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VISUAL IMPACT ANALYSIS Salzburg Airport Tower
Schendl Gabriel ID: 1120878
1
Abstract
This paper investigates the visual impact of the new and old airport tower of Salzburg. In the
introduction, the study object and the study area is presented. Further, some general information
of visual impact is provided and other studies of this effect are shortly introduced. In the
methodological part, it is explained why modelling visual impact is important and the three
applied methods in the analysis are discussed. In the results, the outcomes of the analysis are
visualized. A description and interpretation of these results is done in the discussion part of this
paper. In the conclusion, the most important findings of this study are summarized and finally,
an outlook is provided.
2
Contents Abstract ...................................................................................................................................... 1
List of tables ............................................................................................................................... 3
List of figures ............................................................................................................................. 3
List of equations ......................................................................................................................... 3
Introduction ................................................................................................................................ 4
Methods ...................................................................................................................................... 5
a) Modelling Visual Impact ................................................................................................. 5
b) Viewshed ......................................................................................................................... 6
c) Distance Decay Function / Fuzzy Viewshed ................................................................... 7
d) Overlay of viewsheds with landscape types and population ......................................... 10
Results ...................................................................................................................................... 11
a) Fuzzy Viewsheds ........................................................................................................... 11
b) Overlay of viewsheds with landscape types .................................................................. 12
c) Overlay of viewsheds with population data .................................................................. 13
Discussion ................................................................................................................................ 17
Conclusion ................................................................................................................................ 18
References ................................................................................................................................ 19
Data Sources in the analysis ..................................................................................................... 21
Attachment ............................................................................................................................... 22
3
List of tables Table 1: Variables in Equation 1 ................................................................................................ 9
Table 2: Zones for overlay of viewsheds ................................................................................. 12
Table 3: Overview Affected Population ................................................................................... 16
Table 4: Result of overlay viewsheds and land use raster for the first zone ............................ 22
Table 5: Results of overlay viewsheds and land use raster for the second zone ...................... 24
Table 6: Results of overlay viewsheds and land use raster for the third zone ......................... 26
Table 7: Results of overlay viewsheds and land use raster for the fourth zone ....................... 28
Table 8: Results of overlay viewsheds and land use raster for the fifth zone .......................... 30
List of figures Figure 1: Example for a binary viewshed .................................................................................. 7
Figure 2: Example for a distance buffer layer ............................................................................ 8
Figure 3: Fuzzy Viewshed of the old tower based on a DEM ................................................. 11
Figure 4: Fuzzy Viewshed of the new tower based on a DEM ................................................ 11
Figure 5: Affected Population Zone 1 ...................................................................................... 13
Figure 6: Affected Population Zone 2 ...................................................................................... 14
Figure 7: Affected Population Zone 3 ...................................................................................... 14
Figure 8: Affected Population Zone 4 ...................................................................................... 15
Figure 9: Affected Population for all zones ............................................................................. 15
List of equations Equation 1: Distance Decay Function ........................................................................................ 9
4
Introduction
The goal of this paper is to model the visual impact for the old and the new airport tower of
Salzburg and to find out which of the two towers has a higher visual impact.
In the year 2014, a new tower for the airport of Salzburg was put into operation. This new
building has a height of 53 meters (ORF 2014) and replaced the old tower which had been in
use from 1969 to 2014. It was necessary to construct a new tower because the old was not able
anymore to fulfil the current state of technology. The old tower had a height of 27 meters. After
the new tower was put into operation, the predecessor was not used anymore and parts of it
were dismantled in the meantime (ORF 2015). The study area is the surroundings of the city of
Salzburg within a distance of about 17 kilometers to the airport tower in the state of Salzburg.
Parts of the state of Bavaria which would be in this distance threshold are not considered in the
analysis.
The creation of new buildings leads to changes in viewing conditions of landscapes. This
resulting effect “is identified as a visual impact (Garnero and Fabrizio 2015)“. The investigation
of this effect of view obstructions is difficult. If a high building is created and if a building can
be perceived easily in the surrounding area, the visual impact of such a construction should be
analyzed. Besides it is necessary to find out “from where this building can be seen from
(Garnero and Fabrizio 2015)”. Geographic information systems can be used for the analysis of
visual impact. Doing such an analysis in an objective way can get complicated because factors
like the distance to the building or weather conditions need to be considered (Möller 2006).
This paper is not the first study of visual impact. Möller (2006) analyzed the visual impact of
wind power turbines in Denmark with a geographic overlay of viewsheds with population data.
Bishop and Miller (2007) did a visual assessment of wind turbines which were built along the
north coast of Wales. Loots, Nackaerts et al. (1999) calculated fuzzy viewsheds for a former
city defence system of the ancient Greeks at Sagalassos in Turkey. Rasova (2014) also created
fuzzy viewsheds of prehistoric monuments in the west part of Slovakia. Garnero and Fabrizio
(2015) applied a method to calculate visibility maps of a planned skyscraper in the city of Turin.
5
Methods
a) Modelling Visual Impact
If a new building is created, the viewing conditions of a landscape can change. This effect is
called visual impact. Analyzing this effect on the skyline can be difficult in rural and as well in
urban areas. In the second case, topographic aspects, the heights of buildings and atmospheric
conditions need to be considered in the analysis. Changes to urban landscapes which can be
investigated “are the variation of the skyline of the city and the visibility of the building from
visual corridors of the main streets (Garnero and Fabrizio 2015)”. If buildings can be perceived
easily from the surroundings, it is necessary to model the visual impact of a new building.
Another important aspect is to “understand where this building can be seen from and how much
of it can be seen (Garnero and Fabrizio 2015)“. This can be done with generating visibility
maps of high buildings. This simple method leads to accurate results (Garnero and Fabrizio
2015).
If such a new building is created, affected people complain about the visual impact of it. The
visual impact can be modelled with Geographic Information Systems. Visual impact analysis
is possible with using digital elevation models and population data with a high resolution. Land
use aspects can also be considered. The visibility of buildings can be calculated with viewsheds
with using a certain radius (Möller 2006).
Investigating “visual impact in an objective way is difficult (Möller 2006)”. A building which
can be perceived “from a location does not itself comprise an adverse impact because visibility
is not the same as an actually sensed visual-impact (Möller 2006)“. Influencing factors can be
“the distance to the building, the size, paint colour, structure weather conditions, how often,
how long, and where people are faced with (Möller 2006)”. Due to these factors, visual impact
analysis gets complicated. One approach “to quantify visual exposure is the geographic overlay
of viewsheds with landscapes types or population (Möller 2006)“.
6
b) Viewshed
The term viewshed was introduced in 1967 “as an analogy to the watershed (Nutsford, Reitsma
et al. 2015)“. One year later, the first computer algorithm was programmed for calculating
visibility (Nutsford, Reitsma et al. 2015).
The term viewshed analysis is defined as “a GIS function that identifies all the terrain surfaces
that are visible from a pre-defined observation point (Lee and Stucky 1998)“. The intervisibility
of a terrain surface is regarded as the base for this analysis. In GIS programs, digital elevation
models (DEMs) are used for representing terrain surfaces (Lee and Stucky 1998).
Viewshed analysis in GIS programs offers “a full 360 degree horizontal view orientation (Yang,
Putra et al. 2007)”. This analysis belongs to the 2.5 D concepts (Yang, Putra et al. 2007).
In most cases, viewsheds have an irregular and fragmented form. They usually consist of
discrete patches and not of some continuous polygon areas (Llobera 2003). Viewshed analysis
leads to a binary result: an object can be visible or not visible. The result is “a continuous spatial
representation of visibility that indicates whether or not a viewpoint on a surface can be seen
from a particular observer cell (Möller 2006)“.
In ArcGIS from ESRI (Environmental Systems Research Institute), viewsheds can be
calculated with Spatial Analyst and 3D Analyst tools. The used algorithm “determines the
visibility for each grid-cell centre by comparing the vertical angle to the centre of the cell with
the vertical angle to the local horizon (Möller 2006)“. The output can be seen as “a Boolean
variable that identifies whether each cell is visible (value 1) or not (value 0) from a certain
viewpoint (Garnero and Fabrizio 2015)“. As output, a new raster layer is created. Important
parameters can be the height of the pre-defined observation point or the radius of the viewshed
(Fisher 1993).
Figure 1 on page 7 shows the binary viewshed for the old airport tower based on a DSM with a
radius of 10 kilometers.
7
Figure 1: Example for a binary viewshed
c) Distance Decay Function / Fuzzy Viewshed
The viewshed described before cannot be regarded as a good tool for measuring visibility from
a human perspective. It is necessary to consider the distance between the pre-defined
observation point and the observer. The closer a visible object to an observer, the higher the
visual impact. The higher the distance between the object and the observer, the lower the visual
impact. Many factors like relative size of objects or object-background clarity influence this
process. They all “are a function of the distance between the perceived object and the observer
(Nutsford, Reitsma et al. 2015)”.
Due to these reasons, the viewshed analysis was technically improved. Distance decay functions
and fuzzy viewshed were introduced “in order to simulate the loss of visual resolution with
distance and to move from deterministic to probabilistic viewshed models (van Leusen
2002)(Chapter 6, page 13)“.
The fuzzy viewshed can be used “to more accurately model the real world view afforded by
various environmental conditions within a GIS (Beaulieu 2007)“. This is done with integrating
“a distance decay function into the standard binary viewshed (Beaulieu 2007)”. In contrast to
8
the binary viewshed where cell are identified as visible or not visible, “each cell within a fuzzy
viewshed is assigned a value from 0 to 1 representing the degree of visibility of the cell from
the viewpoint (Beaulieu 2007)“. A value near to 1 means that this cell has a high visibility, a
value near to 0 stands for a low visibility. The three main parts in creating fuzzy viewsheds are
(Beaulieu 2007):
a binary viewshed
a distance buffer and
a distance decay function.
The binary viewshed can be created in ArcGIS with using Spatial Analyst tools. As input data,
a digital elevation model and a pre-defined observer point are needed. The result contains cells
which are classified as visible or not visible from the observer point (Beaulieu 2007).
For creating a fuzzy viewshed, a layer with distance information is needed. This distance layer
is also created in ArcGIS with the Spatial Analyst function Euclidean distance. The output is
“a raster layer in which the value of each cell equals the distance from that cell to the viewpoint
(Beaulieu 2007)“.
Figure 2: Example for a distance buffer layer
9
The distance decay function can be regarded as the most important part in creating fuzzy
viewsheds. It is used “to model the drop in visual clarity that occurs with increasing distance
from the viewpoint (Beaulieu 2007)“. This function is based on the following equation (Fisher
1994):
Equation 1: Distance Decay Function
𝜇 (𝑥𝑖𝑗) = {11
(1+(𝑑𝑣𝑝→𝑖𝑗− 𝑏1
𝑏2)
2
)
for dvp→ij ≤ b1 and for dvp→ij > b1
The following table provides an overview of the variables used in Equation 1 (Beaulieu 2007):
Table 1: Variables in Equation 1
Variable Description
xij fuzzy membership at cell at row I, column j
dvp→ij distance from viewpoint to row i, column j
b1 maximum distance from viewpoint of clear visibility
b2 distance from viewpoint at which visibility drops to 50%
The next step is to complete the equation with choosing the distance variables for the decay
function. Possible values are 1 km for b1 and 2 km for b2. Then, a distance decay buffer has to
be calculated. This “is a raster layer created by applying the distance decay function to the
distance buffer layer (Beaulieu 2007)“. For this task, the raster calculator function of ArcGIS
can be used.
The calculation of a fuzzy viewshed is completed with combining “the layer representing the
distance decay function, and the layer classifying all cells as either not visible or possible visible
from the viewpoint based on the topography of the region (Beaulieu 2007)“. The distance decay
buffer layer has to be multiplied with the layer of the binary viewshed. Like in the step before,
the raster calculator function of ArcGIS is applied. The output layer contains cells represented
by values from 0 to 1. A value close to 1 stand for a high visibility, values close to 0 for a low
visibility (Beaulieu 2007).
10
The distance decay function can be adopted to consider factors which have an impact on the
visibility. Such factors can be “environmental factors affecting conditions between the observer
and the object under view, the physical properties of the object being viewed and constraints
imposed on visibility by the observer (Beaulieu 2007)”. Environmental factors with an impact
on the visibility can be “the presence or absence of atmospheric particulates and varying levels
and directions of illumination (Beaulieu 2007)“. Such atmospheric particulates with a negative
impact on visibility can be smoke, dust, fog, rain, sandstorms or swarms of insects. As physical
properties of the object, the size, the color, its reflectivity or the texture can be mentioned. The
amount and direction has an impact on the visibility. The more light available, the better the
viewing conditions. The direction of illumination needs to be considered because “the degree
of visibility is greater when looking away from the light source than when looking toward it
(Beaulieu 2007)“ like it is the case with sunrises or in sunsets. “Constraints imposed by the
observer on visibility refer to such things as the visual acuity of the observer and the observer’s
culturally influenced concepts of landscape and cognition (Beaulieu 2007)“. Here,
psychological and physiological restraints can be distinguished. Physiological restraints “limit
the visual acuity of the observer, while psychological restraints are cognitive limitations
imposed by the observers background or culture (Beaulieu 2007)“. Visual acuity investigates
the ability of the observer to see specific objects (Beaulieu 2007). Such adaptions were not done
in this analysis.
d) Overlay of viewsheds with landscape types and population
Visual impact can also be modelled with “geographic overlay of viewsheds with landscape
types or population, summarizing land use or population count for cumulative numbers of
visible objects (Möller 2006)“. This is a method for comparison of the visual impact and not
for modelling the total exposure. A zonal summary is carried out. The output of this method are
tables with statistical data. In ArcGIS, a landscape model is created. Input data are digital
elevation models and land cover data. The resulting landscape model can be used for
investigation of the visual impact. This impact of existing object is calculated for observer
locations based on certain topography. For overlaying population data with the viewsheds in
ArcGIS, zonal statistics functions are used. In the result, the affected population and the land-
use will be summarized as values in tables in the zonal statistics (Möller 2006).
11
Results
a) Fuzzy Viewsheds Figure 1 shows the fuzzy viewsheds for the old airport tower based on a DEM.
Figure 3: Fuzzy Viewshed of the old tower based on a DEM
Figure 2 shows the fuzzy viewshed for the new airport tower based on a DEM.
Figure 4: Fuzzy Viewshed of the new tower based on a DEM
12
These two fuzzy viewsheds were both calculated with a toolbox which was downloaded from
the ArcGIS resources. It was not necessary to do all the described steps from before. Running
this model with a DSM as input data was not possible because it delivered results which are
presumably wrong. After the description of the toolbox, a Digital Elevation Model was
necessary as input data. The results were then classified after the following degrees of visibility:
0 – 0,94, 0,94 – 0,96, 0,96 – 0,98, 0,98 – 0,99, 0,99 – 0,995 and 0,995 – 1. For the fuzzy
viewshed of the new tower, only the highest degrees of visibility are visualized. For receiving
the lower degrees, it would have been necessary to set a higher radius of the fuzzy viewshed.
b) Overlay of viewsheds with landscape types
Based on the resulting zones after the degree of visibility of the fuzzy viewshed for the old
airport tower (Figure 3), binary viewsheds based on a DEM and a DSM were created for both
towers. Table 2 gives an overview of these visibility zones:
Table 2: Zones for overlay of viewsheds
Zone number Values in meters
1 0 – 5581
2 5581 – 7525
3 7525 – 10377
4 10377 – 12782
5 12782 – 17471
These viewsheds were then overlaid with a land use vector dataset. For the overlay, this vector
dataset was converted into a raster dataset with a spatial resolution of 10 meters using the tool
“Feature to Raster” in ArcGIS Pro. For the overlay of the viewsheds with the land use raster,
the Spatial Analyst tool “Zonal Statistics as Table” was applied. The resulting table were
converted into Excel files using the tool “Table to Excel”.
The resulting tables of this analysis can be found in the attachment. A value of 10 means that
10 cells are affected; each cell has a size of 100 m².
13
c) Overlay of viewsheds with population data
The binary viewsheds which were used before are now overlaid with a population density raster
layer in ArcGIS with the tool “Zonal Statistics as Table”. The resulting tables were converted
into Excel files to calculate the affected population.
Figure 3 shows the results for the first zone. The zones from the overlay of the viewsheds with
the land use raster are used again here except the fifth zone. An overlay of the population density
raster or the land use raster with fuzzy viewsheds including a distance decay function was not
applied because in this case the affected population respectively the number of affected cells
would have been multiplied with their degree of visibility. As results, values with decimals
would have been calculated instead of values without decimals.
Figure 5: Affected Population Zone 1
0
10000
20000
30000
40000
50000
60000
70000
80000
90000
Old Tower DEM New Tower DEM Old Tower DSM New Tower DSM
Affected Population
14
Figure 4 shows the results for the second zone.
Figure 6: Affected Population Zone 2
Figure 5 shows the results for the third zone.
Figure 7: Affected Population Zone 3
0
2000
4000
6000
8000
10000
12000
14000
16000
18000
Old Tower DEM New Tower DEM Old Tower DSM New Tower DSM
Affected Population
0
500
1000
1500
2000
2500
3000
3500
4000
Old Tower DEM New Tower DEM Old Tower DSM New Tower DSM
Affected Population
15
Figure 6 shows the results for the fourth zone.
Figure 8: Affected Population Zone 4
Figure 6 shows the overall results from this analysis.
Figure 9: Affected Population for all zones
0
100
200
300
400
500
600
Old Tower DEM New Tower DEM Old Tower DSM New Tower DSM
Affected Population
0
20000
40000
60000
80000
100000
120000
Old Tower DEM New Tower DEM Old Tower DSM New Tower DSM
Affected Population
16
Table 3 gives an overview over the affected population. In the fifth zone, no people are affected
by the airport towers.
Table 3: Overview Affected Population
Viewshed Zone 1 Zone 2 Zone 3 Zone 4 Zone 5 Overall
Old Tower
DEM
61334 11173 2492 497 0 75496
New Tower
DEM
83757 15301 3357 551 0 102966
Old Tower
DSM
13110 1969 925 239 0 16243
New Tower
DSM
20005 3206 1561 267 0 25039
17
Discussion
The results from calculating fuzzy viewsheds for both towers show that the new tower has a
higher visual impact because the red and the yellow zones extend over a higher distance
compared to the old airport tower.
The results from the geographic overlay of the viewsheds with the land use types show that
usually more raster cells are affected by the new airport tower. Only in a few cases, the old
airport tower had a higher visual impact. This could be caused by the fact that due to different
positions of the airport towers, the calculated viewsheds do not use exactly the same area. Some
land use types e.g. the category airport are not affected in all five zones. The results also show
that less cells are affected by the airport towers if the viewsheds are based on a digital surface
model. In case of a digital elevation model, more cells are affected.
The results from the geographic overlay of the viewsheds with the population density raser
show a similar pattern. More people are affected by the new airport tower. A large part of the
population lives in the first zone within a distance less than six kilometers to the airport towers.
The results also show that more people are affected by the airport towers if the viewsheds are
based on a digital elevation model. In case of a digital surface model, less people are affected.
In the fifth zone, nobody is affected by the airport towers. A systematic error which can occur
in the overlay of viewsheds based on the DSM with the population density raster is the fact that
in the case of buildings with several floors people who live in a lower floor have a higher
visibility compared to people living in a higher one. Another aspect is the fact that the results
from the overlay of viewsheds based on the DEM show that the number of affected people is
presumably too high. Due to the urban study area, these results should be treated with care. The
results from the overlay of viewsheds based on the DSM seem to be more reliable.
18
Conclusion
The goal of this paper was to do a visual impact analysis for the old and the new airport tower
in Salzburg and to compare the visual impact of these two buildings.
The results from the three applied methods - calculation of fuzzy viewsheds, geographic overlay
of viewsheds with land use types and geographic overlay of viewsheds with population data -
show that the new airport tower has a higher visual impact than the old tower. This is
presumably caused by the greater height of the new airport tower.
A calculation of the fuzzy viewsheds for both airport tower based on a digital surface model is
missing in this analysis. Because the downloaded model did not work with a DSM as input data,
the calculation of the fuzzy viewsheds could be done manually after the described steps in the
methodological part of this paper. Also adaptions to the distance decay function were not
applied in the analysis e.g. in the case of environmental factors. Another further step would be
the investigation of the affected area in the state of Bavaria. Also a validation of the results from
the analysis is not possible.
Another problem is that uncertainty is given in viewsheds. Small changes of the viewing
location can lead to different viewing conditions. Further, every location is marked with a
specific probability of being visible or not; this probability can vary from a small to a large
likelihood. Personal experience leads to the fact “that the viewshed is not really a Boolean
phenomenon” (Fisher 1992). Also errors in digital elevation models like the root-mean-square
error (RMSE) are possible (Fisher 1992). For a higher accuracy of the viewsheds, it would have
been necessary to use a DEM or DSM with a better spatial resolution.
19
References
Beaulieu, T. (2007) Can you see that? Fuzzy viewsheds and realistic models of landscape
visibility.
http://www.georeference.org/forum/e31362F39303930322F46757A7A792076696577736865
647320616E64207265616C6973746963206D6F64656C73206F66206C616E6473636170652
07669736962696C6974792E706466/Fuzzy%20viewsheds%20and%20realistic%20models%
20of%20landscape%20visibility.pdf (accessed on March 29, 2016).
Bishop, I. D. and D. R. Miller (2007). "Visual assessment of off-shore wind turbines: The
influence of distance, contrast, movements, and social variables." Renewable Energy 32: 814 -
831.
Fisher, P. F. (1992). "First Experiments in Viewshed Uncertainty: Simulating Fuzzy
Viewsheds." Photogrammetric Engineering & Remote Sensing 58.3: 345 - 352.
Fisher, P. F. (1993). "Algorithm and implementation uncertainty in viewshed analysis."
International Journal of Geographical Information Science 7:4: 331 - 347.
Fisher, P. F. (1994). Probable and fuzzy models of the viewshed operation. Innovations in GIS:
selected papers from the First National Conference on GIS Research UK. M. F. Worboys.
London, UK, Taylor and Francis: 161 - 175.
Garnero, G. and E. Fabrizio (2015). "Visibility analysis in urban spaces: a raster-based approach
and case studies." Environment and Planning B: Planning and Design 42: 688 - 707.
Lee, J. and D. Stucky (1998). "On applying viewshed analysis for determining least-cost paths
on Digital Elevation Models." International Journal of Geographical Information Science 12:8:
891 - 905.
20
Llobera, M. (2003). "Extending GIS-based visual analysis: the concept of visualscapes."
International Journal of Geographical Information Science 17:1: 25 - 48.
Loots, L., et al. (1999). Fuzzy Viewshed Analysis of the Hellenistic City Defence System at
Sagalassos, Turkey. Archaeology in the Age of the Internet. CAA97. Computer Applications
and Quantitative Methods in Archaeology. Proceedings of the 25th Anniversary Conference.
University of Birmingham, Archaeopress, Oxford.: 82-81 - 82-89.
Möller, B. (2006). "Changing wind-power landscapes: regional assessment of visual impact on
land use and population in Northern Jutland, Denmark." Applied Energy 83: 477 - 494.
Nutsford, D., et al. (2015). "Personalising the viewshed: Visibility analysis from the human
perspective " Applied Geography 62: 1 - 7.
ORF (2014) Airport: Neuer Tower get in Betrieb. http://salzburg.orf.at/news/stories/2630894/
(accessed on March 2, 2016).
ORF (2015) Alter Flughafen-Tower wird zum Teil abgetragen.
http://salzburg.orf.at/news/stories/2733643/ (accessed on March 2, 2016).
Rasova, A. (2014). Fuzzy Viewshed, probable viewshed, and their use in the analysis of
prehistoric monuments placement in Western Slovakia. . Connecting a Digital Europe through
Location and Place. Proceedings of the AGILE'2014 International Conference on Geographic
Information Science. S. Huerta, Granell. Castellon.
van Leusen, M. (2002). Pattern to process: methodological investigations into the formation
and interpretation of spatial patterns in archaeological landscapes, Rijksuniversiteit Groningen.
Doctoraat: 356.
Yang, P. P.-J., et al. (2007). "Viewsphere: a GIS-based 3D visibility analysis for urban design
evaluation." Environment and Planning B: Planning and Design 34: 971 - 992.
21
Data Sources in the analysis
The following datasets were used in the analysis:
Digital Elevation Model and Digital Surface Model of the state of Salzburg with a
spatial resolution of 10 meters (downloaded on March 15, 2016 from
https://www.salzburg.gv.at/themen/bauen-wohnen/raumplanung/sagis/download)
Data about land use of the districts Salzburg and Salzburg – Land (downloaded on April
26, 2016 from http://www.eea.europa.eu/data-and-maps/data/urban-atlas)
Population density raster of the city of Salzburg and its surroundings (ZGIS SBG
Population Point), accessed in ArcGIS via “Add Data From ArcGIS Online
Model to calculate fuzzy viewsheds (downloaded on March 26, 2016 from
http://www.arcgis.com/home/item.html?id=5e9cb4fd73fe4288a4cf534cc5a119aa)
22
Attachment
Table 4 shows the results of the overlay of the binary viewsheds with the land use raster for the
first zone. As already mentioned in the results, a value of 5 means that five cells are affected,
each of them has a size of 100 m². Not all land use types can be found in all of the five following
tables.
Table 4: Result of overlay viewsheds and land use raster for the first zone
Land use
category
Affected cells
VS old tower
DEM
Affected cells
VS new tower
DEM
Affected cells
VS old tower
DSM
Affected cells
VS new tower
DSM
Continuous
Urban Fabric
(S.L. > 80%)
3361 4740 739 1551
Discontinuous
Medium
Density Urban
Fabric (S.L.:
30% - 50%)
30351 42078 4821 12628
Discontinuous
Low Density
Urban Fabric
(S.L.: 10% -
30%)
4563 6201 897 2190
Sports and
leisure facilities
6538 10459 783 2251
Discontinuous
Dense Urban
Fabric (S.L.:
50% - 80%)
37828 49273 5676 14784
Isolated
Structures
1544 1916 250 681
Agricultural +
Semi-natural
126131 170814 14976 71732
23
areas +
Wetlands
Discontinuous
Very Low
Density Urban
Fabric (S.L. <
10%)
240 269 37 50
Industrial,
commercial,
public, military
and private
units
42504 54375 5548 16282
Green urban
areas
13283 17422 4579 6686
Land without
current use
2443 3533 33 377
Other roads
and associated
land
15766 20598 1350 4281
Fast transit
roads and
associated land
5678 7192 363 2924
Railways and
associated land
4049 4919 53 320
Airports 18946 19240 14773 18107
Mineral
extraction and
dump sites
37 68 5 46
Construction
sites
1951 2349 225 708
Forests 53573 66727 16505 32430
Water bodies 1228 2821 28 274
24
Table 5 shows the results of the overlay of the binary viewsheds with the land use raster for the
second zone.
Table 5: Results of overlay viewsheds and land use raster for the second zone
Land use
category
Affected cells
old tower DEM
Affected cells
new tower
DEM
Affected cells
old tower DSM
Affected cells
new tower
DSM
Continuous
Urban Fabric
(S.L. > 80%)
272 343 4 38
Discontinuous
Medium
Density Urban
Fabric (S.L.:
30% - 50%)
10801 13829 1674 3962
Discontinuous
Low Density
Urban Fabric
(S.L.: 10% -
30%)
4519 5377 1603 2367
Sports and
leisure facilities
1156 1707 169 349
Discontinuous
Dense Urban
Fabric (S.L.:
50% - 80%)
7531 10257 806 2592
Isolated
Structures
1763 1835 530 707
Agricultural +
Semi-natural
areas +
Wetlands
52566 66059 14976 23969
Discontinuous
Very Low
107 139 27 53
25
Density Urban
Fabric (S.L. <
10%)
Industrial,
commercial,
public, military
and private
units
7778 11150 1315 3314
Green urban
areas
2342 2713 852 1378
Land without
current use
911 1290 61 109
Other roads
and associated
land
5140 6396 606 1213
Fast transit
roads and
associated land
1530 1765 729 909
Railways and
associated land
2031 2333 27 96
Mineral
extraction and
dump sites
520 506 295 293
Construction
sites
367 662 4 31
Forests 96467 101894 63039 67190
Water bodies 175 235 12 60
26
Table 6 shows the results of the overlay of the binary viewsheds with the land use raster for the
third zone.
Table 6: Results of overlay viewsheds and land use raster for the third zone
Land use
category
Affected cells
old tower DEM
Affected cells
new tower
DEM
Affected cells
old tower DSM
Affected cells
new tower
DSM
Discontinuous
Medium
Density Urban
Fabric (S.L.:
30% - 50%)
5319 6529 1500 2445
Discontinuous
Low Density
Urban Fabric
(S.L.: 10% -
30%)
3907 4579 1566 2205
Sports and
leisure facilities
172 523 8 61
Discontinuous
Dense Urban
Fabric (S.L.:
50% - 80%)
597 895 182 428
Isolated
Structures
3031 3405 1284 1530
Agricultural +
Semi-natural
areas +
Wetlands
84941 96448 47278 54726
Discontinuous
Very Low
Density Urban
Fabric (S.L. <
10%)
144 161 75 92
27
Industrial,
commercial,
public, military
and private
units
3226 4567 710 1844
Green urban
areas
17 73 28 169
Land without
current use
421 451 70 132
Other roads
and associated
land
3766 4470 1083 1421
Fast transit
roads and
associated land
674 771 0 99
Railways and
associated land
400 523 15 15
Mineral
extraction and
dump sites
868 972 272 370
Construction
sites
505 945 37 106
Forests 131988 141256 92113 98543
Water bodies 6 152 2 21
28
Table 7 shows the results of the overlay of the binary viewsheds with the land use raster for the
fourth zone.
Table 7: Results of overlay viewsheds and land use raster for the fourth zone
Land use
category
Affected cells
old tower DEM
Affected cells
new tower
DEM
Affected cells
old tower DSM
Affected cells
new tower
DSM
Continuous
Urban Fabric
(S.L. > 80%)
3 3 0 4
Discontinuous
Medium
Density Urban
Fabric (S.L.:
30% - 50%)
1906 2971 440 1037
Discontinuous
Low Density
Urban Fabric
(S.L.: 10% -
30%)
1567 1909 519 717
Sports and
leisure facilities
0 106 3 7
Discontinuous
Dense Urban
Fabric (S.L.:
50% - 80%)
304 641 48 199
Isolated
Structures
784 1073 382 491
Agricultural +
Semi-natural
areas +
Wetlands
16157 23051 5306 7294
Discontinuous
Very Low
43 51 9 11
29
Density Urban
Fabric (S.L. <
10%)
Industrial,
commercial,
public, military
and private
units
638 1009 229 444
Green urban
areas
156 198 75 99
Land without
current use
179 237 15 47
Other roads
and associated
land
1205 1683 405 546
Fast transit
roads and
associated land
280 322 162 197
Railways and
associated land
111 113 0 1
Mineral
extraction and
dump sites
311 289 167 171
Construction
sites
9 48 0 1
Forests 49055 53096 36874 39907
Water bodies 0 18 0 4
30
Table 8 shows the results of the overlay of the binary viewsheds with the land use raster for the
fifth zone.
Table 8: Results of overlay viewsheds and land use raster for the fifth zone
Land use
category
Affected cells
old tower DEM
Affected cells
new tower
DEM
Affected cells
old tower DSM
Affected cells
new tower
DSM
Isolated
Structures
5 3 3 3
Agricultural +
Semi-natural
areas +
Wetlands
770 2067 1302 1417
Other roads
and associated
land
26 24 0 5
Forests 2334 5228 2873 3807