted into raster. As previous paragraph, we obtain a raster which is
reclassified giving highest value (10) to cells included in such areas and lowest value (0)
to the rest of cells.
1.5.2. Social criteria.
Due to noise pollution, it is considered potential sites cannot be located within 500
meters from urban areas or single dwellings (EDINA, 2001). Same analysis as for rivers
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is applied. Cells included within 500 meters from such areas are giving the highest
value (10) whereas the lowest value (0) is given to the rest of cells.
1.5.3. Economic criteria.
It is evident that the further away potential sites are from road network the more
expensive the project will be. This is also valid for distance from electrical network. In
this sense, potential sites cannot be located further than 10 Km from roads and electrical
network (Baban, 2001).
As there are 2 road layers for roads, Merge tool is used to convert them into one single
layer. Once it is converted into raster, Cost distance from roads is obtained using slope
as input cost raster. Finally the output raster is reclassified according to table 7. As for
electrical network, similar analysis is undertaken.
Euclidian distance from Road Network
Euclidian distance from Electrical Network
Old value New value Old value New value<1000 meters 0 <1000 meters 02000 meters 1 2000 meters 13000 meters 2 3000 meters 24000 meters 3 4000 meters 35000 meters 4 5000 meters 46000 meters 5 6000 meters 57000 meters 6 7000 meters 68000 meters 7 8000 meters 7 9000 meters 8 9000 meters 810000 meters 9 10000 meters 9>10000 meters
10 >10000 meters
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Table 7. Euclidian distance reclassification.
1.5.4. Technical criteria.
To avoid possible interference from woodlands it is consider a buffer of 250 meters.
Same analysis as for urban areas and rivers is applied. Cells included within 250 meters
from woodlands are giving the highest value (10) whereas the lowest value (0) is given
to the rest of cells.
1.6. Weighing of criteria
As AHP is used, all criteria were weighted using pair wise comparison method (see
Table 8).
Intensity of importance Definition Explanation
1 Equal ImportanceTwo activities contribute equally to the objective
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2 Weak or slight
3 Moderate importanceExperience and judgment slightly favor one activity over another
4 Moderate plus
5 Strong importanceExperience and judgment strongly favor one activity over another
6 Strong plus
7Very strong or demonstrated importance
An activity is favored very strongly over another; its dominance demonstrated in practice
8 Very,very strong
9 Extreme importanceThe evidence favoring one activity over anotheris of the highest possible order of affirmation
Table 8. Fundamental Scale used in Pairwise Comparison (Saaty p.85, 2008).
Table 9 “indicates how many times more important or dominant one element is over
another element with respect to the criterion or property with respect to which they are
compared” (Saaty p. 85, 2008).
Ecological Area
Rivers Urban areas
Road Network
Electrical Network
Woodlands
Ecological Area 1 2 1/2 3 3 4Rivers 1/2 1 1/3 1/2 1/2 2
Urban areas 2 3 1 2 2 6Road Network 1/3 2 1/2 1 1 4
Electrical Network 1/3 2 1/2 1 1 4
Woodlands 1/4 1/2 1/6 1/4 1/4 1
Table 9. Criteria weights using AHP.
According to Table 9 relative importance is obtained for each factor:
Ecological Area 0,19Rivers 0,10Urban areas 0,29Road Network 0,19Electrical Network 0,19Woodlands 0,05
Table 10. Relative importance of factors.
1.7. Site selection.
In order to choose the most suitable site, Map Algebra tool was used to obtain a final
raster derived from the different relative importance of each criterion. The output values
range from 0 (no constraint) to 10.1 (maximum constraint). Finally the output of the
MCE is reclassified into 7 classes of suitability (Table 11).
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Old Values New Values Definition0-1 1 Land with very minor or no limitations to use1- 2.5 2 Land with minor limitations2.5 - 3.5 3 Land with moderate limitations3.5 - 4.5 4 Land with moderately severe limitations4.5 – 5.5 5 Land with severe limitations5.5 – 7 6 Land with very severe limitations7 – 10.1 7 Land with extremely severe limitationsTable 11. Land suitability reclassification.
All the analysis carried out to obtain the most suitable locations for a wind farm, can be
seen in figure 6.
Figure 6. Flow chart for phase 2. Source: Model Builder.
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Figure 7. Land Suitability Map for a wind farm in UK. Source: ArcMap 10.
The next step is to overlay the potential sites for wind farms selected in phase 1.
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Selected site
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Figure 8. Selected site. Source: ArcMap 10.
Potential sites have to take account of the size of a 90MW wind farm. According to
Siemens Corporation (2012), a wind turbine of 3.6MW has a swept area of 9000 m 2.
Hence to build the require wind farm, we need 25 wind turbines and 225000 m2 of land.
The selected site (see figure 8) occupies plenty of space as has a total extent of 9 km2
and is located in land with very minor or no limitations to use.
Finally, in order to ensure slope of selected site is less than 10%, DEM of 50 meters
resolution was downloaded for that area from Digimap (see figure 9).
Figure 9. Selected site. Source: ArcMap 10
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Selected site
Selected site
Selected site
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It can be observed that slope of selected site is less than 10%, using a DEM of 50m resolution.
4. CONCLUSION.
The site selected for a wind farm is based on MCE. Phase 1 uses Boolean Criteria as
there are clear thresholds that determine if a project with these characteristics can be
carried out or not. Such constraints defined by specific thresholds, can be classified as 0
(no constraint) or 1 (total constraint). However in phase 2 there are not only constraints
but also fuzzy sets. The inclusion of factors in our analysis yields a different procedure
known as Weighted Linear Combination (Jiang et al, 2000). In this sense economic
factors (cost distance from roads and electrical network) represent a continuous degree
that range in our analysis from 0 (most suitable) to 10 (less suitable). Fuzzy methods
have proven to be more useful than Boolean methods for classification of continuous
variation (Burrough, 1992). On the other hand, it is more difficult to estimate
uncertainty because of the use of criteria of weighted linear combination, as
uncertainties are combined through an averaging process (Jiang et al, 2000). In this
respect, DEM should be of the highest quality as a lack of accuracy in it will propagate
throughout the analysis (Haklay, 1998).
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REFERENCES
Baban, S., Parry T. (2001). Developing and applying a GIS-assisted approach to locating wind farms in the UK. Renewable Energy 24, 59–71.
Burrough, P. A., Macmillan R. A. & Deursen, W (1992). Fuzzy classification methods for determining land suitability from soil profile observations and topography. Department of Physical Geography, University of Utrecht, The Netherlands and Alberta Research Council, Edmonton, Alberta, Canada
Case Study: Modelling Site Suitability for Wind Farms (2001). EDINA (University of Edinburgh). [Accessed 03 March 2012]. Available from: http://edina.ac.uk/learning/emapscholar/casestudies/foley/Manual.pdf
Haklay, M and Feitelson, E and Doytsher, Y (1998). The potential of a GIS-based scoping system: An Israeli proposal and case study. Environmental Impact Assessment Review , 18 (5) 439 - 459.
Jiang, H., Eastman J. R. (2000). Application of fuzzy measures in multi-criteria evaluation in GIS. Int. J. Geographical Information Science, vol. 14, no. 2, 173± 184.
Saaty, T.L., (2008). Decision making with the Analytic Hierarchy Process. Katz Graduate School of Bussiness, University of Pittsburgh, USA.
Wind Turbines (2012). Siemens. [Accessed 03 March 2012]. Available from: http://www.energy.siemens.com/hq/en/power-generation/renewables/wind-power/wind-turbines/swt-3-6-107.htm#content=Technical%20Specification
Wind Powering America (2012). US Department of Energy. [Accessed 03 March 2012]. Available from: http://www.windpoweringamerica.gov/wind_maps.asp
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